Appendix Y - Detailed Site Investigation ( Round 1 )

Page 1

G

EOTECHNIQUE

®

PTY LTD ABN 64 002 841 063

DETAILED SITE INVESTIGATION (Round 1) BUSHELLS CONCORD LOT 2 IN DP230294, Lots 398 & 399 IN DP752023 and Lot 5 IN DP129325 160 BURWOOD ROAD, CONCORD REPORT NO 20136/1

24 MAY 2022

(Version 1)

Lemko Place, Penrith NSW 2750 PO Box 880, Penrith NSW 2751 Telephone (02) 4722 2700 Facsimile (02) 4722 2777 e-mail: info@geotech.com.au www.geotech.com.au


G

EOTECHNIQUE

®

PTY LTD ABN 64 002 841 063

Report No: 20136/1 24 May 2022 Version 1 New Concord Development Pty Ltd C/- Hatch Level 3, 50 Carrington Street SYDNEY NSW 2000 Email: stephen.moore@hatch.com

Attention: Mr S Moore

Dear Sir, re:

Bushells Concord Lot 2 in DP230294, Lots 398 & 399 in DP752023 and Lot 5 in DP129325 160 Burwood Road, Concord Detailed Site Investigation (Round 1)

Please find herewith Detailed Site Investigation report (round 1) for the land known as Bushells Concord, registered as Lot 2 in DP230294, Lots 398 & 399 in DP752023 and Lot 5 in DP129325, and located at 160 Burwood Road, Concord (the site). A brief of the outcome of the investigation is summarised in the Executive Summary. Should you have any questions, please do not hesitate to contact the undersigned. Yours faithfully GEOTECHNIQUE PTY LTD

JAMES NGU Senior Principal Environmental Engineer BE MEngSc MIEAust CPEng NER

Lemko Place, Penrith NSW 2750 PO Box 880, Penrith NSW 2751 Telephone (02) 4722 2700 Facsimile (02) 4722 2777 e-mail: info@geotech.com.au www.geotech.com.au


G

EOTECHNIQUE

®

PTY LTD ABN 64 002 841 063

EXECUTIVE SUMMARY This Detailed Site Investigation (round 1) was carried out for the land known as Bushells Concord, registered as Lot 2 in DP230294, Lots 398 & 399 in DP752023 and Lot 5 in DP129325, and located at 160 Burwood Road, Concord (the site), in the local government area of City of Canada Bay Council. This report was prepared generally in accordance with the NSW Environment Protection Authority (EPA), “Consultants reporting on contaminated land guidelines – NSW EPA, 2020, and to satisfy State “Environmental Planning Policy (Resilience and Hazards)” 2021 which has repealed “Managing Land Contamination: Planning Guidelines, State Environmental Planning Policy No. 55 – Remediation of Land”. The objective is to assess whether there is data gap which is required to be addressed in order to make the site suitable for the proposed neighbourhood centre, medium density residential and public recreation uses, after completion of 2014 and 2015 contamination investigations, 2022 desktop study and 2022 site inspection. In order to achieve the objective, the scope of works included appraisal of the site history and site reconnaissance. The historical aerial photographs, NSW Land Registry Services records, Planning Certificates, EPA records, SafeWork NSW records and previous reports (Appendices A, B, C, D, E, F and G) revealed that: ➢ aerial photographs: the site was developed for commercial / industrial use since 1961; the foreshore appears to be reclaimed between 1961 and 1978; the adjoining eastern property may have been used for industrial purposes prior to 1951 to 1994. Surrounding properties to the north, south and west were a public park, a road and occupied by residential buildings respectively. ➢ the site is and was owned by commercial / industrial companies. Part of the site (Lot 2, the foreshore) was owned by The Maritime Services Board of New South Wales in 1960s. ➢ Planning Certificates dated 29 March 2022, under Section 10.7 (2 & 5) of the Environmental Planning and Assessment Act 1979 showed that the site is not affected by any of the matters prescribed by Section 59(2) of the Contaminated Land Management Act 1997 and there was no contaminated land record. ➢ EPA notices for contaminated lands under Section 58 of the Contaminated Land Management (CLM) Act 1997: The notices relate to investigation and/or remediation of site contamination considered to pose a significant risk of harm under the definition in the CLM Act. A search of the EPA notices on 28 March, 2022 revealed no notices issued for the site. ➢ The EPA also issues environment protection licences to owners or operators of various industrial premises under the POEO Act to control the air, noise, water and waste impacts of an activity. A search of the POEO Public Register on 28 March 2022 found no records for the site.

➢ A search of the records held by SafeWork NSW confirmed the site was licensed to store dangerous goods (four Above Ground Storage Tanks {AST} containing sodium hydroxide solution, one AST containing liquid nitrogen, and a pressurised cylinder storage containing liquefied petroleum gas) on the site in 2015. The record also revealed four underground storage tanks (UST) containing flammable liquids (class 3) on the site between 1975 and 1992. Lemko Place, Penrith NSW 2750 PO Box 880, Penrith NSW 2751 Telephone (02) 4722 2700 Facsimile (02) 4722 2777 e-mail: info@geotech.com.au www.geotech.com.au


G EOTECHNIQUE

PTY LTD ii

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1 Executive Summary continued

➢ 2014 Contamination Assessment 1 The objective of the assessment was to ascertain whether the soil samples (recovered from BH1 to BH10 as shown on the attached Drawing No 13188/3-AA1) being assessed were likely to present a risk of harm to human health and the environment under the condition for the proposed high density residential use. Fill was encountered at all boreholes up to depth of 5 metres (m). Based on this assessment it is considered that soils collected are generally unlikely to pose a risk of harm to human health and the environment and are environmentally suitable to retain on site for the proposed development subjected to:

Addressing potential Arsenic contamination issue in vicinity of BH5 (0.1-0.4m), which is marginally exceed HIL B, by means of detail investigation, possible remediation and validation.

Elevated BaP concentrations identified in samples BH2 (4.5-4.8m) and split sample S1 (original sample BH9 (2.0-2.3m)) would not pose a risk of harm to human health and the environment due to the fact that these concentrations appear deeper than 2.0m which are unlikely to significant upset any terrestrial ecosystem. However, if the soils were to be excavated and used as topsoil, then they may have an impact on the immediate ecosystems where they landed.

Soil pH ranging from acidic (4) to alkaline (9). Acidic condition could have an impact on footing of structures.

2015 Additional Contamination Assessment 2 Further to the above 2014 contamination assessment report; assessment of soil in the area between the pathway and the seawall (the foreshore) was conducted at locations (BH11 to BH16) as shown on the Drawing No 13188/3-AA1 was carried out. The objective of the assessment was to ascertain whether the soil being assessed are likely to present a risk of harm to human health and the environment. The six boreholes (BH11 to BH16) showed fill to depths ranging from 2m to 6m. Based on this assessment, it was considered that the soil samples, recovered from boreholes BH11 to BH16 were unlikely to pose a risk of harm to human health and the terrestrial environment under the conditions for the proposed residential development. It is understood that this portion of the site is proposed for public recreation use.

1: Contamination Assessment report, 160 Burwood Road, Concord, 13188/2-AA, Geotechnique, 2014 2: Additional Contamination Assessment report, 160 Burwood Road, Concord, 13188/4-AA, Geotechnique, 2015


G EOTECHNIQUE

PTY LTD iii

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1 Executive Summary continued

During site inspection on 18 March 2022, Geotechnique identified the following potential environmental concerns, as shown on the attached Drawing No. 20136/1-AA1: ▪

a cover lid (well cap) appears to be associated with UST was identified at a potential underground storage tank area (site feature 15);

Transformer room

We were informed: ❖ Asbestos was identified in the main building (factory) and the gate house (guardhouse) 3. ❖ Other than liquid nitrogen, phosphorous acid and hydrochloric acid, lubricating oil, degreaser, hydraulic oil and solvents (Isopropyl Alcohol, Methyl Ethyl Ketone, Mineral Turpentine) were also used within the factory. ❖ The factory produced coffee from raw coffee bean. There were two main waste products from the process; coffee grounds and caustic solution. While coffee ground removal off site by contractor, the caustic solution which was used to clean the interior of the machineries was neutralised with acid on site and discharge into the sewer system.

Based on the desktop study and the site inspection, the potential environmental concerns (PEC) and the associated potential contaminants of concern within the site are as summarised in the following table.

3: Five Yearly Asbestos Audit For Freshfood Sydney Pty Ltd, 160 Burwood Road, Concord, NSW 10 April 2019, Benbow Environmental


G EOTECHNIQUE

PTY LTD iv

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1 Executive Summary continued

PEC

Rational / Details

Potential Contaminants ➢ ➢

Underground storage tank (UST) areas

possible fuel leak

➢ ➢

Corrosion of possible metal tanks

➢ ➢ ➢

Potential imported fill (soil, etc.) could have been contaminated at the source site(s)

Possible residue of containing material construction

Fill within the site

Beneath and in the vicinity of the factory & guardhouse

Transformer room

Prior to Bushells, the site was believed to have been occupied by a timber yard Adjoining eastern industrial property (prior to 1951 to 1994)

Asbestos, Metals, TPH, VOC, BTEX, PAH, Phenols Organochlorine Pesticides (OCP) Polychlorinated Biphenyls (PCB) etc.

asbestos during

Possible leaking of lubricating oil, degreaser, hydraulic oil and solvents (Isopropyl Alcohol, Methyl Ethyl Ketone, Mineral Turpentine) through the concrete slab of the factory

Possible PCB leak

➢ ➢ ➢

Metals Total Petroleum Hydrocarbons (TPH) Volatile Organic Compound (VOC) Benzene, Toluene, Ethyl Benzene and Xylenes (BTEX) Polycyclic Aromatic Hydrocarbons (PAH) Phenols

Possible use or leaching of wood preservative

Potential off-site migration of any contaminants via groundwater or surface run-off

➢ ➢

Asbestos TPH, VOC, BTEX, PAH & Phenols (beneath and in the vicinity of the factory)

PCB

➢ ➢ ➢ ➢ ➢

Chromium, Copper, Arsenic, Boron Naphthalene OCP Pentachlorophenol Creosote (predominantly PAH and Phenols)

Metals, TPH, VOC, BTEX, PAH, OCP, Phenols Semi-Volatile Organic Compound (SVOC) etc.

➢ ➢


G EOTECHNIQUE

PTY LTD v

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1 Executive Summary continued

The potential receptors, the potential sources and the potential exposure pathways would be as follows.

Potential Receptors

Potential Sources

Potential Exposure Pathways

On-site:

On-site:

On-site:

• •

Contaminated soil/fill & potential contaminated groundwater

Human Environment (groundwater and soil; plant)

Off-site:

Off-site:

• •

Potential contaminated soil & groundwater from adjoining eastern industrial property

➢ ➢

Outdoor and indoor inhalation of VOC vapours and asbestos fibres Incidental ingestion of dust particulates and dermal contact with dust particulates and groundwater

Off-site:

Human Exile Bay / Parramatta River Groundwater and soil; plant

➢ ➢ ➢

Outdoor and indoor inhalation of VOC vapours and asbestos fibres Incidental ingestion of dust particulates and contaminated surface water Dermal contact with dust particulates, surface water and groundwater


G EOTECHNIQUE

PTY LTD vi

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1 Executive Summary continued

Recommendations: The 2015 contamination assessment indicated the soil samples recovered from boreholes BH11 to BH16 (the foreshore) were unlikely to pose a risk of harm to human health and the terrestrial environment under the conditions for the proposed residential development. However, based on the above mentioned potential environmental concerns, with the consideration of the potential receptors, the potential sources and the potential exposure pathways, the following should be considered in order to make the site suitable for the proposed neighbourhood centre, medium density residential and public recreation uses. •

In accordance with the NSW EPA "Sampling Design Guidelines for Contaminated Sites", samples should be recovered from a minimum of 50 locations systematically across the site. Only 16 locations had been investigated so far. Completion of investigation for the remaining 34 locations will be required, preferable (due to access restriction) after completion of demolition of the factory the administration building, the transformer room and the gate house.

Investigation of the soil at and in the vicinity of the existing / previous underground storage tanks (UST) will also be required to determine the contamination status.

Should any new locations of concern be identified during the above proposed investigations, delineation will be required to determine the extent of contamination. The 2014 report identified Arsenic concentration of concern at BH5 (0.1-0.4m) and Benzo(a)Pyrene (BaP) concentrations of concern at BH2 (4.5-4.8m) and BH9 (2.0-2.3m). Copper and Zinc concentrations of concern were also identified at BH2 (4.5-4.8m), delineation is therefore also be required

Groundwater investigation and / or soil gas investigation would be required.

It is considered reasonable for conditional development consent to be issued to require the above recommendations. Based on the results of the testing to determine the need or otherwise for remediation. It is our opinion that based on this approach Council can be satisfied that the site can be made suitable for the proposed uses.


G EOTECHNIQUE

PTY LTD

TABLE OF CONTENTS

Page 1.0

INTRODUCTION ---------------------------------------------------------------------------------------- 1

2.0

SCOPE OF WORKS -------------------------------------------------------------------------------------- 2

3.0

SITE IDENTIFICATION --------------------------------------------------------------------------------- 2

4.0

SITE HISTORY ------------------------------------------------------------------------------------------ 3

4.1

Aerial Photographs ----------------------------------------------------------------------- 3

4.2

NSW Land Registry Services Records --------------------------------------------------- 4

4.3

Section 10.7 Planning Certificates ------------------------------------------------------ 4

4.4

NSW EPA Record of Notices and Environment Protection Licences -------------------- 5

4.5

SafeWork NSW Records ----------------------------------------------------------------- 5

4.6

Summary of Previous Reports ----------------------------------------------------------- 6

5.0

SITE CONDITION AND SURROUNDING ENVIRONMENT ---------------------------------------------- 9

5.1

Site Condition ---------------------------------------------------------------------------- 9

5.2

Surrounding Environment ------------------------------------------------------------- 10

6.0

TOPOGRAPHY, GEOLOGY & HYDROGEOLOGY ------------------------------------------------------ 10

7.0

CONCEPTUAL SITE MODELS ------------------------------------------------------------------------- 11

8.0

DATA QUALITY OBJECTIVE -------------------------------------------------------------------------- 13

9.0

RECOMMENDATIONS --------------------------------------------------------------------------------- 15

10.0

LIMITATIONS ---------------------------------------------------------------------------------------- 16

LIST OF REFERENCES

DRAWINGS Drawing No. 20136/1-AA1 Drawing No. 13188/3-AA1

APPENDICES APPENDIX A: Historical Aerial Photographs APPENDIX B: NSW Land Registry Services Records APPENDIX C : Section 10.7 (2 & 5) Planning Certificates APPENDIX D: NSW EPA Record of Notices & Environment Protection Licences APPENDIX E : SafeWork NSW Records APPENDIX F: 2014 Report 13188/2-AA APPENDIX G: 2015 Report 13188/4-AA APPENDIX H: WaterNSW Records APPENDIX I: Environmental Notes


G EOTECHNIQUE

PTY LTD 1

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

1.0 INTRODUCTION This report presents the outcome of a detailed site investigation (round 1) for the land known as Bushells Concord, currently registered as Lot 2 in DP230294, Lots 398 & 399 in DP752023 and Lot 5 in DP129325, and located at 160 Burwood Road, Concord (the site) in the local government area of City of Canada Bay Council, as indicated below.

SITE

N

Map Data ©2022 Google

It is understood that the site is proposed for neighbourhood centre, medium density residential and public recreation uses. The objective of this investigation is to assess whether there is data gap which is required to be addressed in order to make the site suitable for the proposed neighbourhood centre, medium density residential and public recreation uses, after completion of 2014 and 2015 contamination investigations, 2022 desktop study and 2022 site inspection. This report was prepared generally in accordance with the NSW Environment Protection Authority (EPA), “Consultants reporting on contaminated land guidelines – NSW EPA, 2020, and to satisfy State “Environmental Planning Policy (Resilience and Hazards)” 2021 which has repealed and “Managing Land Contamination: Planning Guidelines, State Environmental Planning Policy No. 55 – Remediation of Land”.


G EOTECHNIQUE

PTY LTD 2

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

2.0

SCOPE OF WORKS

In order to achieve the objectives, the following scope of works was conducted: ▪

3.0

Desktop study of ➢

historical aerial photographs

NSW Land Registry Services records

Section 10.7 (2 & 5) Planning Certificates

NSW Environment Protection Authority (EPA) records

SafeWork NSW records

geological and soil landscape maps

groundwater data

reports (13188/2-AA, 13188/4-AA, etc.) prepared in 2014, 2015 and 2019.

An inspection for current site conditions and identification of any environmental concerns based on visual and olfactory indicators of potential contamination.

SITE IDENTIFICATION

The site is located at 160 Burwood Road, Concord in the local government area of City of Canada Bay Council and is registered as Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325. As shown on Drawing No. 20136/1-AA1, the site is irregular in shape covering an area of about 4 hectares. Reference should be made to the cadastral, deposited and crown plans in Appendix B for details of the site location and dimensions.


G EOTECHNIQUE

PTY LTD 3

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

4.0

SITE HISTORY

In order to formulate a picture of the site history and to assist in identification of any potential contamination, Geotechnique Pty Ltd (Geotechnique) reviewed available information, including historical aerial photographs, NSW Land Registry Services records, Planning Certificate under Section 10.7 of the Environmental Planning and Assessment Act, NSW EPA record of Notices for Contaminated Land and records of the Protection of the Environment Operations (POEO) Public Register, SafeWork NSW information on potential licensing to keep dangerous goods, and previous reports. The review is presented in the following sub-sections. 4.1

Aerial Photographs

Aerial photographs taken in 1951, 1961, 1971, 1978, 1986, 1994, 2002, 2009 and 2021 (Appendix A) were examined. Due to scale, some of the listed observations are best interpretations only. 1951

The site is mostly vacant. There is a large structure on the northern portion of the site with a jetty which extends into a water body. Some unidentified objects were noted within the site. Streets adjoin the northern and southern site boundaries; a possible industrial factory adjoins the eastern boundary and residential properties adjoin the western boundary of the site.

1961

The large structure in the northern portion of the site has been removed, disturbances appear throughout the site and there is a new building in the southern portion of the site. The land surrounding the site appears to remain unchanged since 1951

1971

The building is getting larger. The foreshore of the site appears to be extended north eastwards with obvious filling activities. Surrounding land appears unchanged since 1961 with an exception the adjoining land to the north appears to be a public park.

1978

Other than the building, there appears to be a carpark covers most of the remaining site. The surrounding land appears unchanged since 1971.

1986

The site and surrounding land appears unchanged since 1978.

1994

The site appears to be unchanged since 1986 with exception of what appears to be an above ground storage tank (AST) located in the south eastern corner of the site. Surrounding land appears unchanged since 1986 with exception of land clearing in the adjoining eastern property.

2002

The site and the surrounding land appears unchanged since 1994, with an exception residential development in the adjoining eastern land.

November 2009 & December 2021

The site and surrounding land appear unchanged since 2002.

In summary, the aerial photographs reveal that the site was developed for commercial / industrial use since 1961; the foreshore appears to be reclaimed between 1961 and 1978; the adjoining eastern property may have been used for industrial purposes prior to 1951 to 1994. Surrounding properties to the north, south and west were a public park, a road and occupied by residential buildings respectively.


G EOTECHNIQUE

PTY LTD 4

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

4.2

NSW Land Registry Services Records

Reference should be made to Appendix B for the NSW Land Registry Services records. The chronological list of proprietors for the site is summarised in the tables below. Lot 2 DP230294 Year 1998 - 2022 1984 - 1998 1966 - 1984 1966

Proprietor Freshfood Sydney Pty Limited Bushells Foods Pty Limited Bushells Pty Limited The Maritime Services Board of New South Wales

Lots 398 & 399 DP752023 & Lot 5 DP129325 Year Proprietor 1998 - 2022 Freshfood Sydney Pty Limited 1984 - 1998 Bushells Foods Pty Limited 1956 - 1984 Bushells Pty Limited 1951 - 1956 Murray Bros. Pty Limited The records indicate generally the site is and was owned by commercial / industrial companies. Part of the site (Lot 2, the foreshore) was owned by The Maritime Services Board of New South Wales in 1960s.

4.3

Section 10.7 Planning Certificates

Planning Certificate Nos. PC2022/0752, PC2022/0753, PC2022/0754, and PC2022/0755 under Section 10.7 (2 & 5) of the Environmental Planning and Assessment Act 1979, for Lot 2 in DP230294, Lot 398 in DP752023, Lot 399 in DP752023 and Lot 5 in DP129325, issued on 29 March 2022 by City of Canada Bay Council (Appendix C), indicated the following: •

The site is zoned IN1 General Industrial.

The site does not include or comprise critical habitat.

The site is not within a conservation area.

An item of environmental heritage is not situated on the site.

The site is not affected by any of the matters prescribed by Section 59(2) of the Contaminated Land Management Act 1997.


G EOTECHNIQUE

PTY LTD 5

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

4.4

NSW EPA Record of Notices and Environment Protection Licences

➢ The NSW OEH maintains the record of EPA notices for contaminated lands under Section 58 of the Contaminated Land Management (CLM) Act 1997. The notices relate to investigation and/or remediation of site contamination considered to pose a significant risk of harm under the definition in the CLM Act. A search of the EPA notices on 28 March, 2022 revealed no notices issued for the site. It should be noted that the NSW EPA record for Contaminated Land does not provide a record of all contaminated lands in NSW. At the time of searching the records, 411 sites in NSW were registered in the database. ➢ The EPA issues environment protection licences to owners or operators of various industrial premises under the POEO Act to control the air, noise, water and waste impacts of an activity. A search of the POEO Public Register on 28 March 2022 found no records for the site. ➢ NSW EPA and the POEO Public Register records are detailed in Appendix D of this report.

4.5

SafeWork NSW Records

A request was made to SafeWork NSW to search for any information on storage of hazardous chemicals. A search of the records held by SafeWork NSW (Appendix E) revealed the site was licensed to store dangerous goods (four Above Ground Storage Tanks {AST} containing sodium hydroxide solution, one AST containing liquid nitrogen, and a pressurised cylinder storage containing liquefied petroleum gas) on the site in 2015. The record also revealed four underground storage tanks (UST) containing flammable liquids (class 3) on the site between 1975 and 1992.


G EOTECHNIQUE

PTY LTD 6

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

4.6

Summary of Previous Reports

Contamination Assessment Report 13188/2-AA 2014 (Appendix F)

The objective of the assessment was to ascertain whether the soil samples being assessed were likely to present a risk of harm to human health and the environment under the condition for the proposed high density residential use. The available information associated with report prepared by SLR Consulting Australia Pty Ltd indicated 11 areas of environmental concern (AEC1 to AEC11) within the site and there was a potential for the site to be contaminated with “hydrocarbons, metals, pesticide, asbestos and PCBs”. Borehole locations were appropriately located corresponding to the AECs. Bushells website provides an article about Bushell’s history. According to the article, Bushells purchased the site in 1956. Prior to that, the site was believed to have been occupied by a timber yard. Soil samples were recovered from ten (10) boreholes locations (as shown on the attached Drawing No 13188/3-AA1) in 2014 and forwarded to National Association of Testing Authorities (NATA) accredited testing laboratories for Chemical analysis. Fill was encountered at all boreholes up to depth of 5 metres (m) as summarised in the table below. Topsoil

Fill

Natural Soil

The following types of topsoil were encountered: Type 1: Silty Sand, grey, with root fibres. Type 2: Silty Clay, grey, inclusion of sandstone fragments. The following types of fill were encountered: Type 1: Silty Sand, brown with clay and gravel. Type 2: Silty Clay, grey, trace of ironstone. Type 3: Sandy Clay, dark brown, trace of gravel. Type 4: Silty Sand, grey, inclusion of gravel. Type 5: Silty Clay, grey, inclusion of gravel. Type 6: Sand Clay, dark grey. The following types of natural soil were encountered: Type 1: Silty SAND, dark grey. Type 2: Sandy CLAY, brown and grey. Type 3: Silty CLAY, grey.


G EOTECHNIQUE

PTY LTD 7

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

Based on site observation, the soil profile and the potential for contamination, the below testing strategy was adopted: Environmental Concern In the vicinity of above ground tanks (ASTs), potential underground fuel tanks (USTs)

Borehole BH2, BH5, BH9 and BH10

For screening in related to timber yard and possible pH issue Screening for imported fill

All boreholes

All boreholes

Testing Strategy Full range including metals, TPH, BTEX, PAH, OCP, PCB, total Phenols, total Cyanides, pH and Asbestos for top layer of fill or topsoil, lower layer of fill and natural soil layer immediately below fill. Metals, OCP, PAH and pH for all top layer topsoil or fill and some lower fill layers. Full range for each fill type.

Based on this assessment it is considered that soils collected are generally unlikely to pose a risk of harm to human health and the environment and are environmentally suitable to retain on site for the proposed development subjected to: ➢

Addressing potential Arsenic contamination issue in vicinity of BH5 (0.1-0.4m), which is marginally exceed HIL B, by means of detail investigation, possible remediation and validation.

Elevated BaP concentrations were identified in samples BH2 (4.5-4.8m) and split sample S1 (original sample BH9 (2.0-2.3m)) do not pose a risk of harm to human health and the environment due to the fact that these concentrations appear deeper than 2.0m which are unlikely to significant upset any terrestrial ecosystem. However, if the soils were to be excavated and used as topsoil, then they may have an impact on the immediate ecosystems where they landed.

Soil pH ranging from acidic (4) to alkaline (9). Acidic condition could have an impact on footing of structures.


G EOTECHNIQUE

PTY LTD 8

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

Additional Contamination Assessment Report 13188/4-AA 2015 (Appendix G)

Further to the above 2014 contamination assessment report; assessment of soil in the area between the pathway and the seawall (the foreshore) was conducted at locations (BH11 to BH16) as shown on the Drawing No 13188/3-AA1 was carried out. The objective of the assessment was to ascertain whether the soil being assessed are likely to present a risk of harm to human health and the environment under the conditions for the proposed residential development. The six boreholes (BH11 to BH16) showed fill to depths ranging from 2m to 6m, overlying natural soil and overlying sandstone bedrock, as summarised in the table below. Topsoil Fill

Natural

Bedrock

Sandy Silt, dark brown with some roots Sandy Gravel, yellow, brown Silty Sandy Clay, red brown Silty Clayey Sand, with some gravel Silty Clay, grey, with some gravels Silty Sand, brown, red, with some ironstone Silty Sandy Clay, red, brown Silty Clayey Sand, grey, brown, red Sandstone, grey, brown

The recovered soil samples were analysed for the following potential contaminants of concern: • • • • • • • • •

Metals, including, arsenic (As), cadmium (Cd), chromium (Cr), copper (Cu), lead (Pb), mercury (Hg), nickel (Ni) and zinc (Zn). Total Recoverable Hydrocarbons (TRH). Benzene, Toluene, Ethyl Benzene and Xylenes (BTEX). Organochlorine Pesticides (OCP). Polycyclic Aromatic Hydrocarbons (PAH). Polychlorinated Biphenyls (PCB). Cyanides. Phenols. Asbestos.

Based on this assessment, it was considered that the soil samples, recovered from boreholes BH11 to BH16 were unlikely to pose a risk of harm to human health and the terrestrial environment under the conditions for the proposed residential development. It is understood that this portion of the site is proposed for public recreation use.


G EOTECHNIQUE

PTY LTD 9

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

5.0

SITE CONDITION AND SURROUNDING ENVIRONMENT

5.1

Site Condition

An Environmental Engineer from Geotechnique observed the following (as shown on the attached Drawing No. 20136/1-AA1) during site inspection on 18 March 2022: •

Guardhouse

Administration building

Coffee factory (main building)

Bitumen car parks

Trucks manoeuvring and loading concrete area

Footpath

Landscape areas

Transformer room

Above ground liquid nitrogen, phosphorous acid and hydrochloric acid storage tanks

Scrap metal, disused furniture, caustic soda room, gas main supply, wheelbarrow, lawn mower, diesel oil staining, pallets, galvanized iron shed with liquefied petroleum gas cylinders, etc.

Open area of the site was covered with bitumen, concrete, grass or tree. There were no obvious ash materials, asbestos sheets / pieces, odour in the landscape areas that would indicate the potential for contamination. There were also no obvious features (bowser and breather pipe) associated with underground storage tank (UST); however, a cover lid (well cap) appears to be associated with UST was identified at a potential underground storage tank area (site feature 15, as shown on the attached Drawing No. 20136/1AA1). Asbestos was identified in the main building (factory) and the gate house (guardhouse). Other than liquid nitrogen, phosphorous acid and hydrochloric acid, lubricating oil, degreaser, hydraulic oil and solvents (Isopropyl Alcohol, Methyl Ethyl Ketone, Mineral Turpentine) were also used within the factory. The factory produced coffee from raw coffee bean. There were two main waste products from the process; coffee grounds and caustic solution. While coffee ground removal off site by contractor, the caustic solution which was used to clean the interior of the machineries was neutralised with acid on site and discharge into the sewer system. If the neutralization was not done appropriately or if there was spillage of either the caustic waste or the acid, soil pH within the site could be altered.


G EOTECHNIQUE

PTY LTD 10

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

5.2

Surrounding Environment

At the time of the inspection, observations of the neighbouring properties were as follows: To the north: Public Recreation. To the south: Burwood Road; residential properties across the road. To the east and west: residential properties. To the north-east: Exile Bay / Parramatta River The site features, as well as the layout of the site and surrounding properties are indicated on Drawing No. 20136/1-AA1.

6.0

TOPOGRAPHY, GEOLOGY & HYDROGEOLOGY

In general, the site was relatively flat. The Geological Map of Sydney (Geological Series Sheet 9130, Scale 1:100,000, 1983), published by the Department of Mineral Resources indicates the residual soils within the site to be underlain by Hawkesbury Sandstone comprising medium to coarse grained quartz sandstone, very minor shale and laminite lenses. The Soil Landscape Map of Sydney (soil Landscape Series Sheet 9130, Scale 1:100,000, 2002), prepared by the Soil Conservation Service of NSW, indicates that most of the site is located within the Gymea Soil Landscape characterized by undulating to rolling rises and low hills on Hawkesbury Sandstone. The subsurface soils are typically characterised by high soil erosion hazard, rock outcrop, high permeability and very low fertility. The Soil Landscape map also indicates the northern portion of the site encompasses disturbed terrain comprising land that is extensively disturbed by human activity including complete disturbance, removal or burial of soil, or landfill including soil, rock, building, and waste materials. Groundwater2 during auger boring was encountered at the following depths: BH 11 12 13 14 16

Groundwater Depth (m) 4.0 1.8 2.5 3.0 3.0

A search was carried out on 28 March 2022 through the website of WaterNSW for any registered groundwater bore data within 500 metres (m) of the site. The search revealed no bores were present within this radius (Appendix H). 2: Additional geotechnical investigation report, 160 Burwood Road, Concord, 13188/3-AA, 3 August 2015, Geotechnique


G EOTECHNIQUE

PTY LTD 11

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

7.0

CONCEPTUAL SITE MODELS

Based on the desktop study and the site inspection, the potential environmental concerns (PEC) and the associated potential contaminants of concern within the site are as summarised in the following table. PEC

Rational / Details

Potential Contaminants ➢ ➢

Underground storage tank (UST) areas

possible fuel leak

➢ ➢

Corrosion of possible metal tanks

➢ ➢ ➢

Potential imported fill (soil, etc.) could have been contaminated at the source site(s)

Possible residue of containing material construction

Fill within the site

Beneath and in the vicinity of the factory & guardhouse

Transformer room

Prior to Bushells, the site was believed to have been occupied by a timber yard Adjoining eastern industrial property (prior to 1951 to 1994)

Asbestos, Metals, TPH, VOC, BTEX, PAH, Phenols Organochlorine Pesticides (OCP) Polychlorinated Biphenyls (PCB) etc.

asbestos during

Possible leaking of lubricating oil, degreaser, hydraulic oil and solvents (Isopropyl Alcohol, Methyl Ethyl Ketone, Mineral Turpentine) through the concrete slab of the factory

Possible PCB leak

➢ ➢ ➢

Metals Total Petroleum Hydrocarbons (TPH) Volatile Organic Compound (VOC) Benzene, Toluene, Ethyl Benzene and Xylenes (BTEX) Polycyclic Aromatic Hydrocarbons (PAH) Phenols

Possible use or leaching of wood preservative

Potential off-site migration of any contaminants via groundwater or surface run-off

➢ ➢

Asbestos TPH, VOC, BTEX, PAH & Phenols (beneath and in the vicinity of the factory)

PCB

➢ ➢ ➢ ➢ ➢

Chromium, Copper, Arsenic, Boron Naphthalene OCP Pentachlorophenol Creosote (predominantly PAH and Phenols)

Metals, TPH, VOC, BTEX, PAH, OCP, Phenols Semi-Volatile Organic Compound (SVOC) etc.

➢ ➢


G EOTECHNIQUE

PTY LTD 12

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

Migration of any contaminants to the deeper soil and/or groundwater regime would generally be via leaching from the surface soil and or UST, facilitated by infiltration of surface water. The site is mostly covered with buildings, concrete or bitumen which would minimise the potential for contaminants migrating to deeper soil and groundwater under current site condition. Off-site impacts of any contaminants are generally governed by the transport media available and likely receptor(s). The most common transport medium is water and wind; receptors include uncontaminated soil, groundwater, surface water bodies, humans, flora and fauna. Again, as the site is mostly covered with buildings and concrete / bitumen hardstands, off-site migration of any contaminants from the footprints of buildings and concrete / bitumen hardstands via the wind and the surface water run-off would be unlikely. However, there is a possibility of leaching of any contaminants to deeper soil and/or groundwater due to surface water run-off, through the joints / any cracks of the hardstands; perhaps to an even greater extent after removal of concrete / bitumen hardstands during redevelopment of the site. The foreshore Exile Bay / Parramatta River defines the site’s north eastern boundary. There is a possibility of leaching of any contaminants from the uncovered north eastern portion of the site to the water body. The potential receptors, the potential sources and the potential exposure pathways would be as follows.

Potential Receptors

Potential Sources

Potential Exposure Pathways

On-site:

On-site:

On-site:

• •

Contaminated soil/fill & potential contaminated groundwater

Human Environment (groundwater and soil; plant)

Off-site:

Off-site:

• •

Potential contaminated soil & groundwater from adjoining eastern industrial property

➢ ➢

Outdoor and indoor inhalation of VOC vapours and asbestos fibres Incidental ingestion of dust particulates and dermal contact with dust particulates and groundwater

Off-site:

Human Exile Bay / Parramatta River Groundwater and soil; plant

➢ ➢ ➢

Outdoor and indoor inhalation of VOC vapours and asbestos fibres Incidental ingestion of dust particulates and contaminated surface water Dermal contact with dust particulates, surface water and groundwater


G EOTECHNIQUE

PTY LTD 13

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

8.0

DATA QUALITY OBJECTIVE

The Data quality objectives (DQO) developed for this investigation was generally based on the Guidelines for the NSW Site Auditor Scheme (3rd edition). This site specific DQO adopted consists of the following steps and is outlined as follows: State the problem

↓ Identify the decision

↓ Identify inputs to the decision

↓ Define the study boundaries

↓ Develop a decision rule

State the Problem

It is understood that the site is proposed for neighbourhood centre, medium density residential and public recreation uses.The ‘problem’ as it stands is that previous and existing industrial land use might have given rise to soil and groundwater contamination, as well as might impact the proposed uses and Exile Bay / Parramatta River. The sources of potential environmental concerns (PEC) within the site would be the underground fuel tanks, fill potentially be imported, asbestos and the transformer. In addition, possible off-site contaminants migrated from potential industrial activity within the adjoining eastern property to the site.

Identify the Decisions

The decisions to be made are as follows: •

Is there any data gap which is required to be addressed in order to make the site suitable for the proposed uses, after completion of 2014 and 2015 contamination investigations, recent desktop study and inspection?

Is further investigation required to adequately address the abovementioned decisions?


G EOTECHNIQUE

PTY LTD 14

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

Identify Inputs to the Decisions

The inputs into the decision process are as follows: •

Historical information (presented in Section 4.0).

Site conditions (presented in Section 5.0).

Geological and hydrogeological study (Section 6.0).

Conceptual Site Models (Section 7.0).

The following key professional personnel were involved: James Ngu Danda Sapkota An Nguyen Xiao Zhang

Senior Principal Environmental Engineer Associate (Senior Environmental Engineer) Environmental Scientist Environmental Scientist

Define the Study Boundaries

The study boundary for this investigation is defined by boundaries of the site, as shown on Drawing No 20136/1-AA1 and summarised in Section 3.0 of this report. Develop a Decision Rule

The information obtained through the following desktop study and site inspection will be used to form a decision. ▪

Desktop study of ➢

historical aerial photographs

NSW Land Registry Services records

Section 10.7 (2 & 5) Planning Certificates

NSW Environment Protection Authority (EPA) records

SafeWork NSW records

geological and soil landscape maps

groundwater data

reports (13188/2-AA, 13188/4-AA, etc.) prepared in 2014, 2015 and 2019.

An inspection for current site conditions and identification of any environmental concerns based on visual and olfactory indicators of potential contamination.


G EOTECHNIQUE

PTY LTD 15

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

9.0

RECOMMENDATIONS

The 2015 contamination assessment indicated the soil samples recovered from boreholes BH11 to BH16 (the foreshore) were unlikely to pose a risk of harm to human health and the terrestrial environment under the conditions for the proposed residential development. However, based on the above mentioned potential environmental concerns, with the consideration of the potential receptors, the potential sources and the potential exposure pathways, the following should be considered in order to make the site suitable for the proposed neighbourhood centre, medium density residential and public recreation uses. •

In accordance with the NSW EPA "Sampling Design Guidelines for Contaminated Sites", samples should be recovered from a minimum of 50 locations systematically across the site. Only 16 locations had been investigated so far. Completion of investigation for the remaining 34 locations will be required, preferable (due to access restriction) after completion of demolition of the factory the administration building, the transformer room and the gate house.

Investigation of the soil at and in the vicinity of the existing / previous underground storage tanks (UST) will also be required to determine the contamination status.

Should any new locations of concern be identified during the above proposed investigations, delineation will be required to determine the extent of contamination. The 2014 report identified Arsenic concentration of concern at BH5 (0.1-0.4m) and Benzo(a)Pyrene (BaP) concentrations of concern at BH2 (4.5-4.8m) and BH9 (2.0-2.3m). Copper and Zinc concentrations of concern were also identified at BH2 (4.5-4.8m), delineation is therefore also be required

Groundwater investigation and / or soil gas investigation would be required.

It is considered reasonable for conditional development consent to be issued to require the above recommendations. Based on the results of the testing to determine the need or otherwise for remediation. It is our opinion that based on this approach Council can be satisfied that the site can be made suitable for the proposed uses.


G EOTECHNIQUE

PTY LTD 16

Detailed Site Investigation (Round 1) Bushells Concord 20136/1 Lot 2 in DP230294, Lots 398 & 399 in DP752023, and Lot 5 in DP129325 160 Burwood Road, Concord 24 May 2022 Version 1

10.0 LIMITATIONS The services performed by Geotechnique in preparing this report were conducted in a manner consistent with the level of quality and skill generally exercised by members of the profession and consulting practice. To the best of our knowledge, all information obtained and contained in this report is true and accurate. No further investigation has been carried out to authenticate the information provided. Supporting documentations were obtained where possible, some of which are contained in this report. This report has been prepared for New Concord Development Pty Ltd and Hatch for the purpose stated within. City of Canada Bay Council can rely on the report in making development application determination. Any reliance on this report by other parties shall be at such parties' sole risk, as the report might not contain sufficient information for other purposes. This report shall only be presented in full and may not be used to support any other objective than those set out in the report, except where written approval is provided by Geotechnique. The information in this report is considered accurate at the completion of field work on 18 March 2022. Any variations to the site form or use beyond that date will nullify the conclusions and recommendations stated. Presented in Appendix I is a document entitled "Environmental Notes", which should be read in conjunction with this report.


G EOTECHNIQUE

PTY LTD

LIST OF REFERENCES •

Additional Contamination Assessment report, 160 Burwood Road, Concord, 13188/4-AA, Geotechnique, 2015

Additional geotechnical investigation report, 160 Burwood Road, Concord, 13188/3-AA, Geotechnique, 2015

Consultants reporting on contaminated land guidelines – NSW EPA, 2020

Contamination Assessment Geotechnique, 2014

Contaminated Land Management Act

Contaminated Land Management: Guidelines for the NSW Site Auditor Scheme (3rd Edition) – NSW EPA

Five Yearly Asbestos Audit For Freshfood Sydney Pty Ltd, 160 Burwood Road, Concord, NSW, Benbow Environmental, 2019

Geological Map of Sydney (Geological Series Sheet 9130, Scale 1:100,000, 1983), published by the Department of Mineral Resources

National Environment Protection (Assessment of Site Contamination) Measures, 1999 (April 2013) - National Environmental Protection Council

Protection of the Environment Operations Act

Soil Landscape Map of Sydney (soil Landscape Series Sheet 9130, Scale 1:100,000, 2002),

State “Environmental Planning Policy (Resilience and Hazards)” 2021

report,

160

Burwood

Road,

Concord,

13188/2-AA,


DRAWINGS

Drawing No. 20136/1-AA1 Drawing No. 13188/3-AA1


14

11 10 12

9

13

S/F# Description 1 Above ground liquid nitrogen, phosphorous acid and hydrochloric acid storage tanks* 2 Bitumen car park (potentially filled) in the vicinity of administration building

1

DUKE

2 4

3

UE AVEN

16 5

15 17 8 7

LEGEND Wire mesh fence

6

D ROA OOD W R U B

Imagery ©2022 NearMap.com

Open area was covered with concrete, bitumen, grass or tree

3 4 5

Scrap metal, disused furniture etc. Caustic soda * room Coffee factory

6 7 8 9 10

Gas main supply Wheelbarrow, lawn mower & diesel oil staining. Transformer room Pallets Galvanized iron shed with liquefied petroleum gas cylinders *

11 12 13 14 15 16 17 Note

Landscape area, previously occupied by building Bitumen car park Trucks manoeuvring and loading concrete area Footpath Potential underground storage tank Administration building Guardhouse *: registered with Safe Work

NOTES

G

EOTECHNIQUE

®

PTY LTD

PO Box 880 Penrith NSW 2750 Tel: 02 4722 2700 Fax: 02 4722 2777 e-mail:info@geotech.com.au www.geotech.com.au

1. Site features are indicative and are not to scale. 2. This drawing has been produced using a base plan provided by others to which additional information e.g test pits, borehole locations or notes have been added. Some or all of the plan may not be relevant at the time of producing this drawing

Bushells Site 160 Burwood Road, Concord Site Features

Drawing No: 20136/1 Job No: 20136/1 Drawn By: XZ Date: 31 March 2022 Checked By: JN File No: 20136-1 Layers: 0, AA1


BH14 BH13

BH15 BH2

BH3

BH16

BH11 BH12

BH5 BH1 BH4 BH9

BH7

DUK E

BH8

U AVEN E

BH6

BH10

W OO BU R

AD D RO

LEGEND Borehole (August 2014)

0

Imagery ©2014 NearMap.com

Borehole (July 2015)

EOTECHNIQUE

40

60

80

100m

Scale 1:2000 NOTES

G

20

®

PTY LTD

PO Box 880 Penrith NSW 2750 Tel: 02 4722 2700 Fax: 02 4722 2777 e-mail:info@geotech.com.au www.geotech.com.au

1. Site features are indicative and are not to scale. 2. This drawing has been produced using a base plan provided by others to which additional information e.g test pits, borehole locations or notes have been added. Some or all of the plan may not be relevant at the time of producing this drawing

Nix Management Pty Ltd Proposed Development Robert Timms Factory Site (Bushell’s) 160 Burwood Road, Concord Borehole Locations

Drawing No: 13188/3-AA1 Job No: 13188/3 Drawn By: MH Date: 30 July 2015 Checked By: ZA File No: 13188-3 Layers: 0, AA1


APPENDIX A

HISTORICAL AERIAL PHOTOGRAPHS


G EOTECHNIQUE

PTY LTD 1

20136/1

December 2021

November 2009 JN.mh/28.03.2022


G EOTECHNIQUE

PTY LTD 2

20136/1

2002

1994 JN.mh/28.03.2022


G EOTECHNIQUE

PTY LTD 3

20136/1

1986

1978 JN.mh/28.03.2022


G EOTECHNIQUE

PTY LTD 4

20136/1

1971

1961 JN.mh/28.03.2022


G EOTECHNIQUE

PTY LTD 5

20136/1

1951

JN.mh/28.03.2022


APPENDIX B

NSW LAND REGISTRY SERVICES RECORDS


G

EOTECHNIQUE

20136/1 Summary of Proprietors Lot 2 DP230294 Year 1998 - 2022 1984 - 1998 1966 - 1984 1966

Proprietor Freshfood Sydney Pty Limited Bushells Foods Pty Limited Bushells Pty Limited The Maritime Services Board of New South Wales

Lots 398 & 399 DP752023 & Lot 5 DP129325 (auto consol 6304-64) Year 1998 - 2022 1984 - 1998 1956 - 1984 1951 - 1956

Proprietor Freshfood Sydney Pty Limited Bushells Foods Pty Limited Bushells Pty Limited Murray Bros. Pty Limited

PTY LTD


Cadastral Records Enquiry Report : Lot 5 DP 129325

Ref : NOUSER

Locality : CONCORD

Parish : CONCORD

LGA : CANADA BAY

County : CUMBERLAND

Report Generated 11:19:22 AM, 28 March, 2022 Copyright © Crown in right of New South Wales, 2017

This information is provided as a searching aid only.Whilst every endeavour is made to ensure that current map, plan and titling information is accurately reflected, the Registrar General cannot guarantee the information provided. For ALL ACTIVITY PRIOR TO SEPTEMBER 2002 you must refer to the RGs Charting and Reference Maps

Page 1 of 3




Req:R727769 /Doc:CP 00037-2030 P /Rev:29-Oct-2014 /NSW LRS /Prt:28-Apr-2022 09:24 /Seq:1 of 1 © Office of the Registrar-General /Src:GlobalX /Ref:advlgeo


NEW SOUTH WALES LAND REGISTRY SERVICES - TITLE SEARCH ----------------------------------------------------FOLIO: 2/230294 -----SEARCH DATE ----------25/3/2022

TIME ---10:45 AM

EDITION NO ---------8

DATE ---2/7/2020

LAND ---LOT 2 IN DEPOSITED PLAN 230294 AT EXILE BAY LOCAL GOVERNMENT AREA CANADA BAY PARISH OF CONCORD COUNTY OF CUMBERLAND TITLE DIAGRAM DP230294 FIRST SCHEDULE -------------FRESHFOOD SYDNEY PTY LIMITED

(T 3930008)

SECOND SCHEDULE (2 NOTIFICATIONS) --------------1 LAND EXCLUDES MINERALS 2 DP268777 RIGHT OF FOOTWAY VARIABLE WIDTH AFFECTING THE PART(S) SHOWN SO BURDENED IN DP268777 NOTATIONS --------UNREGISTERED DEALINGS: NIL ***

advlgeo

END OF SEARCH

***

PRINTED ON 25/3/2022

Obtained from NSW LRS on 25 March 2022 09:45 AM AEST © Office of the Registrar-General 2022 * Any entries preceded by an asterisk do not appear on the current edition of the Certificate of Title. Warning: the information appearing under notations has not been formally recorded in the Register. GlobalX hereby certifies that the information contained in this document has been provided electronically by the Registrar General in accordance with Section 96B(2) of the Real Property Act 1900. Note: Information contained in this document is provided by GlobalX Pty Ltd, ABN 35 099 032 596, www.globalx.com.au an approved NSW Information Broker.


NEW SOUTH WALES LAND REGISTRY SERVICES - HISTORICAL SEARCH ---------------------------------------------------------SEARCH DATE ----------25/3/2022 10:53AM FOLIO: 2/230294 -----First Title(s): SEE PRIOR TITLE(S) Prior Title(s): VOL 10387 FOL 217 Recorded -------5/6/1987

Number ------

7/4/1988

Type of Instrument -----------------TITLE AUTOMATION PROJECT

C.T. Issue ---------LOT RECORDED FOLIO NOT CREATED

CONVERTED TO COMPUTER FOLIO

FOLIO CREATED CT NOT ISSUED

10/2/1998

3787010

CHANGE OF NAME

EDITION 1

17/2/1998

3801775

DEPARTMENTAL DEALING

EDITION 2

17/4/1998

DP268777

DEPOSITED PLAN

20/4/1998

3925989

DEPARTMENTAL DEALING

EDITION 3

21/4/1998 21/4/1998

3930008 3930009

TRANSFER MORTGAGE

EDITION 4

27/3/2001

7408114

DEPARTMENTAL DEALING

11/5/2006

AC249687

DISCHARGE OF MORTGAGE

EDITION 5

20/7/2017

AM580002

MORTGAGE

EDITION 6

22/9/2018

AN730188

DEPARTMENTAL DEALING

EDITION 7 CORD ISSUED

2/7/2020

AQ214702

DISCHARGE OF MORTGAGE

EDITION 8

***

END OF SEARCH

advlgeo Obtained from NSW LRS on 25 March 2022 09:53 AM AEST

***

PRINTED ON 25/3/2022 © Office of the Registrar-General 2022





NEW SOUTH WALES LAND REGISTRY SERVICES - TITLE SEARCH ----------------------------------------------------FOLIO: AUTO CONSOL 6304-64 -----SEARCH DATE ----------25/3/2022

TIME ---10:45 AM

EDITION NO ---------5

DATE ---2/7/2020

LAND ---LAND DESCRIBED IN SCHEDULE OF PARCELS AT CONCORD LOCAL GOVERNMENT AREA CANADA BAY PARISH OF CONCORD COUNTY OF CUMBERLAND TITLE DIAGRAM SEE SCHEDULE OF PARCELS FIRST SCHEDULE -------------FRESHFOOD SYDNEY PTY LIMITED

(T 3930008)

SECOND SCHEDULE (2 NOTIFICATIONS) --------------1 RESERVATIONS AND CONDITIONS IN THE CROWN GRANT(S) 2 T964422 LEASE TO SYDNEY COUNTY COUNCIL OF SUBSTATION LOT 1 IN DP202324, AS REGARDS TO LOT 5 IN DP129325 TOGETHER WITH RIGHT OF WAY & CABLE EASEMENT OVER ANOTHER PART OF THE LAND WITHIN DESCRIBED. EXPIRES 31.12.2030. AK971351 LEASE OF LEASE T964422 TO BLUE ASSET PARTNER PTY LTD, ERIC ALPHA ASSET CORPORATION 1 PTY LTD, ERIC ALPHA ASSET CORPORATION 2 PTY LTD, ERIC ALPHA ASSET CORPORATION 3 PTY LTD & ERIC ALPHA ASSET CORPORATION 4 PTY LTD EXPIRES: SEE DEALING. CLAUSE 2.3 (b) (ii). AK971352 LEASE OF LEASE AK971351 TO BLUE OP PARTNER PTY LTD, ERIC ALPHA OPERATOR CORPORATION 1 PTY LTD, ERIC ALPHA OPERATOR CORPORATION 2 PTY LTD, ERIC ALPHA OPERATOR CORPORATION 3 PTY LTD & ERIC ALPHA OPERATOR CORPORATION 4 PTY LTD EXPIRES: SEE DEALING. CLAUSE 12.1 AK971502 MORTGAGE OF LEASE AK971351 TO ANZ FIDUCIARY SERVICES PTY LTD AK971571 CHANGE OF NAME AFFECTING LEASE T964422 LESSEE NOW ALPHA DISTRIBUTION MINISTERIAL HOLDING CORPORATION NOTATIONS --------UNREGISTERED DEALINGS: NIL

END OF PAGE 1 - CONTINUED OVER advlgeo

PRINTED ON 25/3/2022


NEW SOUTH WALES LAND REGISTRY SERVICES - TITLE SEARCH ----------------------------------------------------FOLIO: AUTO CONSOL 6304-64 ------

PAGE

SCHEDULE OF PARCELS ------------------LOT 5 IN DP129325 LOTS 398-399 IN DP752023 ***

advlgeo

END OF SEARCH

2

TITLE DIAGRAM ------------DP129325 CROWN PLAN 37.2030. ***

PRINTED ON 25/3/2022

Obtained from NSW LRS on 25 March 2022 09:45 AM AEST © Office of the Registrar-General 2022 * Any entries preceded by an asterisk do not appear on the current edition of the Certificate of Title. Warning: the information appearing under notations has not been formally recorded in the Register. GlobalX hereby certifies that the information contained in this document has been provided electronically by the Registrar General in accordance with Section 96B(2) of the Real Property Act 1900. Note: Information contained in this document is provided by GlobalX Pty Ltd, ABN 35 099 032 596, www.globalx.com.au an approved NSW Information Broker.


NEW SOUTH WALES LAND REGISTRY SERVICES - HISTORICAL SEARCH ---------------------------------------------------------SEARCH DATE ----------25/3/2022 10:53AM FOLIO: 398/752023 -----First Title(s): SEE PRIOR TITLE(S) Prior Title(s): VOL 6304 FOL 64 Recorded -------15/12/1988

Number ------

16/2/1995 27/3/2001

7408114 ***

Type of Instrument -----------------TITLE AUTOMATION PROJECT

C.T. Issue ---------LOT RECORDED FOLIO NOT CREATED

CONVERTED TO AUTO CONSOL 6304-64

CONSOL CREATED CT NOT ISSUED

DEPARTMENTAL DEALING END OF SEARCH

advlgeo Obtained from NSW LRS on 25 March 2022 09:53 AM AEST

***

PRINTED ON 25/3/2022 © Office of the Registrar-General 2022


NEW SOUTH WALES LAND REGISTRY SERVICES - HISTORICAL SEARCH ---------------------------------------------------------SEARCH DATE ----------25/3/2022 10:53AM FOLIO: 399/752023 -----First Title(s): SEE PRIOR TITLE(S) Prior Title(s): VOL 6304 FOL 64 Recorded -------15/12/1988

Number ------

16/2/1995 27/3/2001

7408114 ***

Type of Instrument -----------------TITLE AUTOMATION PROJECT

C.T. Issue ---------LOT RECORDED FOLIO NOT CREATED

CONVERTED TO AUTO CONSOL 6304-64

CONSOL CREATED CT NOT ISSUED

DEPARTMENTAL DEALING END OF SEARCH

advlgeo Obtained from NSW LRS on 25 March 2022 09:53 AM AEST

***

PRINTED ON 25/3/2022 © Office of the Registrar-General 2022


NEW SOUTH WALES LAND REGISTRY SERVICES - HISTORICAL SEARCH ---------------------------------------------------------SEARCH DATE ----------25/3/2022 10:53AM FOLIO: 5/129325 -----First Title(s): SEE PRIOR TITLE(S) Prior Title(s): VOL 6304 FOL 64 Recorded -------13/2/1995

Number -----DP129325

Type of Instrument -----------------DEPOSITED PLAN

C.T. Issue ---------LOT RECORDED FOLIO NOT CREATED

15/2/1995

AMENDMENT: PARISH-COUNTY

16/2/1995

CONVERTED TO AUTO CONSOL 6304-64

27/3/2001

7408114 ***

CONSOL CREATED CT NOT ISSUED

DEPARTMENTAL DEALING END OF SEARCH

advlgeo Obtained from NSW LRS on 25 March 2022 09:53 AM AEST

***

PRINTED ON 25/3/2022 © Office of the Registrar-General 2022


Req:R553027 /Doc:CT 06304-064 CT /Rev:09-Aug-2012 /NSW LRS /Prt:25-Mar-2022 11:20 /Seq:1 of 4 © Office of the Registrar-General /Src:GlobalX /Ref:advlgeo


Req:R553027 /Doc:CT 06304-064 CT /Rev:09-Aug-2012 /NSW LRS /Prt:25-Mar-2022 11:20 /Seq:3 of 4 © Office of the Registrar-General /Src:GlobalX /Ref:advlgeo


APPENDIX C

SECTION 10.7 (2 & 5) PLANNING CERTIFICATES


APPLICANT:

Geotechnique Pty Ltd P O Box 880 PENRITH NSW 2750

PLANNING CERTIFICATE - under section 10.7 Environmental Planning and Assessment Act 1979

Property:

160 Burwood Road CONCORD NSW 2137

Title:

Lot 2 DP 230294

Certificate No:

PC2022/0752

Certificate Date:

29/03/2022

Receipt No:

Online Receipt

Certificate Fee:

$133.00

Land No:

33847

Applicant’s Ref:

20136/1

Canada Bay Civic Centre Drummoyne 1a Marlborough Street Drummoyne NSW 2047 Locked Bag 1470 Drummoyne NSW 1470 ABN 79 130 029 350

Tel 9911 6555 council@canadabay.nsw.gov.au www.canadabay.nsw.gov.au


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

SECTION 10.7(2) In accordance with the requirements of section 10.7(2) of the Environmental Planning and Assessment Act (1979) (“the Act”), the following prescribed matters relate to the land at the date of this certificate. ITEM 1 1.

Names of relevant planning instruments and DCPs

The following environmental planning instruments apply to the carrying out of development on the land: Canada Bay Local Environmental Plan 2013 State Environmental Planning Policy (Biodiversity and Conservation) 2021 State Environmental Planning Policy (Building Sustainability Index: BASIX) 2004 State Environmental Planning Policy (Exempt and Complying Development Codes) 2008 State Environmental Planning Policy (Housing) 2021 State Environmental Planning Policy (Industry and Employment) 2021 State Environmental Planning Policy No. 65 – Design Quality of Residential Flat Development State Environmental Planning Policy (Planning Systems) 2021 State Environmental Planning Policy (Precincts – Central River City) 2021 State Environmental Planning Policy (Primary Production) 2021 State Environmental Planning Policy (Resilience and Hazards) 2021 State Environmental Planning Policy (Resources and Energy) 2021 State Environmental Planning Policy (Transport and Infrastructure) 2021

2.

The following proposed environmental planning instruments apply to the carrying out of development on the land and are or have been the subject of community consultation or on public exhibition under the Environmental Planning and Assessment Act 1979: Planning Proposal - LEP Miscellaneous Amendments (PP2020/0002) State Environmental Planning Policy (Environment) Design and Place State Environmental Planning Policy

3.

The following development control plans apply to the carrying out of development on the land: City of Canada Bay Development Control Plan Sydney Harbour Foreshores & Waterways Area Development Control Plan

ITEM 2 1.

Zoning and land use under relevant LEPs

(a) Zoning details in the instruments identified in item 1(1) above Zone IN1 General Industrial

Page 2 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

1

Certificate Date: 29/03/2022

Objectives of zone 

To provide a wide range of industrial and warehouse land uses.

 To encourage employment opportunities.

2



To minimise any adverse effect of industry on other land uses.



To support and protect industrial land for industrial uses.

Permitted without consent Environmental protection works

3

Permitted with consent Depots; Freight transport facilities; Garden Centres; General industries; Hardware and Building Supplies; Industrial training facilities; Light industries; Neighbourhood shops; Roads; Places of Public Worship; Warehouse or distribution centres; Any other development not specified in item 2 or 4

4

Prohibited Agriculture; Air transport facilities; Airstrips; Amusement centres; Boat launching ramps; Boat sheds; Camping grounds; Caravan parks; Cemeteries; Charter and tourism boating facilities; Child care centres; Commercial premises; Community facilities; Correctional centres; Crematoria; Eco-tourist facilities; Educational establishments; Entertainment facilities; Exhibition homes; Exhibition villages; Extractive industries; Farm buildings; Forestry; Function centres; Health services facilities; Heavy industrial storage establishments; Heavy industries; Helipads; Highway service centres; Home-based child care; Home businesses; Home occupations; Home occupations (sex services); Information and education facilities; Jetties; Marinas; Mooring pens; Moorings; Open cut mining; Public administration buildings; Recreation facilities (major); Registered clubs; Research stations; Residential accommodation; Respite day care centres; Restricted premises; Rural industries; Sex services premises; Tourist and visitor accommodation; Water recreation structures; Water supply systems; Wharf or boating facilities; Wholesale supplies

Additional permitted uses No additional uses apply (b) Are there development standards applying to the land, which fix minimum land dimensions for the erection of a dwelling house on the land? No fixed minimum land dimensions apply to this land (c) Does the land include or comprise critical habitat? The land does not include or comprise critical habitat under an EPI (d) Is the land within a heritage conservation area? The land is not within a heritage conservation area (e) Is there a heritage item situated on the land? There are no heritage items situated on the land

Page 3 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

2.

Certificate Date: 29/03/2022

(a) Zoning details in the instruments identified in item 1(2) above No draft zoning applies to the land Additional permitted uses No draft additional uses apply (b) Are there development standards applying to the land, which fix minimum land dimensions for the erection of a dwelling house on the land? No fixed minimum land dimensions apply to the land under a draft environmental planning instrument (c) Does the land include or comprise critical habitat? The land does not include or comprise critical habitat under a draft EPI (d) Is the land within a draft heritage conservation area? The land is not within a draft heritage conservation area (e) Is there a draft heritage item situated on the land? There are no draft heritage items situated on the land

ITEM 2A - Zoning and land use under State Environmental Planning Policy (Sydney Region Growth Centres) 2006 Is the land identified within any zone under Part 3 of State Environmental Planning Policy (Sydney Region Growth Centres) 2006, a Precinct Plan, or a Proposed Precinct Plan that is or has been the subject of community consultation or on public exhibition under the Act? No

ITEM 3 –

Complying Development Exclusions

Is the land, land on which complying development may be carried out under clauses 1.17A(1)(c) to (e),(2),(3) and (4), 1.18 (1)(c3) and 1.19 of State Environmental Planning Policy (Exempt and Complying Development Codes) 2008? Housing Code No, to the extent that the land is affected by specific land exemptions listed below. You should consult the relevant local environmental plan maps to determine the extent of affection over the land. Land that is identified as Class 1 or 2. However, if the land exemption only applies to part of the lot the exclusion does not apply to the remainder of the lot. Refer to Acid Sulfate Soils Maps for further detail on the part of the lot that may be affected. Rural Housing Code No, to the extent that the land is affected by specific land exemptions listed below. You

Page 4 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

should consult the relevant local environmental plan maps to determine the extent of affection over the land.

Low Rise Housing Diversity Code No, to the extent that the land is affected by specific land exemptions listed below. You should consult the relevant local environmental plan maps to determine the extent of affection over the land. Land that is identified as Class 1 or 2. However, if the land exemption only applies to part of the lot the exclusion does not apply to the remainder of the lot. Refer to Acid Sulfate Soils Maps for further detail on the part of the lot that may be affected. Greenfield Housing Code No, to the extent that the land is affected by specific land exemptions listed below. You should consult the relevant local environmental plan maps to determine the extent of affection over the land. Land that is identified as Class 1 or 2. However, if the land exemption only applies to part of the lot the exclusion does not apply to the remainder of the lot. Refer to Acid Sulfate Soils Maps for further detail on the part of the lot that may be affected. Inland Code No, to the extent that the land is affected by specific land exemptions listed below. You should consult the relevant local environmental plan maps to determine the extent of affection over the land. Land that is identified as Class 1 or 2. However, if the land exemption only applies to part of the lot the exclusion does not apply to the remainder of the lot. Refer to Acid Sulfate Soils Maps for further detail on the part of the lot that may be affected. Housing Alterations Code Yes, under the Housing Alterations Code complying development may be carried out on the land.

General Development Code Yes, under the General Development Code complying development may be carried out on the land.

Commercial and Industrial Alterations Code Yes, under the General Commercial and Industrial Code complying development may be carried out on the land.

Commercial and Industrial (New Buildings and Additions) Code No, to the extent that the land is affected by specific land exemptions listed below. You should consult the relevant local environmental plan maps to determine the extent of affection over the land. Land that is identified as Class 1 or 2. However, if the land exemption only applies to part

Page 5 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

of the lot the exclusion does not apply to the remainder of the lot. Refer to Acid Sulfate Soils Maps for further detail on the part of the lot that may be affected. Container Recycling Facilities Code Yes, under the Container Recycling Facilities Code complying development may be carried out on the land.

Subdivisions Code Yes, under the Subdivisions Code complying development may be carried out on the land.

Demolition Code Yes, under the Demolition Code complying development may be carried out on the land.

Fire Safety Code Yes, under the Fire Safety Code complying development may be carried out on the land.

ITEM 4 – Repealed

ITEM 4A – Repealed

ITEM 4B – Annual charges under Local Government Act 1993 for coastal protection services that relate to existing coastal protection works Has the owner (or any previous owner) of the land consented in writing to the land being subject to annual charges under section 496B of the Local Government Act 1993 for coastal protection services that relate to existing coastal protection works (within the meaning of section 553B of that Act)? No

ITEM 5 –

Mine subsidence

Is the land proclaimed to be in a mine subsidence district within the meaning of section 15 of the Mine Subsidence Compensation Act 1961? No

ITEM 6 –

Road widening and road realignment

Is the land affected by any road widening or road realignment under: (a) Division 2 of Part 3 of the Roads Act 1993; or (b) Any environmental planning instrument; or

Page 6 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

(c) Any resolution of the Council? No

ITEM 7 – Council and other public authority policies on hazard risk restrictions (a)

Whether or not the land is affected by a policy adopted by the Council that restricts the development of the land because of the likelihood of:(i)

land slip

No

(ii)

bushfire

No

(iii)

tidal inundation

No

(iv)

subsidence

No

(v)

acid sulphate soils

Yes

The land is identified as being within Class 2 on the Acid Sulfate Soil Map under the Canada Bay LEP 2013. Works prohibited without Council approval (except as provided by subclause 4 of clause 6.1 of the Canada Bay LEP 2013) include:

(vi)



Works below the natural ground surface



Works by which the watertable is likely to be lowered.

land contamination

Yes

Council has adopted by resolution a policy on contaminated land that applies to all land within the City of Canada Bay. Please note that this statement refers to whether or not Council has a policy regarding contamination and is not a statement on whether the property is affected by contamination or potential contamination. (b)

Whether or not the land is affected by a policy adopted by any other public authority and notified to the Council for the express purpose of its adoption by that authority being referred to in planning certificates issued by the Council that restricts the development of the land because of the likelihood of:(i)

land slip

No

(ii)

bushfire

No

(iii)

tidal inundation

No

(iv)

subsidence

No

(v)

acid sulphate soils

No

(vi)

land contamination

No

ITEM 7A – Flood related development controls 1.

If the land or part of the land is within the flood planning area and subject to flood related development controls.

Page 7 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

No

2.

If the land or part of the land is between the flood planning area and the probable maximum flood and subject to flood related development controls. Yes, please refer to Council’s Planning Controls webpage for more information on Flood Planning.

ITEM 8 –

Land reserved for acquisition

Is there an environmental planning instrument, or proposed environmental planning instrument referred to in clause 1 which makes provision in relation to the acquisition of the land by a public authority, as referred to in section 3.15 of the Environmental Planning and Assessment Act 1979? No

ITEM 9 –

Contributions plans

The name of each contributions plan applying to the land is:City of Canada Bay Local Infrastructure Contributions Plan City of Canada Bay Affordable Housing Contributions Scheme

ITEM 9A - Biodiversity certified land Is the land biodiversity certified land under Part 8 of the Biodiversity Conservation Act 2016 (including land certified under Part 7AA of the Threatened Species Conservation Act 1995)? No

ITEM 10 – Biodiversity stewardship sites Has Council been notified by the Chief Executive of the Office of Environment and Heritage that the land is a biodiversity stewardship site under a biodiversity stewardship agreement under Part 5 of the Biodiversity Conservation Act 2016 (including biobanking agreements under Part 7A of the Threatened Species Conservation Act 1995)? No

ITEM 10A – Native vegetation clearing set asides

Page 8 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

Under section 60ZC of the Local Land Service Act 2013, has Council been notified by Local Land Services (or is it registered in the public register under that section) that the land contains a set aside area? No

ITEM 11 – Bush fire prone land (a) (b) (c)

All of the land is bush fire prone land. Some of the land is bush fire prone land. None of the land is bush fire prone land.

No No Yes

ITEM 12 – Property vegetation plans Has Council been notified (by the person or body that approved the plan) of the existence of a property vegetation plan approved under Part 4 of the Native Vegetation Act 2003 (and that continues in force) applying to the land? No

ITEM 13 – Orders under Trees (Disputes Between Neighbours) Act 2006 Has Council been notified that an order has been made under the Trees (Disputes Between Neighbours) Act 2006 to carry out work in relation to a tree on the land? No

ITEM 14 – Directions under Part 3A Is there a direction by the Minister in force under section 75P (2) (c1) of the Environmental Planning and Assessment Act 1979 that a provision of an environmental planning instrument prohibiting or restricting the carrying out of a project or a stage of a project on the land under Part 4 of the Act does not have effect? No

ITEM 15 – Site compatibility certificates and conditions for seniors housing (a)

Has a current site compatibility certificate (seniors housing), of which the Council is aware, been issued under State Environmental Planning Policy (Housing for Seniors or People with a Disability) 2004 in respect of proposed development on the land? No

(b)

Have any terms of a kind referred to in clause 18(2) of State Environmental Planning Policy (Housing for Seniors or People with a Disability) 2004 been imposed as a condition of consent to a development application granted after 11 October 2007 in respect of the land? No

Page 9 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

ITEM 16 – Site compatibility certificates for infrastructure, schools or TAFE establishments Has a valid site compatibility certificate (infrastructure) or a site compatibility certificate (schools or TAFE establishments),of which the Council is aware, been issued? No

ITEM 17 – Site compatibility certificates and conditions for affordable rental housing 1.

Has a current site compatibility certificate (affordable rental housing), of which the Council is aware, been issued in respect of proposed development on the land? No

2.

Have any terms of a kind referred to in clause 17(1) or 38(1) of State Environmental Planning Policy (Affordable Rental Housing) 2009 been imposed as a condition of consent to a development application in respect of the land? No

ITEM 18 – Paper subdivision information Has a development plan been adopted that applies to the land or that is proposed to be subject to a consent ballot? No

ITEM 19 – Site verification certificates Has Council been made aware of a current site verification certificate that has been issued in respect of the land? No

ITEM 20 – Loose – fill asbestos insulation Has Council been notified that the land includes any residential premises (within the meaning of Division 1A of Part 8 of the Home Building Act 1989) that are listed on the register that is required to be maintained under that Division? No. Contact NSW Fair Trading for more information.

ITEM 21 – Affected building notices and building product rectification orders 1.

Is any affected building notice in force in respect of the land? No

Page 10 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

2.

Certificate Date: 29/03/2022

Is any building product rectification order in force in respect of the land that has not been fully complied with? No

3.

Has a notice of intention to make a building product rectification order been given in respect of that land that is outstanding? No

ITEM 22 – Matters arising under the Contaminated Land Management Act 1997 Section 59(2) of the Contaminated Land Management Act 1997 prescribes the following additional matters to be specified in planning certificates:(a)

At the date of this certificate, is the land (or part of the land) to which this certificate relates significantly contaminated land? No

(b)

At the date of this certificate, is the land to which this certificate relates subject to a management order? No

(c)

At the date of this certificate, is the land to which this certificate relates the subject of an approved voluntary management proposal? No

(d)

At the date of this certificate, is the land to which this certificate relates subject to an ongoing maintenance order? No

(e)

At the date of this certificate, is the land to which this certificate relates the subject of a site audit statement and a copy of such a statement has been provided to the Council? No

SECTION 10.7(5) ADVICE In accordance with section 10.7(5) of the Act the following advice is given on other relevant matters affecting the land. 1.

Demolition Under the local environmental plan applying to the land, development consent is required for the demolition of any building on the land except where the demolition complies with the exempt development requirements specified in State Environmental Planning Policy (Exempt and Complying Development Codes) 2008 and the Canada Bay Local Environmental Plan, 2013.

Page 11 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

2.

Certificate Date: 29/03/2022

Foreshore Building Line Is the land affected by a foreshore building line? No

3.

Other Heritage considerations Is the land adjoining or opposite a heritage item under the provisions of the Local Environmental Plan applying to the land? Yes

Has the property been identified as one that is contributory to the heritage values of a conservation area? No Is the land adjoining or opposite a heritage conservation area under the provisions of the Local Environmental Plan applying to the land? No Does the land contain an item of environmental heritage identified within the Sydney Regional Environmental Plan (Sydney Harbour Catchment) 2005? No 4.

Aircraft Noise Is the land affected by aircraft noise? The property could be affected by aircraft noise. For further details contact Airservices Australia (www.airservices.gov.au), or refer to Council’s Public Mapping Service (www.canadabay.nsw.gov.au/eservices/publicmappingservice).

5.

Other Advice The Council commissioned a flood study which applies to this land. Please refer to the Draft Exile Bay Flood Study for more information.

GENERAL INFORMATION The absence of any reference to a matter affecting the land shall not imply that the land is not affected by that matter not referred to in this certificate. Information provided under section 10.7(2) is in accordance with the matters prescribed under schedule 4 of the Environmental Planning and Assessment Regulation 2000 and is provided only to the extent that the Council has been notified by the Department of Public Works or Department of Planning.

Page 12 of 13


Certificate No.: PC2022/0752

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

When advice in accordance with section 10.7(5) is requested the Council is under no obligation to furnish any advice. If advice is provided Council draws your attention to section 10.7(6) and schedule 6 of the Environmental Planning and Assessment Act 1979 which have the effect that Council shall not incur any liability in respect of advice provided in good faith pursuant to section 10.7(5), including the furnishing of advice in respect of contaminated land. Any enquiries regarding State and Regional Environmental Planning Policies should be directed to the Department of Planning at http:// www.planning.nsw.gov.au Please contact Council’s Strategic Planning section for further information about this Planning Certificate.

John Clark General Manager

Page 13 of 13


APPLICANT:

Geotechnique Pty Ltd P O Box 880 PENRITH NSW 2750

PLANNING CERTIFICATE - under section 10.7 Environmental Planning and Assessment Act 1979

Property:

160 Burwood Road CONCORD NSW 2137

Title:

Lot 398 DP 752023

Certificate No:

PC2022/0753

Certificate Date:

29/03/2022

Receipt No:

Online Receipt

Certificate Fee:

$133.00

Land No:

33845

Applicant’s Ref:

20136/1

Canada Bay Civic Centre Drummoyne 1a Marlborough Street Drummoyne NSW 2047 Locked Bag 1470 Drummoyne NSW 1470 ABN 79 130 029 350

Tel 9911 6555 council@canadabay.nsw.gov.au www.canadabay.nsw.gov.au


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

SECTION 10.7(2) In accordance with the requirements of section 10.7(2) of the Environmental Planning and Assessment Act (1979) (“the Act”), the following prescribed matters relate to the land at the date of this certificate. ITEM 1 1.

Names of relevant planning instruments and DCPs

The following environmental planning instruments apply to the carrying out of development on the land: Canada Bay Local Environmental Plan 2013 State Environmental Planning Policy (Biodiversity and Conservation) 2021 State Environmental Planning Policy (Building Sustainability Index: BASIX) 2004 State Environmental Planning Policy (Exempt and Complying Development Codes) 2008 State Environmental Planning Policy (Housing) 2021 State Environmental Planning Policy (Industry and Employment) 2021 State Environmental Planning Policy No. 65 – Design Quality of Residential Flat Development State Environmental Planning Policy (Planning Systems) 2021 State Environmental Planning Policy (Precincts – Central River City) 2021 State Environmental Planning Policy (Primary Production) 2021 State Environmental Planning Policy (Resilience and Hazards) 2021 State Environmental Planning Policy (Resources and Energy) 2021 State Environmental Planning Policy (Transport and Infrastructure) 2021

2.

The following proposed environmental planning instruments apply to the carrying out of development on the land and are or have been the subject of community consultation or on public exhibition under the Environmental Planning and Assessment Act 1979: Planning Proposal - LEP Miscellaneous Amendments (PP2020/0002) State Environmental Planning Policy (Environment) Design and Place State Environmental Planning Policy

3.

The following development control plans apply to the carrying out of development on the land: City of Canada Bay Development Control Plan Sydney Harbour Foreshores & Waterways Area Development Control Plan

ITEM 2 1.

Zoning and land use under relevant LEPs

(a) Zoning details in the instruments identified in item 1(1) above Zone IN1 General Industrial

Page 2 of 12


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

1

Certificate Date: 29/03/2022

Objectives of zone 

To provide a wide range of industrial and warehouse land uses.

 To encourage employment opportunities.

2



To minimise any adverse effect of industry on other land uses.



To support and protect industrial land for industrial uses.

Permitted without consent Environmental protection works

3

Permitted with consent Depots; Freight transport facilities; Garden Centres; General industries; Hardware and Building Supplies; Industrial training facilities; Light industries; Neighbourhood shops; Roads; Places of Public Worship; Warehouse or distribution centres; Any other development not specified in item 2 or 4

4

Prohibited Agriculture; Air transport facilities; Airstrips; Amusement centres; Boat launching ramps; Boat sheds; Camping grounds; Caravan parks; Cemeteries; Charter and tourism boating facilities; Child care centres; Commercial premises; Community facilities; Correctional centres; Crematoria; Eco-tourist facilities; Educational establishments; Entertainment facilities; Exhibition homes; Exhibition villages; Extractive industries; Farm buildings; Forestry; Function centres; Health services facilities; Heavy industrial storage establishments; Heavy industries; Helipads; Highway service centres; Home-based child care; Home businesses; Home occupations; Home occupations (sex services); Information and education facilities; Jetties; Marinas; Mooring pens; Moorings; Open cut mining; Public administration buildings; Recreation facilities (major); Registered clubs; Research stations; Residential accommodation; Respite day care centres; Restricted premises; Rural industries; Sex services premises; Tourist and visitor accommodation; Water recreation structures; Water supply systems; Wharf or boating facilities; Wholesale supplies

Additional permitted uses No additional uses apply (b) Are there development standards applying to the land, which fix minimum land dimensions for the erection of a dwelling house on the land? No fixed minimum land dimensions apply to this land (c) Does the land include or comprise critical habitat? The land does not include or comprise critical habitat under an EPI (d) Is the land within a heritage conservation area? The land is not within a heritage conservation area (e) Is there a heritage item situated on the land? There are no heritage items situated on the land

Page 3 of 12


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

2.

Certificate Date: 29/03/2022

(a) Zoning details in the instruments identified in item 1(2) above No draft zoning applies to the land Additional permitted uses No draft additional uses apply (b) Are there development standards applying to the land, which fix minimum land dimensions for the erection of a dwelling house on the land? No fixed minimum land dimensions apply to the land under a draft environmental planning instrument (c) Does the land include or comprise critical habitat? The land does not include or comprise critical habitat under a draft EPI (d) Is the land within a draft heritage conservation area? The land is not within a draft heritage conservation area (e) Is there a draft heritage item situated on the land? There are no draft heritage items situated on the land

ITEM 2A - Zoning and land use under State Environmental Planning Policy (Sydney Region Growth Centres) 2006 Is the land identified within any zone under Part 3 of State Environmental Planning Policy (Sydney Region Growth Centres) 2006, a Precinct Plan, or a Proposed Precinct Plan that is or has been the subject of community consultation or on public exhibition under the Act? No

ITEM 3 –

Complying Development Exclusions

Is the land, land on which complying development may be carried out under clauses 1.17A(1)(c) to (e),(2),(3) and (4), 1.18 (1)(c3) and 1.19 of State Environmental Planning Policy (Exempt and Complying Development Codes) 2008? Housing Code Yes, under the Housing Code complying development may be carried out on the land.

Rural Housing Code Yes, under the Rural Housing Code complying development may be carried out on the land.

Low Rise Housing Diversity Code Yes, under the Low Rise Housing Diversity Code complying development may be carried out on the land.

Page 4 of 12


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

Greenfield Housing Code Yes, under the Greenfield Housing Code complying development may be carried out on the land.

Inland Code Yes, under the Inland Housing Code complying development may be carried out on the land.

Housing Alterations Code Yes, under the Housing Alterations Code complying development may be carried out on the land.

General Development Code Yes, under the General Development Code complying development may be carried out on the land.

Commercial and Industrial Alterations Code Yes, under the General Commercial and Industrial Code complying development may be carried out on the land.

Commercial and Industrial (New Buildings and Additions) Code Yes, under the General Commercial and Industrial (New Buildings and Additions) Code complying development may be carried out on the land.

Container Recycling Facilities Code Yes, under the Container Recycling Facilities Code complying development may be carried out on the land.

Subdivisions Code Yes, under the Subdivisions Code complying development may be carried out on the land.

Demolition Code Yes, under the Demolition Code complying development may be carried out on the land.

Fire Safety Code Yes, under the Fire Safety Code complying development may be carried out on the land.

ITEM 4 – Repealed

ITEM 4A – Repealed

Page 5 of 12


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

ITEM 4B – Annual charges under Local Government Act 1993 for coastal protection services that relate to existing coastal protection works Has the owner (or any previous owner) of the land consented in writing to the land being subject to annual charges under section 496B of the Local Government Act 1993 for coastal protection services that relate to existing coastal protection works (within the meaning of section 553B of that Act)? No

ITEM 5 –

Mine subsidence

Is the land proclaimed to be in a mine subsidence district within the meaning of section 15 of the Mine Subsidence Compensation Act 1961? No

ITEM 6 –

Road widening and road realignment

Is the land affected by any road widening or road realignment under: (a) Division 2 of Part 3 of the Roads Act 1993; or (b) Any environmental planning instrument; or (c) Any resolution of the Council? No

ITEM 7 – Council and other public authority policies on hazard risk restrictions (a)

Whether or not the land is affected by a policy adopted by the Council that restricts the development of the land because of the likelihood of:(i)

land slip

No

(ii)

bushfire

No

(iii)

tidal inundation

No

(iv)

subsidence

No

(v)

acid sulphate soils

Yes

The land is identified as being within Class 5 on the Acid Sulfate Soil Map under the Canada Bay LEP 2013. Works prohibited without Council approval (except as provided by subclause 4 of clause 6.1 of the Canada Bay LEP 2013) include:  Works within 500 metres of adjacent Class 1, 2, 3 or 4 land that is below 5 metres Australian Height Datum by which the watertable is likely to be lowered below 1 metre Australian Height Datum on adjacent Class 1, 2, 3 or 4 land.

Page 6 of 12


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

(vi)

land contamination

Certificate Date: 29/03/2022

Yes

Council has adopted by resolution a policy on contaminated land that applies to all land within the City of Canada Bay. Please note that this statement refers to whether or not Council has a policy regarding contamination and is not a statement on whether the property is affected by contamination or potential contamination. (b)

Whether or not the land is affected by a policy adopted by any other public authority and notified to the Council for the express purpose of its adoption by that authority being referred to in planning certificates issued by the Council that restricts the development of the land because of the likelihood of:(i)

land slip

No

(ii)

bushfire

No

(iii)

tidal inundation

No

(iv)

subsidence

No

(v)

acid sulphate soils

No

(vi)

land contamination

No

ITEM 7A – Flood related development controls 1.

If the land or part of the land is within the flood planning area and subject to flood related development controls.

No

2.

If the land or part of the land is between the flood planning area and the probable maximum flood and subject to flood related development controls. Yes, please refer to Council’s Planning Controls webpage for more information on Flood Planning.

ITEM 8 –

Land reserved for acquisition

Is there an environmental planning instrument, or proposed environmental planning instrument referred to in clause 1 which makes provision in relation to the acquisition of the land by a public authority, as referred to in section 3.15 of the Environmental Planning and Assessment Act 1979? No

ITEM 9 –

Contributions plans

Page 7 of 12


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

The name of each contributions plan applying to the land is:City of Canada Bay Local Infrastructure Contributions Plan City of Canada Bay Affordable Housing Contributions Scheme

ITEM 9A - Biodiversity certified land Is the land biodiversity certified land under Part 8 of the Biodiversity Conservation Act 2016 (including land certified under Part 7AA of the Threatened Species Conservation Act 1995)? No

ITEM 10 – Biodiversity stewardship sites Has Council been notified by the Chief Executive of the Office of Environment and Heritage that the land is a biodiversity stewardship site under a biodiversity stewardship agreement under Part 5 of the Biodiversity Conservation Act 2016 (including biobanking agreements under Part 7A of the Threatened Species Conservation Act 1995)? No

ITEM 10A – Native vegetation clearing set asides Under section 60ZC of the Local Land Service Act 2013, has Council been notified by Local Land Services (or is it registered in the public register under that section) that the land contains a set aside area? No

ITEM 11 – Bush fire prone land (a) (b) (c)

All of the land is bush fire prone land. Some of the land is bush fire prone land. None of the land is bush fire prone land.

No No Yes

ITEM 12 – Property vegetation plans Has Council been notified (by the person or body that approved the plan) of the existence of a property vegetation plan approved under Part 4 of the Native Vegetation Act 2003 (and that continues in force) applying to the land? No

ITEM 13 – Orders under Trees (Disputes Between Neighbours) Act 2006 Has Council been notified that an order has been made under the Trees (Disputes Between Neighbours) Act 2006 to carry out work in relation to a tree on the land?

Page 8 of 12


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

No

ITEM 14 – Directions under Part 3A Is there a direction by the Minister in force under section 75P (2) (c1) of the Environmental Planning and Assessment Act 1979 that a provision of an environmental planning instrument prohibiting or restricting the carrying out of a project or a stage of a project on the land under Part 4 of the Act does not have effect? No

ITEM 15 – Site compatibility certificates and conditions for seniors housing (a)

Has a current site compatibility certificate (seniors housing), of which the Council is aware, been issued under State Environmental Planning Policy (Housing for Seniors or People with a Disability) 2004 in respect of proposed development on the land? No

(b)

Have any terms of a kind referred to in clause 18(2) of State Environmental Planning Policy (Housing for Seniors or People with a Disability) 2004 been imposed as a condition of consent to a development application granted after 11 October 2007 in respect of the land? No

ITEM 16 – Site compatibility certificates for infrastructure, schools or TAFE establishments Has a valid site compatibility certificate (infrastructure) or a site compatibility certificate (schools or TAFE establishments),of which the Council is aware, been issued? No

ITEM 17 – Site compatibility certificates and conditions for affordable rental housing 1.

Has a current site compatibility certificate (affordable rental housing), of which the Council is aware, been issued in respect of proposed development on the land? No

2.

Have any terms of a kind referred to in clause 17(1) or 38(1) of State Environmental Planning Policy (Affordable Rental Housing) 2009 been imposed as a condition of consent to a development application in respect of the land? No

ITEM 18 – Paper subdivision information

Page 9 of 12


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

Has a development plan been adopted that applies to the land or that is proposed to be subject to a consent ballot? No

ITEM 19 – Site verification certificates Has Council been made aware of a current site verification certificate that has been issued in respect of the land? No

ITEM 20 – Loose – fill asbestos insulation Has Council been notified that the land includes any residential premises (within the meaning of Division 1A of Part 8 of the Home Building Act 1989) that are listed on the register that is required to be maintained under that Division? No. Contact NSW Fair Trading for more information.

ITEM 21 – Affected building notices and building product rectification orders 1.

Is any affected building notice in force in respect of the land? No

2.

Is any building product rectification order in force in respect of the land that has not been fully complied with? No

3.

Has a notice of intention to make a building product rectification order been given in respect of that land that is outstanding? No

ITEM 22 – Matters arising under the Contaminated Land Management Act 1997 Section 59(2) of the Contaminated Land Management Act 1997 prescribes the following additional matters to be specified in planning certificates:(a)

At the date of this certificate, is the land (or part of the land) to which this certificate relates significantly contaminated land? No

(b)

At the date of this certificate, is the land to which this certificate relates subject to a management order? No

Page 10 of 12


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

(c)

Certificate Date: 29/03/2022

At the date of this certificate, is the land to which this certificate relates the subject of an approved voluntary management proposal? No

(d)

At the date of this certificate, is the land to which this certificate relates subject to an ongoing maintenance order? No

(e)

At the date of this certificate, is the land to which this certificate relates the subject of a site audit statement and a copy of such a statement has been provided to the Council? No

SECTION 10.7(5) ADVICE In accordance with section 10.7(5) of the Act the following advice is given on other relevant matters affecting the land. 1.

Demolition Under the local environmental plan applying to the land, development consent is required for the demolition of any building on the land except where the demolition complies with the exempt development requirements specified in State Environmental Planning Policy (Exempt and Complying Development Codes) 2008 and the Canada Bay Local Environmental Plan, 2013.

2.

Foreshore Building Line Is the land affected by a foreshore building line? No

3.

Other Heritage considerations Is the land adjoining or opposite a heritage item under the provisions of the Local Environmental Plan applying to the land? No Has the property been identified as one that is contributory to the heritage values of a conservation area? No Is the land adjoining or opposite a heritage conservation area under the provisions of the Local Environmental Plan applying to the land? No Does the land contain an item of environmental heritage identified within the Sydney Regional Environmental Plan (Sydney Harbour Catchment) 2005?

Page 11 of 12


Certificate No.: PC2022/0753

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

No 4.

Aircraft Noise Is the land affected by aircraft noise? The property could be affected by aircraft noise. For further details contact Airservices Australia (www.airservices.gov.au), or refer to Council’s Public Mapping Service (www.canadabay.nsw.gov.au/eservices/publicmappingservice).

5.

Other Advice The Council commissioned a flood study which applies to this land. Please refer to the Draft Exile Bay Flood Study for more information.

GENERAL INFORMATION The absence of any reference to a matter affecting the land shall not imply that the land is not affected by that matter not referred to in this certificate. Information provided under section 10.7(2) is in accordance with the matters prescribed under schedule 4 of the Environmental Planning and Assessment Regulation 2000 and is provided only to the extent that the Council has been notified by the Department of Public Works or Department of Planning. When advice in accordance with section 10.7(5) is requested the Council is under no obligation to furnish any advice. If advice is provided Council draws your attention to section 10.7(6) and schedule 6 of the Environmental Planning and Assessment Act 1979 which have the effect that Council shall not incur any liability in respect of advice provided in good faith pursuant to section 10.7(5), including the furnishing of advice in respect of contaminated land. Any enquiries regarding State and Regional Environmental Planning Policies should be directed to the Department of Planning at http:// www.planning.nsw.gov.au Please contact Council’s Strategic Planning section for further information about this Planning Certificate.

John Clark General Manager

Page 12 of 12


APPLICANT:

Geotechnique Pty Ltd P O Box 880 PENRITH NSW 2750

PLANNING CERTIFICATE - under section 10.7 Environmental Planning and Assessment Act 1979

Property:

160 Burwood Road CONCORD NSW 2137

Title:

Lot 399 DP 752023

Certificate No:

PC2022/0754

Certificate Date:

29/03/2022

Receipt No:

Online Receipt

Certificate Fee:

$133.00

Land No:

33846

Applicant’s Ref:

20136/1

Canada Bay Civic Centre Drummoyne 1a Marlborough Street Drummoyne NSW 2047 Locked Bag 1470 Drummoyne NSW 1470 ABN 79 130 029 350

Tel 9911 6555 council@canadabay.nsw.gov.au www.canadabay.nsw.gov.au


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

SECTION 10.7(2) In accordance with the requirements of section 10.7(2) of the Environmental Planning and Assessment Act (1979) (“the Act”), the following prescribed matters relate to the land at the date of this certificate. ITEM 1 1.

Names of relevant planning instruments and DCPs

The following environmental planning instruments apply to the carrying out of development on the land: Canada Bay Local Environmental Plan 2013 State Environmental Planning Policy (Biodiversity and Conservation) 2021 State Environmental Planning Policy (Building Sustainability Index: BASIX) 2004 State Environmental Planning Policy (Exempt and Complying Development Codes) 2008 State Environmental Planning Policy (Housing) 2021 State Environmental Planning Policy (Industry and Employment) 2021 State Environmental Planning Policy No. 65 – Design Quality of Residential Flat Development State Environmental Planning Policy (Planning Systems) 2021 State Environmental Planning Policy (Precincts – Central River City) 2021 State Environmental Planning Policy (Primary Production) 2021 State Environmental Planning Policy (Resilience and Hazards) 2021 State Environmental Planning Policy (Resources and Energy) 2021 State Environmental Planning Policy (Transport and Infrastructure) 2021

2.

The following proposed environmental planning instruments apply to the carrying out of development on the land and are or have been the subject of community consultation or on public exhibition under the Environmental Planning and Assessment Act 1979: Planning Proposal - LEP Miscellaneous Amendments (PP2020/0002) State Environmental Planning Policy (Environment) Design and Place State Environmental Planning Policy

3.

The following development control plans apply to the carrying out of development on the land: City of Canada Bay Development Control Plan Sydney Harbour Foreshores & Waterways Area Development Control Plan

ITEM 2 1.

Zoning and land use under relevant LEPs

(a) Zoning details in the instruments identified in item 1(1) above Zone IN1 General Industrial

Page 2 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

1

Certificate Date: 29/03/2022

Objectives of zone 

To provide a wide range of industrial and warehouse land uses.

 To encourage employment opportunities.

2



To minimise any adverse effect of industry on other land uses.



To support and protect industrial land for industrial uses.

Permitted without consent Environmental protection works

3

Permitted with consent Depots; Freight transport facilities; Garden Centres; General industries; Hardware and Building Supplies; Industrial training facilities; Light industries; Neighbourhood shops; Roads; Places of Public Worship; Warehouse or distribution centres; Any other development not specified in item 2 or 4

4

Prohibited Agriculture; Air transport facilities; Airstrips; Amusement centres; Boat launching ramps; Boat sheds; Camping grounds; Caravan parks; Cemeteries; Charter and tourism boating facilities; Child care centres; Commercial premises; Community facilities; Correctional centres; Crematoria; Eco-tourist facilities; Educational establishments; Entertainment facilities; Exhibition homes; Exhibition villages; Extractive industries; Farm buildings; Forestry; Function centres; Health services facilities; Heavy industrial storage establishments; Heavy industries; Helipads; Highway service centres; Home-based child care; Home businesses; Home occupations; Home occupations (sex services); Information and education facilities; Jetties; Marinas; Mooring pens; Moorings; Open cut mining; Public administration buildings; Recreation facilities (major); Registered clubs; Research stations; Residential accommodation; Respite day care centres; Restricted premises; Rural industries; Sex services premises; Tourist and visitor accommodation; Water recreation structures; Water supply systems; Wharf or boating facilities; Wholesale supplies

Additional permitted uses No additional uses apply (b) Are there development standards applying to the land, which fix minimum land dimensions for the erection of a dwelling house on the land? No fixed minimum land dimensions apply to this land (c) Does the land include or comprise critical habitat? The land does not include or comprise critical habitat under an EPI (d) Is the land within a heritage conservation area? The land is not within a heritage conservation area (e) Is there a heritage item situated on the land? There are no heritage items situated on the land

Page 3 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

2.

Certificate Date: 29/03/2022

(a) Zoning details in the instruments identified in item 1(2) above No draft zoning applies to the land Additional permitted uses No draft additional uses apply (b) Are there development standards applying to the land, which fix minimum land dimensions for the erection of a dwelling house on the land? No fixed minimum land dimensions apply to the land under a draft environmental planning instrument (c) Does the land include or comprise critical habitat? The land does not include or comprise critical habitat under a draft EPI (d) Is the land within a draft heritage conservation area? The land is not within a draft heritage conservation area (e) Is there a draft heritage item situated on the land? There are no draft heritage items situated on the land

ITEM 2A - Zoning and land use under State Environmental Planning Policy (Sydney Region Growth Centres) 2006 Is the land identified within any zone under Part 3 of State Environmental Planning Policy (Sydney Region Growth Centres) 2006, a Precinct Plan, or a Proposed Precinct Plan that is or has been the subject of community consultation or on public exhibition under the Act? No

ITEM 3 –

Complying Development Exclusions

Is the land, land on which complying development may be carried out under clauses 1.17A(1)(c) to (e),(2),(3) and (4), 1.18 (1)(c3) and 1.19 of State Environmental Planning Policy (Exempt and Complying Development Codes) 2008? Housing Code No, to the extent that the land is affected by specific land exemptions listed below. You should consult the relevant local environmental plan maps to determine the extent of affection over the land. Land that is identified as Class 1 or 2. However, if the land exemption only applies to part of the lot the exclusion does not apply to the remainder of the lot. Refer to Acid Sulfate Soils Maps for further detail on the part of the lot that may be affected. Rural Housing Code No, to the extent that the land is affected by specific land exemptions listed below. You

Page 4 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

should consult the relevant local environmental plan maps to determine the extent of affection over the land.

Low Rise Housing Diversity Code No, to the extent that the land is affected by specific land exemptions listed below. You should consult the relevant local environmental plan maps to determine the extent of affection over the land. Land that is identified as Class 1 or 2. However, if the land exemption only applies to part of the lot the exclusion does not apply to the remainder of the lot. Refer to Acid Sulfate Soils Maps for further detail on the part of the lot that may be affected. Greenfield Housing Code No, to the extent that the land is affected by specific land exemptions listed below. You should consult the relevant local environmental plan maps to determine the extent of affection over the land. Land that is identified as Class 1 or 2. However, if the land exemption only applies to part of the lot the exclusion does not apply to the remainder of the lot. Refer to Acid Sulfate Soils Maps for further detail on the part of the lot that may be affected. Inland Code No, to the extent that the land is affected by specific land exemptions listed below. You should consult the relevant local environmental plan maps to determine the extent of affection over the land. Land that is identified as Class 1 or 2. However, if the land exemption only applies to part of the lot the exclusion does not apply to the remainder of the lot. Refer to Acid Sulfate Soils Maps for further detail on the part of the lot that may be affected. Housing Alterations Code Yes, under the Housing Alterations Code complying development may be carried out on the land.

General Development Code Yes, under the General Development Code complying development may be carried out on the land.

Commercial and Industrial Alterations Code Yes, under the General Commercial and Industrial Code complying development may be carried out on the land.

Commercial and Industrial (New Buildings and Additions) Code No, to the extent that the land is affected by specific land exemptions listed below. You should consult the relevant local environmental plan maps to determine the extent of affection over the land. Land that is identified as Class 1 or 2. However, if the land exemption only applies to part

Page 5 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

of the lot the exclusion does not apply to the remainder of the lot. Refer to Acid Sulfate Soils Maps for further detail on the part of the lot that may be affected. Container Recycling Facilities Code Yes, under the Container Recycling Facilities Code complying development may be carried out on the land.

Subdivisions Code Yes, under the Subdivisions Code complying development may be carried out on the land.

Demolition Code Yes, under the Demolition Code complying development may be carried out on the land.

Fire Safety Code Yes, under the Fire Safety Code complying development may be carried out on the land.

ITEM 4 – Repealed

ITEM 4A – Repealed

ITEM 4B – Annual charges under Local Government Act 1993 for coastal protection services that relate to existing coastal protection works Has the owner (or any previous owner) of the land consented in writing to the land being subject to annual charges under section 496B of the Local Government Act 1993 for coastal protection services that relate to existing coastal protection works (within the meaning of section 553B of that Act)? No

ITEM 5 –

Mine subsidence

Is the land proclaimed to be in a mine subsidence district within the meaning of section 15 of the Mine Subsidence Compensation Act 1961? No

ITEM 6 –

Road widening and road realignment

Is the land affected by any road widening or road realignment under: (a) Division 2 of Part 3 of the Roads Act 1993; or (b) Any environmental planning instrument; or

Page 6 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

(c) Any resolution of the Council? No

ITEM 7 – Council and other public authority policies on hazard risk restrictions (a)

Whether or not the land is affected by a policy adopted by the Council that restricts the development of the land because of the likelihood of:(i)

land slip

No

(ii)

bushfire

No

(iii)

tidal inundation

No

(iv)

subsidence

No

(v)

acid sulphate soils

Yes

The land is identified as being within Class 2 on the Acid Sulfate Soil Map under the Canada Bay LEP 2013. Works prohibited without Council approval (except as provided by subclause 4 of clause 6.1 of the Canada Bay LEP 2013) include:

(vi)



Works below the natural ground surface



Works by which the watertable is likely to be lowered.

land contamination

Yes

Council has adopted by resolution a policy on contaminated land that applies to all land within the City of Canada Bay. Please note that this statement refers to whether or not Council has a policy regarding contamination and is not a statement on whether the property is affected by contamination or potential contamination. (b)

Whether or not the land is affected by a policy adopted by any other public authority and notified to the Council for the express purpose of its adoption by that authority being referred to in planning certificates issued by the Council that restricts the development of the land because of the likelihood of:(i)

land slip

No

(ii)

bushfire

No

(iii)

tidal inundation

No

(iv)

subsidence

No

(v)

acid sulphate soils

No

(vi)

land contamination

No

ITEM 7A – Flood related development controls 1.

If the land or part of the land is within the flood planning area and subject to flood related development controls.

Page 7 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

No

2.

If the land or part of the land is between the flood planning area and the probable maximum flood and subject to flood related development controls. Yes, please refer to Council’s Planning Controls webpage for more information on Flood Planning.

ITEM 8 –

Land reserved for acquisition

Is there an environmental planning instrument, or proposed environmental planning instrument referred to in clause 1 which makes provision in relation to the acquisition of the land by a public authority, as referred to in section 3.15 of the Environmental Planning and Assessment Act 1979? No

ITEM 9 –

Contributions plans

The name of each contributions plan applying to the land is:City of Canada Bay Local Infrastructure Contributions Plan City of Canada Bay Affordable Housing Contributions Scheme

ITEM 9A - Biodiversity certified land Is the land biodiversity certified land under Part 8 of the Biodiversity Conservation Act 2016 (including land certified under Part 7AA of the Threatened Species Conservation Act 1995)? No

ITEM 10 – Biodiversity stewardship sites Has Council been notified by the Chief Executive of the Office of Environment and Heritage that the land is a biodiversity stewardship site under a biodiversity stewardship agreement under Part 5 of the Biodiversity Conservation Act 2016 (including biobanking agreements under Part 7A of the Threatened Species Conservation Act 1995)? No

ITEM 10A – Native vegetation clearing set asides

Page 8 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

Under section 60ZC of the Local Land Service Act 2013, has Council been notified by Local Land Services (or is it registered in the public register under that section) that the land contains a set aside area? No

ITEM 11 – Bush fire prone land (a) (b) (c)

All of the land is bush fire prone land. Some of the land is bush fire prone land. None of the land is bush fire prone land.

No No Yes

ITEM 12 – Property vegetation plans Has Council been notified (by the person or body that approved the plan) of the existence of a property vegetation plan approved under Part 4 of the Native Vegetation Act 2003 (and that continues in force) applying to the land? No

ITEM 13 – Orders under Trees (Disputes Between Neighbours) Act 2006 Has Council been notified that an order has been made under the Trees (Disputes Between Neighbours) Act 2006 to carry out work in relation to a tree on the land? No

ITEM 14 – Directions under Part 3A Is there a direction by the Minister in force under section 75P (2) (c1) of the Environmental Planning and Assessment Act 1979 that a provision of an environmental planning instrument prohibiting or restricting the carrying out of a project or a stage of a project on the land under Part 4 of the Act does not have effect? No

ITEM 15 – Site compatibility certificates and conditions for seniors housing (a)

Has a current site compatibility certificate (seniors housing), of which the Council is aware, been issued under State Environmental Planning Policy (Housing for Seniors or People with a Disability) 2004 in respect of proposed development on the land? No

(b)

Have any terms of a kind referred to in clause 18(2) of State Environmental Planning Policy (Housing for Seniors or People with a Disability) 2004 been imposed as a condition of consent to a development application granted after 11 October 2007 in respect of the land? No

Page 9 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

ITEM 16 – Site compatibility certificates for infrastructure, schools or TAFE establishments Has a valid site compatibility certificate (infrastructure) or a site compatibility certificate (schools or TAFE establishments),of which the Council is aware, been issued? No

ITEM 17 – Site compatibility certificates and conditions for affordable rental housing 1.

Has a current site compatibility certificate (affordable rental housing), of which the Council is aware, been issued in respect of proposed development on the land? No

2.

Have any terms of a kind referred to in clause 17(1) or 38(1) of State Environmental Planning Policy (Affordable Rental Housing) 2009 been imposed as a condition of consent to a development application in respect of the land? No

ITEM 18 – Paper subdivision information Has a development plan been adopted that applies to the land or that is proposed to be subject to a consent ballot? No

ITEM 19 – Site verification certificates Has Council been made aware of a current site verification certificate that has been issued in respect of the land? No

ITEM 20 – Loose – fill asbestos insulation Has Council been notified that the land includes any residential premises (within the meaning of Division 1A of Part 8 of the Home Building Act 1989) that are listed on the register that is required to be maintained under that Division? No. Contact NSW Fair Trading for more information.

ITEM 21 – Affected building notices and building product rectification orders 1.

Is any affected building notice in force in respect of the land? No

Page 10 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

2.

Certificate Date: 29/03/2022

Is any building product rectification order in force in respect of the land that has not been fully complied with? No

3.

Has a notice of intention to make a building product rectification order been given in respect of that land that is outstanding? No

ITEM 22 – Matters arising under the Contaminated Land Management Act 1997 Section 59(2) of the Contaminated Land Management Act 1997 prescribes the following additional matters to be specified in planning certificates:(a)

At the date of this certificate, is the land (or part of the land) to which this certificate relates significantly contaminated land? No

(b)

At the date of this certificate, is the land to which this certificate relates subject to a management order? No

(c)

At the date of this certificate, is the land to which this certificate relates the subject of an approved voluntary management proposal? No

(d)

At the date of this certificate, is the land to which this certificate relates subject to an ongoing maintenance order? No

(e)

At the date of this certificate, is the land to which this certificate relates the subject of a site audit statement and a copy of such a statement has been provided to the Council? No

SECTION 10.7(5) ADVICE In accordance with section 10.7(5) of the Act the following advice is given on other relevant matters affecting the land. 1.

Demolition Under the local environmental plan applying to the land, development consent is required for the demolition of any building on the land except where the demolition complies with the exempt development requirements specified in State Environmental Planning Policy (Exempt and Complying Development Codes) 2008 and the Canada Bay Local Environmental Plan, 2013.

Page 11 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

2.

Certificate Date: 29/03/2022

Foreshore Building Line Is the land affected by a foreshore building line? No

3.

Other Heritage considerations Is the land adjoining or opposite a heritage item under the provisions of the Local Environmental Plan applying to the land? Yes

Has the property been identified as one that is contributory to the heritage values of a conservation area? No Is the land adjoining or opposite a heritage conservation area under the provisions of the Local Environmental Plan applying to the land? No Does the land contain an item of environmental heritage identified within the Sydney Regional Environmental Plan (Sydney Harbour Catchment) 2005? No 4.

Aircraft Noise Is the land affected by aircraft noise? The property could be affected by aircraft noise. For further details contact Airservices Australia (www.airservices.gov.au), or refer to Council’s Public Mapping Service (www.canadabay.nsw.gov.au/eservices/publicmappingservice).

5.

Other Advice The Council commissioned a flood study which applies to this land. Please refer to the Draft Exile Bay Flood Study for more information.

GENERAL INFORMATION The absence of any reference to a matter affecting the land shall not imply that the land is not affected by that matter not referred to in this certificate. Information provided under section 10.7(2) is in accordance with the matters prescribed under schedule 4 of the Environmental Planning and Assessment Regulation 2000 and is provided only to the extent that the Council has been notified by the Department of Public Works or Department of Planning.

Page 12 of 13


Certificate No.: PC2022/0754

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

When advice in accordance with section 10.7(5) is requested the Council is under no obligation to furnish any advice. If advice is provided Council draws your attention to section 10.7(6) and schedule 6 of the Environmental Planning and Assessment Act 1979 which have the effect that Council shall not incur any liability in respect of advice provided in good faith pursuant to section 10.7(5), including the furnishing of advice in respect of contaminated land. Any enquiries regarding State and Regional Environmental Planning Policies should be directed to the Department of Planning at http:// www.planning.nsw.gov.au Please contact Council’s Strategic Planning section for further information about this Planning Certificate.

John Clark General Manager

Page 13 of 13


APPLICANT:

Geotechnique Pty Ltd P O Box 880 PENRITH NSW 2750

PLANNING CERTIFICATE - under section 10.7 Environmental Planning and Assessment Act 1979

Property:

160 Burwood Road CONCORD NSW 2137

Title:

Lot 5 DP 129325

Certificate No:

PC2022/0755

Certificate Date:

29/03/2022

Receipt No:

Online Receipt

Certificate Fee:

$133.00

Land No:

23425

Applicant’s Ref:

20136/1

Canada Bay Civic Centre Drummoyne 1a Marlborough Street Drummoyne NSW 2047 Locked Bag 1470 Drummoyne NSW 1470 ABN 79 130 029 350

Tel 9911 6555 council@canadabay.nsw.gov.au www.canadabay.nsw.gov.au


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

SECTION 10.7(2) In accordance with the requirements of section 10.7(2) of the Environmental Planning and Assessment Act (1979) (“the Act”), the following prescribed matters relate to the land at the date of this certificate. ITEM 1 1.

Names of relevant planning instruments and DCPs

The following environmental planning instruments apply to the carrying out of development on the land: Canada Bay Local Environmental Plan 2013 State Environmental Planning Policy (Biodiversity and Conservation) 2021 State Environmental Planning Policy (Building Sustainability Index: BASIX) 2004 State Environmental Planning Policy (Exempt and Complying Development Codes) 2008 State Environmental Planning Policy (Housing) 2021 State Environmental Planning Policy (Industry and Employment) 2021 State Environmental Planning Policy No. 65 – Design Quality of Residential Flat Development State Environmental Planning Policy (Planning Systems) 2021 State Environmental Planning Policy (Precincts – Central River City) 2021 State Environmental Planning Policy (Primary Production) 2021 State Environmental Planning Policy (Resilience and Hazards) 2021 State Environmental Planning Policy (Resources and Energy) 2021 State Environmental Planning Policy (Transport and Infrastructure) 2021

2.

The following proposed environmental planning instruments apply to the carrying out of development on the land and are or have been the subject of community consultation or on public exhibition under the Environmental Planning and Assessment Act 1979: Planning Proposal - LEP Miscellaneous Amendments (PP2020/0002) State Environmental Planning Policy (Environment) Design and Place State Environmental Planning Policy

3.

The following development control plans apply to the carrying out of development on the land: City of Canada Bay Development Control Plan Sydney Harbour Foreshores & Waterways Area Development Control Plan

ITEM 2 1.

Zoning and land use under relevant LEPs

(a) Zoning details in the instruments identified in item 1(1) above Zone IN1 General Industrial

Page 2 of 12


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

1

Certificate Date: 29/03/2022

Objectives of zone 

To provide a wide range of industrial and warehouse land uses.

 To encourage employment opportunities.

2



To minimise any adverse effect of industry on other land uses.



To support and protect industrial land for industrial uses.

Permitted without consent Environmental protection works

3

Permitted with consent Depots; Freight transport facilities; Garden Centres; General industries; Hardware and Building Supplies; Industrial training facilities; Light industries; Neighbourhood shops; Roads; Places of Public Worship; Warehouse or distribution centres; Any other development not specified in item 2 or 4

4

Prohibited Agriculture; Air transport facilities; Airstrips; Amusement centres; Boat launching ramps; Boat sheds; Camping grounds; Caravan parks; Cemeteries; Charter and tourism boating facilities; Child care centres; Commercial premises; Community facilities; Correctional centres; Crematoria; Eco-tourist facilities; Educational establishments; Entertainment facilities; Exhibition homes; Exhibition villages; Extractive industries; Farm buildings; Forestry; Function centres; Health services facilities; Heavy industrial storage establishments; Heavy industries; Helipads; Highway service centres; Home-based child care; Home businesses; Home occupations; Home occupations (sex services); Information and education facilities; Jetties; Marinas; Mooring pens; Moorings; Open cut mining; Public administration buildings; Recreation facilities (major); Registered clubs; Research stations; Residential accommodation; Respite day care centres; Restricted premises; Rural industries; Sex services premises; Tourist and visitor accommodation; Water recreation structures; Water supply systems; Wharf or boating facilities; Wholesale supplies

Additional permitted uses No additional uses apply (b) Are there development standards applying to the land, which fix minimum land dimensions for the erection of a dwelling house on the land? No fixed minimum land dimensions apply to this land (c) Does the land include or comprise critical habitat? The land does not include or comprise critical habitat under an EPI (d) Is the land within a heritage conservation area? The land is not within a heritage conservation area (e) Is there a heritage item situated on the land? There are no heritage items situated on the land

Page 3 of 12


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

2.

Certificate Date: 29/03/2022

(a) Zoning details in the instruments identified in item 1(2) above No draft zoning applies to the land Additional permitted uses No draft additional uses apply (b) Are there development standards applying to the land, which fix minimum land dimensions for the erection of a dwelling house on the land? No fixed minimum land dimensions apply to the land under a draft environmental planning instrument (c) Does the land include or comprise critical habitat? The land does not include or comprise critical habitat under a draft EPI (d) Is the land within a draft heritage conservation area? The land is not within a draft heritage conservation area (e) Is there a draft heritage item situated on the land? There are no draft heritage items situated on the land

ITEM 2A - Zoning and land use under State Environmental Planning Policy (Sydney Region Growth Centres) 2006 Is the land identified within any zone under Part 3 of State Environmental Planning Policy (Sydney Region Growth Centres) 2006, a Precinct Plan, or a Proposed Precinct Plan that is or has been the subject of community consultation or on public exhibition under the Act? No

ITEM 3 –

Complying Development Exclusions

Is the land, land on which complying development may be carried out under clauses 1.17A(1)(c) to (e),(2),(3) and (4), 1.18 (1)(c3) and 1.19 of State Environmental Planning Policy (Exempt and Complying Development Codes) 2008? Housing Code Yes, under the Housing Code complying development may be carried out on the land.

Rural Housing Code Yes, under the Rural Housing Code complying development may be carried out on the land.

Low Rise Housing Diversity Code Yes, under the Low Rise Housing Diversity Code complying development may be carried out on the land.

Page 4 of 12


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

Greenfield Housing Code Yes, under the Greenfield Housing Code complying development may be carried out on the land.

Inland Code Yes, under the Inland Housing Code complying development may be carried out on the land.

Housing Alterations Code Yes, under the Housing Alterations Code complying development may be carried out on the land.

General Development Code Yes, under the General Development Code complying development may be carried out on the land.

Commercial and Industrial Alterations Code Yes, under the General Commercial and Industrial Code complying development may be carried out on the land.

Commercial and Industrial (New Buildings and Additions) Code Yes, under the General Commercial and Industrial (New Buildings and Additions) Code complying development may be carried out on the land.

Container Recycling Facilities Code Yes, under the Container Recycling Facilities Code complying development may be carried out on the land.

Subdivisions Code Yes, under the Subdivisions Code complying development may be carried out on the land.

Demolition Code Yes, under the Demolition Code complying development may be carried out on the land.

Fire Safety Code Yes, under the Fire Safety Code complying development may be carried out on the land.

ITEM 4 – Repealed

ITEM 4A – Repealed

Page 5 of 12


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

ITEM 4B – Annual charges under Local Government Act 1993 for coastal protection services that relate to existing coastal protection works Has the owner (or any previous owner) of the land consented in writing to the land being subject to annual charges under section 496B of the Local Government Act 1993 for coastal protection services that relate to existing coastal protection works (within the meaning of section 553B of that Act)? No

ITEM 5 –

Mine subsidence

Is the land proclaimed to be in a mine subsidence district within the meaning of section 15 of the Mine Subsidence Compensation Act 1961? No

ITEM 6 –

Road widening and road realignment

Is the land affected by any road widening or road realignment under: (a) Division 2 of Part 3 of the Roads Act 1993; or (b) Any environmental planning instrument; or (c) Any resolution of the Council? No

ITEM 7 – Council and other public authority policies on hazard risk restrictions (a)

Whether or not the land is affected by a policy adopted by the Council that restricts the development of the land because of the likelihood of:(i)

land slip

No

(ii)

bushfire

No

(iii)

tidal inundation

No

(iv)

subsidence

No

(v)

acid sulphate soils

Yes

The land is identified as being within Class 5 on the Acid Sulfate Soil Map under the Canada Bay LEP 2013. Works prohibited without Council approval (except as provided by subclause 4 of clause 6.1 of the Canada Bay LEP 2013) include:  Works within 500 metres of adjacent Class 1, 2, 3 or 4 land that is below 5 metres Australian Height Datum by which the watertable is likely to be lowered below 1 metre Australian Height Datum on adjacent Class 1, 2, 3 or 4 land.

Page 6 of 12


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

(vi)

land contamination

Certificate Date: 29/03/2022

Yes

Council has adopted by resolution a policy on contaminated land that applies to all land within the City of Canada Bay. Please note that this statement refers to whether or not Council has a policy regarding contamination and is not a statement on whether the property is affected by contamination or potential contamination. (b)

Whether or not the land is affected by a policy adopted by any other public authority and notified to the Council for the express purpose of its adoption by that authority being referred to in planning certificates issued by the Council that restricts the development of the land because of the likelihood of:(i)

land slip

No

(ii)

bushfire

No

(iii)

tidal inundation

No

(iv)

subsidence

No

(v)

acid sulphate soils

No

(vi)

land contamination

No

ITEM 7A – Flood related development controls 1.

If the land or part of the land is within the flood planning area and subject to flood related development controls.

No

2.

If the land or part of the land is between the flood planning area and the probable maximum flood and subject to flood related development controls. Yes, please refer to Council’s Planning Controls webpage for more information on Flood Planning.

ITEM 8 –

Land reserved for acquisition

Is there an environmental planning instrument, or proposed environmental planning instrument referred to in clause 1 which makes provision in relation to the acquisition of the land by a public authority, as referred to in section 3.15 of the Environmental Planning and Assessment Act 1979? No

ITEM 9 –

Contributions plans

Page 7 of 12


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

The name of each contributions plan applying to the land is:City of Canada Bay Local Infrastructure Contributions Plan City of Canada Bay Affordable Housing Contributions Scheme

ITEM 9A - Biodiversity certified land Is the land biodiversity certified land under Part 8 of the Biodiversity Conservation Act 2016 (including land certified under Part 7AA of the Threatened Species Conservation Act 1995)? No

ITEM 10 – Biodiversity stewardship sites Has Council been notified by the Chief Executive of the Office of Environment and Heritage that the land is a biodiversity stewardship site under a biodiversity stewardship agreement under Part 5 of the Biodiversity Conservation Act 2016 (including biobanking agreements under Part 7A of the Threatened Species Conservation Act 1995)? No

ITEM 10A – Native vegetation clearing set asides Under section 60ZC of the Local Land Service Act 2013, has Council been notified by Local Land Services (or is it registered in the public register under that section) that the land contains a set aside area? No

ITEM 11 – Bush fire prone land (a) (b) (c)

All of the land is bush fire prone land. Some of the land is bush fire prone land. None of the land is bush fire prone land.

No No Yes

ITEM 12 – Property vegetation plans Has Council been notified (by the person or body that approved the plan) of the existence of a property vegetation plan approved under Part 4 of the Native Vegetation Act 2003 (and that continues in force) applying to the land? No

ITEM 13 – Orders under Trees (Disputes Between Neighbours) Act 2006 Has Council been notified that an order has been made under the Trees (Disputes Between Neighbours) Act 2006 to carry out work in relation to a tree on the land?

Page 8 of 12


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

No

ITEM 14 – Directions under Part 3A Is there a direction by the Minister in force under section 75P (2) (c1) of the Environmental Planning and Assessment Act 1979 that a provision of an environmental planning instrument prohibiting or restricting the carrying out of a project or a stage of a project on the land under Part 4 of the Act does not have effect? No

ITEM 15 – Site compatibility certificates and conditions for seniors housing (a)

Has a current site compatibility certificate (seniors housing), of which the Council is aware, been issued under State Environmental Planning Policy (Housing for Seniors or People with a Disability) 2004 in respect of proposed development on the land? No

(b)

Have any terms of a kind referred to in clause 18(2) of State Environmental Planning Policy (Housing for Seniors or People with a Disability) 2004 been imposed as a condition of consent to a development application granted after 11 October 2007 in respect of the land? No

ITEM 16 – Site compatibility certificates for infrastructure, schools or TAFE establishments Has a valid site compatibility certificate (infrastructure) or a site compatibility certificate (schools or TAFE establishments),of which the Council is aware, been issued? No

ITEM 17 – Site compatibility certificates and conditions for affordable rental housing 1.

Has a current site compatibility certificate (affordable rental housing), of which the Council is aware, been issued in respect of proposed development on the land? No

2.

Have any terms of a kind referred to in clause 17(1) or 38(1) of State Environmental Planning Policy (Affordable Rental Housing) 2009 been imposed as a condition of consent to a development application in respect of the land? No

ITEM 18 – Paper subdivision information

Page 9 of 12


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

Has a development plan been adopted that applies to the land or that is proposed to be subject to a consent ballot? No

ITEM 19 – Site verification certificates Has Council been made aware of a current site verification certificate that has been issued in respect of the land? No

ITEM 20 – Loose – fill asbestos insulation Has Council been notified that the land includes any residential premises (within the meaning of Division 1A of Part 8 of the Home Building Act 1989) that are listed on the register that is required to be maintained under that Division? No. Contact NSW Fair Trading for more information.

ITEM 21 – Affected building notices and building product rectification orders 1.

Is any affected building notice in force in respect of the land? No

2.

Is any building product rectification order in force in respect of the land that has not been fully complied with? No

3.

Has a notice of intention to make a building product rectification order been given in respect of that land that is outstanding? No

ITEM 22 – Matters arising under the Contaminated Land Management Act 1997 Section 59(2) of the Contaminated Land Management Act 1997 prescribes the following additional matters to be specified in planning certificates:(a)

At the date of this certificate, is the land (or part of the land) to which this certificate relates significantly contaminated land? No

(b)

At the date of this certificate, is the land to which this certificate relates subject to a management order? No

Page 10 of 12


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

(c)

Certificate Date: 29/03/2022

At the date of this certificate, is the land to which this certificate relates the subject of an approved voluntary management proposal? No

(d)

At the date of this certificate, is the land to which this certificate relates subject to an ongoing maintenance order? No

(e)

At the date of this certificate, is the land to which this certificate relates the subject of a site audit statement and a copy of such a statement has been provided to the Council? No

SECTION 10.7(5) ADVICE In accordance with section 10.7(5) of the Act the following advice is given on other relevant matters affecting the land. 1.

Demolition Under the local environmental plan applying to the land, development consent is required for the demolition of any building on the land except where the demolition complies with the exempt development requirements specified in State Environmental Planning Policy (Exempt and Complying Development Codes) 2008 and the Canada Bay Local Environmental Plan, 2013.

2.

Foreshore Building Line Is the land affected by a foreshore building line? No

3.

Other Heritage considerations Is the land adjoining or opposite a heritage item under the provisions of the Local Environmental Plan applying to the land? Yes

Has the property been identified as one that is contributory to the heritage values of a conservation area? No Is the land adjoining or opposite a heritage conservation area under the provisions of the Local Environmental Plan applying to the land? No

Page 11 of 12


Certificate No.: PC2022/0755

Planning Certificate Property: 160 Burwood Road CONCORD NSW 2137

Certificate Date: 29/03/2022

Does the land contain an item of environmental heritage identified within the Sydney Regional Environmental Plan (Sydney Harbour Catchment) 2005? No 4.

Aircraft Noise Is the land affected by aircraft noise? The property could be affected by aircraft noise. For further details contact Airservices Australia (www.airservices.gov.au), or refer to Council’s Public Mapping Service (www.canadabay.nsw.gov.au/eservices/publicmappingservice).

5.

Other Advice The structural adequacy and maintenance of awnings attached to the property and which encroach over Council controlled land are the responsibility of the owner of the land pursuant to Section 142 of the Roads Act 1993 and Council’s Safety of Shop Awnings Policy. The Council commissioned a flood study which applies to this land. Please refer to the Draft Exile Bay Flood Study for more information.

GENERAL INFORMATION The absence of any reference to a matter affecting the land shall not imply that the land is not affected by that matter not referred to in this certificate. Information provided under section 10.7(2) is in accordance with the matters prescribed under schedule 4 of the Environmental Planning and Assessment Regulation 2000 and is provided only to the extent that the Council has been notified by the Department of Public Works or Department of Planning. When advice in accordance with section 10.7(5) is requested the Council is under no obligation to furnish any advice. If advice is provided Council draws your attention to section 10.7(6) and schedule 6 of the Environmental Planning and Assessment Act 1979 which have the effect that Council shall not incur any liability in respect of advice provided in good faith pursuant to section 10.7(5), including the furnishing of advice in respect of contaminated land. Any enquiries regarding State and Regional Environmental Planning Policies should be directed to the Department of Planning at http:// www.planning.nsw.gov.au Please contact Council’s Strategic Planning section for further information about this Planning Certificate.

John Clark General Manager

Page 12 of 12


APPENDIX D

NSW EPA Record of Notices & Environment Protection Licences


Home Public registers Contaminated land record of notices

For business and industry 

Contaminated land - record of notices Record under section 58 of the Contaminated Land Management Act 1997 This record is maintained by OEH in accordance with Part 5 of the Contaminated Land Management Act 1997 (CLM Act). The record does provide The record does not provide a record of written notices issued a record of all contaminated land by OEH under the CLM Act, in NSW. See frequently asked including preliminary questions investigation orders. a list of notifications of contamination that OEH the names of the sites, owners or occupiers at the time of OEH receives. the names of the sites, owners action in relation to the site or occupiers if it changes after copies of site audit statements (SAS) provided to OEH under OEH action in relation to the site. section 52 of the CLM Act and relating to significantly some personal information. contaminated land.

For local government  Contact us

... more about the CLM record of notices From 1 July 2009 there were changes to the terminology of certain OEH actions under the CLM Act. See the list of these changes. The record includes notices issued under sections 35 and 36 of the Environmentally Hazardous Chemicals Act 1985. These sections have been repealed. These notices are treated by the CLM Act as management orders. Before using the record of notices see the Disclaimer and terms of use.

As at Monday, 28 March 2022 there are 1920 notices in the record relating to 411 sites. Show me the entire record or Search the record

28 March 2022

131 555 (tel:131555) Online (https://yoursay.epa.nsw.gov.au/epa-website-feedback) info@epa.nsw.gov.au (mailto:info@epa.nsw.gov.au) EPA Office Locations (https://www.epa.nsw.gov.au/about-us/contact-us/locations) Accessibility (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/help-index) Disclaimer (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/disclaimer) Privacy (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/privacy) Copyright (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/copyright)

Find us on

 (https://au.l environmen protection authority (https://twitter.c epa-) (https://w


Home Public registers Contaminated land record of notices

Search results Your search for:LGA: CITY OF CANADA BAY COUNCIL

Suburb

Address

ABBOTSFORD 83 Wymston PARADE

Site Name Former Gasworks

Matched 130 notices relating to 14 sites. Search Again Refine Search Notices related to this site 1 current and 1 former 1 former

ABBOTSFORD 82, 83, 84 Wymston Pde, & Former Gasworks 37, 39, 43, 45 St Albans STREET ABBOTSFORD 43 St Albans STREET Former Gasworks CABARITA Cabarita ROAD Dulux (Orica Australia) CABARITA 47 and 48 Phillips STREET Wellcome Soil Containment Cells Cabarita CONCORD Nullawarra AVENUE Concord RSL Club CONCORD Nullawarra AVENUE Majors Bay Reserve MORTLAKE MORTLAKE

Tennyson ROAD Kendall BAY

RHODES RHODES

Walker STREET Walker STREET

RHODES

Oulton AVENUE

RHODES

Homebush BAY

RHODES

Mary STREET

1 former 1 former 1 current and 12 former 2 current 1 current and 1 former Former AGL site 22 former Kendall Bay Sediments 5 current and 5 former Former Allied Feeds site 7 former Former UCAL site 1 current and 54 former Homebush Bay sediments adjoining 1 current and former Berger Paint factory 11 former Homebush Bay Sediments adjoining 1 current and the former UCAL and Allied Feeds 4 former sites Rhodes Waterside 2 former

Page 1 of 1 28 March 2022

and industry 

For business

For local government  Contact us 131 555 (tel:131555) Online (https://yoursay.epa.nsw.gov.au/epa-website-feedback) info@epa.nsw.gov.au (mailto:info@epa.nsw.gov.au) EPA Office Locations (https://www.epa.nsw.gov.au/about-us/contact-us/locations) Accessibility (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/help-index) Disclaimer (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/disclaimer) Privacy (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/privacy) Copyright (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/copyright)

Find us on

 (https://au.l environmen protection authority (https://twitter.c epa-) (https://w


Home Public registers Contaminated land record of notices

Search results Your search for:Suburb: CONCORD

Suburb

Address

CONCORD Nullawarra AVENUE CONCORD Nullawarra AVENUE

Site Name Concord RSL Club Majors Bay Reserve

Matched 4 notices relating to 2 sites. Search Again Refine Search Notices related to this site 2 current 1 current and 1 former

Page 1 of 1 28 March 2022

For business and industry  For local government  Contact us 131 555 (tel:131555) Online (https://yoursay.epa.nsw.gov.au/epa-website-feedback) info@epa.nsw.gov.au (mailto:info@epa.nsw.gov.au) EPA Office Locations (https://www.epa.nsw.gov.au/about-us/contact-us/locations) Accessibility (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/help-index) Disclaimer (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/disclaimer) Privacy (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/privacy) Copyright (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/copyright)

Find us on

 (https://au.l environmen protection authority (https://twitter.c epa-) (https://w


Home Public registers Contaminated land record of notices

Search results Your search for:FULL REGISTER

CAPTAINS FLAT1 Copper Creek Road ROAD

Matched 1920 notices relating to 411 sites. Search Again Refine Search Site Name Notices related to this site Rail corridor adjacent to Lake 2 current George Mine

1 Copper Creek ROAD, CAPTAINS FLAT CARINGBAH 101-103 Cawarra ROAD CARINGBAH 105 Cawarra ROAD CASINO 86 Johnston STREET CHARLESTOWN273 Charlestown ROAD CHARLESTOWN81 Pacific HIGHWAY

Adjacent to Spirent Australia Spirent Australia Casino Roadhouse 7-Eleven Charlestown Caltex Service Station

Suburb

Address

3 4 2 2 3 3 5 6 8

former former current former current and former former former former

134-136 Pacific HIGHWAY BP Service Station

4 2 6 3 1 6

former current and former current and former former

Aviation DRIVE

Mobil Coffs Harbour Airport

1 former

314-316 Harbour DRIVE

Mobil Service Station

9 former

86-88 Great Western HIGHWAY Nullawarra AVENUE Nullawarra AVENUE

Coles Express (former Ampol) Service Station Concord RSL Club Majors Bay Reserve

4 former

CHARLESTOWN91-93 Pacific HIGHWAY CHATSWOOD 728 Pacific HIGHWAY CHATSWOOD 607 Pacific HIGHWAY CHESTER HILL 127 Orchard ROAD CHIPPENDALE Wellington STREET CHIPPING NORTON COFFS HARBOUR COFFS HARBOUR COFFS HARBOUR COLYTON CONCORD CONCORD

85-107 Alfred STREET

CONDOBOLIN 6 Burnett STREET COOMA 48-52 Sharp STREET

Caltex Woolworths (Former BP) Chatswood Toyota Former Caltex Chatswood Service Station Former Orica, Chester Hill Cnr Regent Street & Wellington Street, Chippendale Former ACR

2 current 1 current and 1 former Former Mobil Depot 5 former Former Shell Service Station 4 former 1 2 3 4 5 6 7 8 9 10 ...

Page 5 of 21 28 March 2022

For business and industry  For local government 

Contact us 131 555 (tel:131555) Online (https://yoursay.epa.nsw.gov.au/epa-website-feedback) info@epa.nsw.gov.au (mailto:info@epa.nsw.gov.au) EPA Office Locations (https://www.epa.nsw.gov.au/about-us/contact-us/locations) Accessibility (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/help-index) Disclaimer (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/disclaimer) Privacy (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/privacy) Copyright (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/copyright)

Find us on

 (https://au.l environmen protection authority (https://twitter.c epa-) (https://w


Home Public registers POEO Public Register Licences, applications and notices search

Search results Your search for: General Search with the following criteria Suburb - Concord returned 4 results Export to excel

1 of 1 Pages

Search Again

Number Name

Location

Type

6228

55 BURWOOD ROAD, CONCORD, NSW 2137 55 BURWOOD ROAD, CONCORD, NSW 2137 CNR PARRAMATTA & CONCORD ROADS, CONCORD, NSW 2137 CNR PARRAMATTA & CONCORD ROADS, CONCORD, NSW 2137

POEO licence No longer in 10 Jan 2000 force

OWEN FERGUSON HEALTH PTY. LTD.

1049890 OWEN FERGUSON HEALTH PTY. LTD. 5965

SUMMIT CULLENS PTY LIMITED

1031249 SUMMIT CULLENS PTY LIMITED

Status

s.58 Licence Issued Variation

Issued date

18 Jul 2005

POEO licence Surrendered13 May 2000

s.80 Issued Surrender of a Licence

01 Oct 2003

28 March 2022

For business and industry  For local government  Contact us 131 555 (tel:131555) Online (https://yoursay.epa.nsw.gov.au/epa-website-feedback) info@epa.nsw.gov.au (mailto:info@epa.nsw.gov.au) EPA Office Locations (https://www.epa.nsw.gov.au/about-us/contact-us/locations) Accessibility (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/help-index) Disclaimer (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/disclaimer) Privacy (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/privacy) Copyright (https://www.epa.nsw.gov.au/about-us/contact-us/website-service-standards/copyright)

Find us on

 (https://au.l environmen protection authority (https://twitter.c epa-) (https://w


Background A strategy to systematically prioritise, assess and respond to notifications under Section 60 of the Contaminated Land Management Act 1997 (CLM Act) has been developed by the EPA. This strategy acknowledges the EPA’s obligations to make information available to the public under Government Information (Public Access) Act 2009 . When a site is notified to the EPA, it may be accompanied by detailed site reports where the owner has been proactive in addressing the contamination and its source. However, often there is minimal information on the nature or extent of the contamination. After receiving a report, the first step is to confirm that the report does not relate to a pollution incident. The Protection of the Environment Operations Act 1997 (POEO Act) deals with pollution incidents, waste stockpiling or dumping. The EPA also has an incident management process to manage significant incidents (https://www.epa.nsw.gov.au/reporting-and-incidents/incidentmanagement). In many cases, the information indicates the contamination is securely immobilised within the site, such as under a building or carpark, and is not currently causing any significant risks for the community or environment. Such sites may still need to be cleaned up, but this can be done in conjunction with any subsequent building or redevelopment of the land. These sites do not require intervention under the CLM Act, and are dealt with through the planning and development consent process. In these cases, the EPA informs the local council or other planning authority, so that the information can be recorded and considered at the appropriate time (https://www.epa.nsw.gov.au/your-environment/contaminated-land/managing-contaminated-land/role-of-planning-authorities). Where indications are that the contamination could cause actual harm to the environment or an unacceptable offsite impact (i.e. the land is 'significantly contaminated'), the EPA would apply the regulatory provisions of the CLM Act to have the responsible polluter and/or landowner investigate and remediate the site. If the reported contamination could present an immediate or long-term threat to human health NSW Health will be consulted. SafeWork NSW and Water NSW can also be consulted if there appear to be occupational health and safety risks or an impact on groundwater quality. As such, the sites notified to the EPA and presented in the list of contaminated sites notified to the EPA are at various stages of the assessment and remediation process. Understanding the nature of the underlying contamination, its implications and implementing a remediation program where required, can take a considerable period of time. The list provides an indication, in relation to each nominated site, as to the management status of that particular site. Further detailed information may be available from the EPA or the person who notified the site. The following questions and answers may assist those interested in this issue.

Frequently asked questions Why does my land appear on the list of notified sites? Your land may appear on the list because: • the site owner and/or the polluter has notified the EPA under section 60 of the CLM Act • the EPA has been notified via other means and is satisfied that the site is or was contaminated. If a site is on the list, it does not necessarily mean the contamination is significant enough to regulate under the CLM Act.

List current as at 8 March 2022

1 of 129


Does the list contain all contaminated sites in NSW? No. The list only contains contaminated sites that EPA is aware of. If a site is not on the list, it does not necessarily mean the site is not contaminated. The EPA relies on responsible parties and the public to notify contaminated sites.

How are notified contaminated sites managed by the EPA? There are different ways the EPA can manage notified contaminated sites. Options include: • regulation under the CLM Act, POEO Act, or both • notifying the relevant planning authority for management under the planning and development process • managing the site under the Protection of the Environment Operation (Underground Petroleum Storage Systems) Regulation 2014. There are specific cases where contamination is managed under a tailored program operated by another agency (for example, the Resources & Geoscience's Legacy Mines Program).

What should I do if I am a potential buyer of a site that appears on the list? You should seek advice from the seller to understand the contamination issue. You may need to seek independent contamination or legal advice. The information provided in the list is indicative only and a starting point for your own assessment. Land contamination from past site uses is common, mainly in urban environments. If the site is properly remediated or managed, it may not affect the intended future use of the site.

Who can I contact if I need more information about a site? You can contact the Environment Line at any time by calling 131 555 or by emailing info@environment.nsw.gov.au.

List of NSW Contaminated Sites Notified to the EPA

List current as at 8 March 2022

2 of 129


Disclaimer The EPA has taken all reasonable care to ensure that the information in the list of contaminated sites notified to the EPA (the list) is complete and correct. The EPA does not, however, warrant or represent that the list is free from errors or omissions or that it is exhaustive. The EPA may, without notice, change any or all of the information in the list at any time. You should obtain independent advice before you make any decision based on the information in the list. The list is made available on the understanding that the EPA, its servants and agents, to the extent permitted by law, accept no responsibility for any damage, cost, loss or expense incurred by you as a result of: 1. any information in the list; or 2. any error, omission or misrepresentation in the list; or 3. any malfunction or failure to function of the list; 4. without limiting (2) or (3) above, any delay, failure or error in recording, displaying or updating information.

Site Status

Explanation

Under assessment

The contamination is being assessed by the EPA to determine whether regulation is required. The EPA may require further information to complete the assessment. For example, the completion of management actions regulated under the planning process or Protection of the Environment Operations Act 1997 .

Under Preliminary Investigation Order

The EPA has issued a Preliminary Investigation Order under s10 of the Contaminated Land Management Act 1997 , to obtain additional information needed to complete the assessment.

Regulation under CLM Act not required

The EPA has completed an assessment of the contamination and decided that regulation under the Contaminated Land Management Act 1997 is not required.

List current as at 8 March 2022

3 of 129


Regulation being finalised

The EPA has completed an assessment of the contamination and decided that the contamination is significant enough to warrant regulation under the Contaminated Land Management Act 1997 . A regulatory approach is being finalised.

Contamination currently regulated under CLM Act

The EPA has completed an assessment of the contamination and decided that the contamination is significant enough to warrant regulation under the Contaminated Land Management Act 1997 (CLM Act). Management of the contamination is regulated by the EPA under the CLM Act. Regulatory notices are available on the EPA’s Contaminated Land Public Record.

Contamination currently regulated under POEO Act

Contamination is currently regulated under the Protection of the Environment Operations Act 1997 (POEO Act). The EPA as the appropriate regulatory authority reasonably suspects that a pollution incident is occurring/ has occurred and that it requires regulation under the POEO Act. The EPA may use environment protection notices, such as clean up notices, to require clean up action to be taken. Such regulatory notices are available on the POEO public register.

Contamination being managed via the planning process (EP&A Act)

The EPA has completed an assessment of the contamination and decided that the contamination is significant enough to warrant regulation. The contamination of this site is managed by the consent authority under the Environmental Planning and Assessment Act 1979 (EP&A Act) planning approval process, with EPA involvement as necessary to ensure significant contamination is adequately addressed. The consent authority is typically a local council or the Department of Planning and Environment.

Contamination formerly regulated under the CLM Act

The EPA has determined that the contamination is no longer significant enough to warrant regulation under the Contaminated Land Management Act 1997 (CLM Act). The contamination was addressed under the CLM Act.

Contamination formerly regulated under the POEO Act

The EPA has determined that the contamination is no longer significant enough to warrant regulation. The contamination was addressed under the Protection of the Environment Operations Act 1997 (POEO Act).

List current as at 8 March 2022

4 of 129


Contamination was addressed via the planning process (EP&A Act)

The EPA has determined that the contamination is no longer significant enough to warrant regulation. The contamination was addressed by the appropriate consent authority via the planning process under the Environmental Planning and Assessment Act 1979 (EP&A Act).

Ongoing maintenance required to manage residual contamination (CLM Act)

The EPA has determined that ongoing maintenance, under the Contaminated Land Management Act 1997 (CLM Act), is required to manage the residual contamination. Regulatory notices under the CLM Act are available on the EPA’s Contaminated Land Public Record.

List current as at 8 March 2022

5 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

ABBOTSFORD

Former Gasworks

83 Wymston PARADE

Gasworks

Contamination formerly regulated under the CLM Act

-33.85288351

151.1265979

ABBOTSFORD

Former Gasworks

82, 83, 84 Wymston Pde, & 37, 39, 43, 45 St Albans STREET Gasworks

Contamination formerly regulated under the CLM Act

-33.85288316

151.1267729

ABBOTSFORD

Former Gasworks

85 Wymston PARADE

Gasworks

Regulation under CLM Act not required

-33.85265214

151.1266277

ABBOTSFORD

Former Gasworks

80-81 Wymston Pde and 35 and 41 St Albans STREET

Gasworks

Regulation under CLM Act not required

-33.85306653

151.1268142

ABBOTSFORD

Former Gasworks

43 St Albans STREET

Gasworks

Contamination formerly regulated under the CLM Act

-33.85270604

151.126976

ABERDEEN

Former Transport Depot

87-89 St Andrew STREET

Other Industry

Regulation under CLM Act not required

-32.17160931

150.8972859

ALBION PARK

Caltex Albion Park Service Station

1 Calderwood ROAD

Service Station

Regulation under CLM Act not required

-34.57131362

150.7647971

ALBION PARK RAIL

Caltex Service Station

174 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.56134097

150.7953663

ALBION PARK RAIL

Caltex Service Station

31 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.55162786

150.7880626

ALBION PARK RAIL

Former Timber Storage Area

36 Rivulet CRESCENT

Other Industry

Regulation under CLM Act not required

-34.54872597

150.7899351

ALBURY

Mobil Depot, Railway Place Albury

1 Railway PLACE

Other Petroleum

Regulation under CLM Act not required

-36.08526805

146.9236999

ALBURY

Woolworths Petrol

515 Young STREET

Service Station

Regulation under CLM Act not required

-36.08073723

146.92351

ALBURY

Former Caltex Service Station

842 David STREET

Service Station

Regulation under CLM Act not required

-36.06398743

146.9252143

ALBURY

SRA Land, 514 to 526 Young Street

514 to 526 Young STREET

Other Petroleum

Regulation under CLM Act not required

-36.08084123

146.9241682

ALBURY

Former Gasworks and surrounding commercial land

441 Kiewa STREET

Gasworks

Contamination currently regulated under CLM Act

-36.08416926

146.9137704

List current as at 8 March 2022

6 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

ALBURY

Coles Express Albury

465 Guinea STREET

Service Station

Regulation under CLM Act not required

ALBURY

Former Thales Australia site, Albury

161 Fallon STREET

Other Industry

ALBURY

Xpress Service Station

616-624 Young STREET

Service Station

ALBURY

Albury Plaza

Cnr Smollett Street and Townsend STREET Other Industry

ALBURY

Mobil Albury Aviation Fuel Depot

Hangar 8 (Albury Airport), Ogden PLACE

ALBURY

SRA Land

ALBURY

Latitude

Longitude

-36.07513665

146.9213077

Contamination formerly regulated under the CLM Act

-36.064966

146.9434831

Contamination formerly regulated under the CLM Act

-36.0755401

146.9255668

Regulation under CLM Act not required

-36.08112933

146.9135719

Other Petroleum

Regulation under CLM Act not required

-36.07178139

146.9530165

448 and 452 Young STREET

Unclassified

Regulation under CLM Act not required

-36.08438605

146.9235454

Caltex Service Station

Dean Street, Corner Creek STREET

Service Station

Regulation under CLM Act not required

-36.07978937

146.9110825

ALEXANDRIA

Former Mobil Service Station

20 O'Riordan STREET

Service Station

Regulation under CLM Act not required

-33.9075539

151.2014811

ALEXANDRIA

Caltex Alexandria Service Station

133 Wyndham St, cnr McEvoy STREET

Service Station

Regulation under CLM Act not required

-33.90220927

151.2000425

ALEXANDRIA

Former Cadbury Schweppes

49-59 O'Riordan STREET

Other Industry

Contamination formerly regulated under the CLM Act

-33.91406619

151.195067

ALEXANDRIA

Formerly Gas N Go Alexandria (fully redeveloped into residential apartment as of September 2016) 10-20 Botany ROAD

Service Station

Regulation under CLM Act not required

-33.89536227

151.1987818

ALEXANDRIA

Mascot Developments

494-504 Gardeners ROAD

Other Industry

Regulation under CLM Act not required

-33.9198218

151.191282

ALEXANDRIA

Alexandria GoGas

562 Botany ROAD

Service Station

Regulation under CLM Act not required

-33.91577222

151.2000753

ALEXANDRIA

Australian Refined Alloys

202-212 Euston ROAD

Metal Industry

Regulation under CLM Act not required

-33.91505136

151.185872

ALEXANDRIA

Alexandra Canal Sediments

Off Huntley STREET

Other Industry

Contamination currently regulated under CLM Act

-33.92204213

151.1770009

List current as at 8 March 2022

7 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

ALEXANDRIA

Australia Post

10-24 Ralph STREET

Other Industry

Contamination was addressed via the planning process (EP&A Act)

-33.91583041

151.197997

ALEXANDRIA

Perry Park

1B Maddox STREET

Landfill

Regulation under CLM Act not required

-33.90809949

151.1962945

ALEXANDRIA

Alexandria Gardens

146-156 Wyndham Street & 146-156 Botany ROAD

Unclassified

Regulation under CLM Act not required

-33.89956961

151.1997377

ALEXANDRIA

Sydney Park

Sydney Park ROAD

Landfill

Contamination currently regulated under CLM Act

-33.91031048

151.1844672

ALEXANDRIA

Former Industrial Site (now Value Suites)

16 O'Riordan STREET

Other Industry

Regulation under CLM Act not required

-33.9069796

151.201902

ALEXANDRIA

205-225 Euston Road, Alexandria

205-225 Euston ROAD

Other Industry

Regulation under CLM Act not required

-33.912233

151.185932

ALEXANDRIA

The Gentry Alexandria

31-41 William STREET

Unclassified

Regulation under CLM Act not required

-33.91258565

151.1981861

ALEXANDRIA

6 - 8 Huntley Street, Alexandria NSW 2004 6 - 8 Huntley STREET

Metal Industry

Under assessment

-33.909918

151.19268

ALEXANDRIA

566 Gardeners Road, Alexandria NSW

566 Gardeners ROAD

Unclassified

Under assessment

-33.919062

151.184108

ALSTONVILLE

Caltex Service Station Alstonville

73 Main STREET

Service Station

Regulation under CLM Act not required

-28.84115994

153.4388699

AMBARVALE

Caltex Service Station

37 Woodhouse DRIVE

Service Station

Regulation under CLM Act not required

-34.08438034

150.8019168

ANNANDALE

7-Eleven (former Mobil) Annandale Service Station

198 Parramatta ROAD

Service Station

Regulation under CLM Act not required

-33.88706434

151.1741135

ANNANDALE

Shell Coles Express Service Station

124-126 Johnston STREET

Service Station

Regulation under CLM Act not required

-33.88085651

151.1704805

APPIN

Elladale Creek Aqueduct Upper Canal

Macquariedale ROAD

Unclassified

Regulation under CLM Act not required

-34.18867067

150.7539597

APPIN

West Cliff Colliery

Wedderburn ROAD

Other Petroleum

Regulation under CLM Act not required

-34.21970612

150.8217522

List current as at 8 March 2022

8 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

ARDLETHAN

Landmark Fertiliser Storage Facility

18 & 24-26 Ariah STREET

Chemical Industry

Regulation under CLM Act not required

-34.35696645

146.9007084

ARGENTON

NSW Mines Rescue Services - Argenton

533 Lake ROAD

Other Industry

Regulation under CLM Act not required

-32.93807208

151.6269664

ARMIDALE

Former Mobil Depot

132 Niagara STREET

Other Petroleum

Contamination formerly regulated under the CLM Act

-30.51115918

151.6490343

ARMIDALE

Caltex Service Station

146 Miller STREET

Service Station

Regulation under CLM Act not required

-30.51362759

151.6481123

ARMIDALE

RTA land adjoining Martin Street estate

Martin STREET

Other Industry

Contamination formerly regulated under the CLM Act

-30.50445941

151.6415415

ARMIDALE

Shell Service Station

93 Marsh STREET

Service Station

Regulation under CLM Act not required

-30.51299824

151.6697557

ARMIDALE

Parklands near the former gasworks

Beardy Street and Allingham STREET

Gasworks

Regulation under CLM Act not required

-30.51013465

151.6652722

ARMIDALE

Gasworks and portion of Harris Park

Corner of Beardy Street and Allingham STREET

Gasworks

Contamination currently regulated under CLM Act

-30.51157374

151.6623009

ARMIDALE

Former Lot 3 Martin Street

89 Martin STREET

Other Industry

Regulation under CLM Act not required

-30.50664682

151.64542

ARMIDALE

Martin Street Estate

Martin STREET

Other Industry

Regulation under CLM Act not required

-30.50559024

151.6431854

ARMIDALE

Caltex Armidale Girraween Service Station 6-8 Queen Elizabeth DRIVE

Service Station

Regulation under CLM Act not required

-30.50348872

151.6510748

ARMIDALE

Martin Street, Crown Land

Martin STREET

Other Industry

Contamination formerly regulated under the CLM Act

-30.50414076

151.6429516

ARMIDALE

Former Shell Depot

134 Niagara STREET

Other Petroleum

Regulation under CLM Act not required

-30.51180178

151.6488634

ARMIDALE

Caltex Service Station

144 Marsh STREET

Service Station

Regulation under CLM Act not required

-30.51709925

151.6675802

ARMIDALE

Caltex North Hill Service Station

2-4 Marsh STREET

Service Station

Regulation under CLM Act not required

-30.50320439

151.6727051

List current as at 8 March 2022

9 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

ARMIDALE

Mobil Armidale Service Station and Former Depot

10-12 McLennan STREET

Service Station

Regulation under CLM Act not required

-30.51107573

151.648242

ARMIDALE

Caltex Service Station

19/10541 New England HIGHWAY

Service Station

Regulation under CLM Act not required

-30.53210764

151.6160492

ARMIDALE

Armidale Dumaresq Council Grafton Road Depot 15-25 Grafton ROAD

Other Petroleum

Regulation under CLM Act not required

-30.52058076

151.6815261

ARNCLIFFE

7-Eleven Arncliffe

28 Princes HIGHWAY

Service Station

Under assessment

-33.93428397

151.1525438

ARNCLIFFE

Combined Projects Arncliffe

104-128 Princes HIGHWAY

Other Industry

Regulation under CLM Act not required

-33.93783874

151.1494559

ARTARMON

7-Eleven (former Mobil) Artarmon Service 477 Pacific HIGHWAY Station

Service Station

Regulation under CLM Act not required

-33.81053826

151.1774248

ASHBY

Ashby Dry Dock

via Clarence STREET

Other Industry

Contamination formerly regulated under the CLM Act

-29.44158377

153.1972304

ASHFIELD

7-Eleven Ashfield

132 Liverpool Road STREET

Service Station

Contamination currently regulated under CLM Act

-33.8902785

151.1297902

ASHFIELD

Vehicle Workshop

445-449 Liverpool ROAD

Service Station

Regulation under CLM Act not required

-33.88826829

151.1167477

ASQUITH

BP Service Station

462 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.68982678

151.106156

ATTUNGA

Attunga Limestone Mine (Waste Oil Site) Garthowen ROAD

Other Industry

Regulation under CLM Act not required

-30.92920627

150.8579435

AUBURN

DIC Australia

323 Chisholm ROAD

Other Industry

Regulation under CLM Act not required

-33.87228962

151.0157032

AUBURN

Former Ajax Chemical Factory

9 Short STREET

Other Industry

Contamination formerly regulated under the CLM Act

-33.83671601

151.0292071

AUBURN

Janyon

Manchester ROAD

Other Industry

Regulation under CLM Act not required

-33.84467826

151.020745

AUBURN

Maintrain Facility - Sydney Trains Auburn Manchester ROAD

Other Industry

Regulation under CLM Act not required

-33.84410947

151.0242502

List current as at 8 March 2022

10 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

AUBURN

Department of Corrective Services land adjacent to the former Auburn Landfill

Jamieson STREET

Landfill

Contamination formerly regulated under the CLM Act

AUBURN

Commercial Premises

11-13 Percy STREET

Other Industry

Under assessment

AWABA

Awaba Colliery

Wilton ROAD

Other Industry

BALGOWLAH

BP Service Station

Cnr Sydney Road and Maretimo STREET

BALGOWLAH

Latitude

Longitude

-33.82928257

151.0590653

-33.849995

151.040652

Regulation under CLM Act not required

-33.02098186

151.5383612

Service Station

Regulation under CLM Act not required

-33.79546175

151.2559309

Part of Manly Council Maintenance Depot 8-10 Roseberry STREET

Other Petroleum

Regulation under CLM Act not required

-33.78928907

151.2679557

BALGOWNIE

Fuel Power Plus

99 Balgownie ROAD

Service Station

Contamination currently regulated under POEO Act

-34.38925632

150.8808544

BALLINA

Former Mobil Service Station

37-41 Cherry STREET

Service Station

Regulation under CLM Act not required

-28.86952673

153.5624436

BALLINA

Ballina Shell

273 River STREET

Service Station

Regulation under CLM Act not required

-28.86809272

153.5552789

BALLINA

Woolworths Petrol

Kerr STREET

Service Station

Regulation under CLM Act not required

-28.85824461

153.5605439

BALLINA

Ballina Mays Motors

River STREET

Other Petroleum

Regulation under CLM Act not required

-28.86935402

153.5585931

BALRANALD

Caltex Service Station

Sturt HIGHWAY

Service Station

Regulation under CLM Act not required

-34.66747746

143.5662034

BANKSIA

Woolworths Petrol Service Station Banksia

314 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-33.94567308

151.1416884

BANKSIA

Cooks Cove Development

Cooks Cove PARK

Landfill

Regulation under CLM Act not required

-33.94492759

151.1549947

BANKSMEADOW

Orica Botany Groundwater Project

16-20 Beauchamp ROAD

Chemical Industry

Contamination currently regulated under CLM Act

-33.95526361

151.2152005

BANKSMEADOW

Discovery Cove, Former Ampol Rail Terminal

1801 Botany ROAD

Other Petroleum

Regulation being finalised

-33.96162178

151.2184122

List current as at 8 March 2022

11 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BANKSMEADOW

Caltex Terminal

1-3 Penrhyn ROAD

Other Petroleum

Contamination currently regulated under POEO Act

-33.96335328

151.2171062

BANKSMEADOW

Orica Botany (Pre-2003 Regulation)

Denison STREET

Chemical Industry

Contamination currently regulated under CLM Act

-33.9516159

151.2195804

BANKSMEADOW

Veolia Waste Transfer Terminal (former Keith Engineering site)

34-36 McPherson STREET

Other Industry

Regulation under CLM Act not required

-33.95811039

151.2195225

BANKSMEADOW

Orica Former Chlor Alkali Plant (same site Botany Industrial Park, off Denison as Orica Botany Groundwater Project) STREET

Chemical Industry

Contamination currently regulated under CLM Act

-33.95664283

151.221685

BANKSMEADOW

Former Pipeline

Corish CIRCLE

Other Petroleum

Regulation being finalised

-33.94705787

151.2209919

BANKSMEADOW

Pacific National Rail Siding

1 Beauchamp ROAD

Chemical Industry

Contamination currently regulated under CLM Act

-33.95757712

151.2204974

BANKSMEADOW

Former Mobil Banksmeadow Terminal

Coal Pier ROAD

Other Petroleum

Regulation under CLM Act not required

-33.95405624

151.2142048

BANKSMEADOW

Orica Car Park Waste Encapsulation

Corish CIRCLE

Landfill

Contamination formerly regulated under the POEO Act

-33.94703665

151.22083

BANKSTOWN

7-Eleven Service Station

689 Henry Lawson DRIVE

Service Station

Regulation under CLM Act not required

-33.92749953

150.9804784

BANORA POINT

Caltex Service Station

Corner Leisure Drive and Darlington DRIVE

Service Station

Regulation under CLM Act not required

-28.21390712

153.5417434

BARGO

Tahmoor Colliery

Remembrance DRIVE

Other Industry

Regulation under CLM Act not required

-34.25090795

150.5793631

BARMEDMAN

Caltex - Barmedman

Corner Watson Street and Star STREET

Other Petroleum

Regulation under CLM Act not required

-34.14351302

147.3824934

BARRACK HEIGHTS

Caltex Service Station

332-336 Shellharbour ROAD

Service Station

Regulation under CLM Act not required

-34.56489171

150.8597814

BASS HILL

Woolworths Caltex Bass Hill

862 Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-33.9008648

150.9991181

BATEAU BAY

Former landfill

The Entrance ROAD

Landfill

Contamination currently regulated under CLM Act

-33.3938305

151.4699046

List current as at 8 March 2022

12 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BATEAU BAY

Woolworths Service Station Bateau Bay

9 Bay Village ROAD

Service Station

Regulation under CLM Act not required

-33.37316432

151.4737125

BATEHAVEN

Caltex Service Station

264 Beach ROAD

Service Station

Regulation under CLM Act not required

-35.73255166

150.1997536

BATEHAVEN

Coles Express Service Station Batehaven

198 Beach ROAD

Service Station

Regulation under CLM Act not required

-35.72671807

150.1944931

BATEMANS BAY

Caltex Service Station

87-89 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-35.71940701

150.1762788

BATHURST

Shell Coles Express Service Station

(Cnr Stewart and Rocket Street) 298 Stewart STREET

Service Station

Regulation under CLM Act not required

-33.41910999

149.5677773

BATHURST

Former Shell Depot Bathurst

56 Bant STREET

Other Petroleum

Regulation under CLM Act not required

-33.43471575

149.5774595

BATHURST

Bathurst Rail Fabrication Centre

34 Alpha STREET

Other Industry

Regulation under CLM Act not required

-33.42805153

149.5829156

BATHURST

Bathurst - Former Caltex Depot

114 Howick STREET

Other Petroleum

Regulation under CLM Act not required

-33.42296963

149.5862574

BATHURST

Caltex Bathurst Service Station

53 Durham STREET

Service Station

Regulation under CLM Act not required

-33.41689545

149.5848527

BATHURST

Former Police Station

Corner of William Street and Durham STREET

Other Petroleum

Contamination formerly regulated under the CLM Act

-33.41592424

149.5842233

BATHURST

Former Mobil Depot

1 Lambert STREET

Other Petroleum

Regulation under CLM Act not required

-33.42875534

149.5806344

BATHURST

Crago Mill site

Piper STREET

Other Industry

Regulation under CLM Act not required

-33.42777602

149.5809428

BATHURST

Former Mobil Depot

Lower Russell STREET

Other Petroleum

Regulation under CLM Act not required

-33.42497876

149.585128

BATHURST

Shell Coles Express Bathurst Service Station

59 Durham STREET

Service Station

Regulation under CLM Act not required

-33.41639415

149.5843243

BATHURST

Former Gasworks

71 Russell STREET

Gasworks

Contamination formerly regulated under the CLM Act

-33.42420302

149.5864517

List current as at 8 March 2022

13 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BATHURST

Former Devro Cattle Hide Processing Plant

46 Vale ROAD

Other Industry

Regulation under CLM Act not required

-33.43926137

149.5803563

BATLOW

Crown Reserves

Mill ROAD

Other Industry

Regulation under CLM Act not required

-35.535161

148.155354

BAULKHAM HILLS

Caltex Baulkham Hills Service Station

117 Seven Hills ROAD

Service Station

Regulation under CLM Act not required

-33.76139872

150.9750767

BAULKHAM HILLS

Caltex Service Station

130 Seven Hills ROAD

Service Station

Regulation under CLM Act not required

-33.76180431

150.9746297

BAULKHAM HILLS

Shell Coles Express Service Station

363 Windsor ROAD

Service Station

Regulation under CLM Act not required

-33.7601819

150.9916224

BAULKHAM HILLS

IBM Baulkham Hills Data Centre

3 Brookhollow AVENUE

Other Petroleum

Regulation under CLM Act not required

-33.732493

150.968029

BEACON HILL

Caltex Service Station

176 Warringah ROAD

Service Station

Contamination currently regulated under CLM Act

-33.75381485

151.2602617

BEACON HILL

Former 7-Eleven Service Station, Beacon Hill

312 Warringah ROAD

Service Station

Regulation under CLM Act not required

-33.75129647

151.2469656

BEACONSFIELD

63-85 Victoria St, Beaconsfield

63-85 Victoria STREET

Other Industry

Regulation under CLM Act not required

-33.9102929

151.2016275

BEGA

Coles Express (former Caltex) Service Station

2-6 Swan (Corner Carp) STREET

Service Station

Regulation under CLM Act not required

-36.67388263

149.838163

BEGA

Former BP Service Station

100 - 102 Gipps STREET

Service Station

Regulation under CLM Act not required

-36.67563094

149.8433291

BEGA

Former Bega Gasworks

19-29 Upper STREET

Gasworks

Under preliminary investigation order

-36.67710613

149.8480253

BEGA

Caltex Service Station

36-40 Lagoon STREET

Service Station

Regulation under CLM Act not required

-36.66832965

149.8289048

BEGA

Lands Adjoining the Former Bega Gasworks

Part of Upper, East, Gordon & Gloucester STREET Gasworks

Under preliminary investigation order

-36.67704706

149.848425

BEGA

Spenco Site - owned by Bega Spotlight Property 2 Pty Ltd

53-65 Bega Street STREET

Regulation under CLM Act not required

-36.67135539

149.8450828

List current as at 8 March 2022

Other Industry

14 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BELMONT

Coles Express Belmont Service Station

502 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.03317155

151.6605194

BELMONT

Former Ampol Service Station

467-469 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.0299728

151.6613301

BELMONT NORTH

Woolworths Service Station Belmont North

399 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.02454211

151.6634893

BELMONT NORTH

Caltex Belmont North Service Station

406 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.02476876

151.6623655

BELMONT NORTH

Belmont Bus Depot

2 Floraville ROAD

Other Petroleum

Regulation under CLM Act not required

-33.02476269

151.6606657

BELMORE

SRA Land

348 Burwood ROAD

Unclassified

Regulation under CLM Act not required

-33.91753611

151.0859487

BELMORE

7-Eleven Service Station

792-794 Canterbury ROAD

Service Station

Regulation under CLM Act not required

-33.92567992

151.0873469

BELROSE

Glenrose Shopping Centre

56-58 Glen STREET

Unclassified

Contamination currently regulated under CLM Act

-33.73917996

151.2101029

BELROSE

Woolworths Petrol

60 Glen STREET

Service Station

Regulation under CLM Act not required

-33.74009002

151.2091045

BELROSE

Caltex Service Station

157 Forest WAY

Service Station

Regulation under CLM Act not required

-33.7347675

151.2212004

BENNETTS GREEN

Former Windale Wastewater Treatment Works

8 Templar PLACE

Other Industry

Regulation under CLM Act not required

-33.00317523

151.6936636

BERESFIELD

BP Beresfield Truckstop

2 Kinta Drive, corner John Renshaw DRIVE Service Station

Regulation under CLM Act not required

-32.81122768

151.6393427

BERESFIELD

Former Koppers Timber Treatment Site

53 Weakleys DRIVE

Other Industry

Regulation under CLM Act not required

-32.79902937

151.6358846

BERKELEY VALE

Former Berkeley Vale Service Station

121-123 Lakedge AVENUE

Service Station

Regulation under CLM Act not required

-33.34899186

151.4423109

BERKSHIRE PARK

Shell Coles Express Berkshire Park

746 - 752 Richmond ROAD

Service Station

Regulation under CLM Act not required

-33.66508654

150.7990243

List current as at 8 March 2022

15 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BEROWRA

Caltex Berowra Service Station

12-14 Berowra Waters ROAD

Service Station

Regulation under CLM Act not required

-33.6233827

151.1505554

BEROWRA

7-Eleven Berowra Service Station

965-969 Pacific (Cnr Waratah Rd) HIGHWAY

Service Station

Regulation under CLM Act not required

-33.62673163

151.1479171

BEROWRA

Shell Coles Express Berowra

955 Pacific (Cnr Yallambee Rd) HIGHWAY Service Station

Regulation under CLM Act not required

-33.62818015

151.1475736

BEROWRA

42 Berowra Waters Road

42 Berowra Waters ROAD

Unclassified

Regulation under CLM Act not required

-33.6203823

151.1481246

BERRIGAN

Caltex Service Station Berrigan

155-165 Chanter STREET

Service Station

Regulation under CLM Act not required

-35.6557616

145.8015557

BERRY

Berry Service Centre - Shell Branded

88 Queen STREET

Service Station

Regulation under CLM Act not required

-34.77571634

150.6961713

BERRY

BP branded service station Berry (Formerly Shell)

75 Queen STREET

Service Station

Contamination currently regulated under POEO Act

-34.77500516

150.695167

BEXLEY

7-Eleven Bexley

474 Forest ROAD

Service Station

Regulation under CLM Act not required

-33.95160096

151.1252355

BEXLEY

7-Eleven (former Mobil) Service Station Bexley

613 Forest ROAD

Service Station

Regulation under CLM Act not required

-33.95539246

151.118447

BILAMBIL HEIGHTS

Former Banana Plantation Land

38 McAllisters ROAD

Other Industry

Regulation under CLM Act not required

-28.21218056

153.4778762

BILLINUDGEL

CSR Readymix

Mogo PLACE

Other Industry

Regulation under CLM Act not required

-28.50210255

153.5278161

BILLINUDGEL

Billinudgel General Store

2A Wilfred STREET

Service Station

Under assessment

-28.50210255

153.5278161

BLACKMANS FLAT

Mount Piper Extension Development Site 2847 Boulder ROAD

Other Industry

Regulation under CLM Act not required

-33.35619968

150.0279881

BLACKMANS FLAT

Western Coal Services (former Lamberts Gully Mine)

Castlereagh HIGHWAY

Other Industry

Regulation under CLM Act not required

-33.36713827

150.0483236

BLACKTOWN

Former Caltex Service Station

131 Richmond ROAD

Service Station

Regulation under CLM Act not required

-33.75866104

150.8962614

List current as at 8 March 2022

16 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BLACKTOWN

Valspar Blacktown

4 Steel STREET

Chemical Industry

Regulation under CLM Act not required

-33.75425018

150.9127714

BLACKTOWN

Harpers Bush (Reserve 752)

Reservoir ROAD

Unclassified

Regulation under CLM Act not required

-33.79119448

150.8967838

BLACKTOWN

7-Eleven Service Station

60 Walters ROAD

Service Station

Regulation under CLM Act not required

-33.77599783

150.8948926

BLAKEHURST

Woolworths Service Station Blakehurst

390 Princes HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-33.99019694

151.1135663

BLAKEHURST

The Bay Nursing Home

392 & 394 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-33.99030465

151.1140293

BLAXLAND

7-Eleven (former Mobil) Service Station

137 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.74627

150.6137669

BOAMBEE

Lindsay Bros transport depot site

542 Pacific HIGHWAY

Other Petroleum

Regulation under CLM Act not required

-30.33106848

153.0802985

BOAMBEE

BP-branded (former Mobil) Boambee Service Station

601 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-30.33544287

153.0817266

BOBS FARM

Bob's Farm

15 Fenningham Island ROAD

Other Industry

Regulation under CLM Act not required

-32.74867207

152.0316217

BOGGABILLA

Former Caltex Service Station

90 Simpson Street, corner Newell HIGHWAY

Service Station

Regulation under CLM Act not required

-28.60654029

150.3571056

BOGGABILLA

Lowes (Former Mobil) Depot

Newell HIGHWAY

Other Petroleum

Regulation under CLM Act not required

-28.61023985

150.3529156

BOMADERRY

Caltex Service Station

341 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.84561952

150.5946978

BOMADERRY

Caltex Service Station Bomaderry

246 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.83833824

150.5958799

BOMADERRY

Former Mobil Emoleum Depot

7 Victa WAY

Other Petroleum

Regulation under CLM Act not required

-34.84454618

150.6139462

BOMADERRY

Former Shell Depot

44 Railway STREET

Other Petroleum

Regulation under CLM Act not required

-34.85193621

150.6117038

List current as at 8 March 2022

17 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BOMADERRY

SRA Land

Lot 2 Meroo STREET

Unclassified

Regulation under CLM Act not required

-34.85314813

150.6099573

BOMADERRY

Bomaderry Works Depot

10 McIntyre WAY

Other Petroleum

Regulation under CLM Act not required

-34.84576748

150.6131411

BOMADERRY

Commercial Land

320 Princes HIGHWAY

Other Industry

Contamination currently regulated under CLM Act

-34.84424073

150.5958149

BOMBALA

Caltex Service Station Bombala

159-161 Maybe STREET

Service Station

Regulation under CLM Act not required

-36.91234945

149.2374622

BOMBALA

Former Bright Street Timber Mill

Bright STREET

Other Industry

Regulation under CLM Act not required

-36.91547645

149.2302454

BOMBALA

Caltex Bombala Service Station

High Street corner Stephen STREET

Service Station

Regulation under CLM Act not required

-36.90447935

149.241292

BOMBALA

Prime Pine site

Sandy LANE

Other Industry

Regulation under CLM Act not required

-36.9315425

149.2110959

BOMEN

Caltex Terminal

34 Lewington STREET

Other Petroleum

Regulation under CLM Act not required

-35.0700202

147.4121955

BOMEN

Enirgi Power Storage Recycling

509 Byrnes ROAD

Other Industry

Under assessment

-35.058638

147.428731

BONDI

BP-branded Service Station

185 Bondi ROAD

Service Station

Regulation under CLM Act not required

-33.89432208

151.2647671

BONDI

Caltex Service Station Bondi

51 Bondi ROAD

Service Station

Regulation under CLM Act not required

-33.8936307

151.260001

BONDI JUNCTION

Waverley Bus Depot

1-15 Oxford STREET

Other Industry

Regulation under CLM Act not required

-33.89165341

151.2421246

BONNY HILLS

Bonny View Store

923 Ocean DRIVE

Service Station

Regulation under CLM Act not required

-31.59075636

152.8392935

BONNYRIGG

Metro (Formerly United & AP SAVER) Service Station Bonnyrigg

709 Cabramatta (W) ROAD

Service Station

Regulation under CLM Act not required

-33.89297085

150.8925935

BONNYRIGG HEIGHTS

BP-Branded Service Station Bonnyrigg

451 North Liverpool ROAD

Service Station

Regulation under CLM Act not required

-33.89416327

150.8578378

List current as at 8 March 2022

18 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BOOLAROO

Cardiff West Estate - Pasminco Cockle Creek

Adjacent to PCC Smelter at 13A Main ROAD

Metal Industry

Regulation under CLM Act not required

-32.93950137

151.6349183

BOOLAROO

Cockle Creek and Cockle Bay Sediments

Off Creek Reserve ROAD

Metal Industry

Contamination currently regulated under CLM Act

-32.96079541

151.6141327

BOOLAROO

Pasminco Cockle Creek Smelter

Lake ROAD

Metal Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-32.94434593

151.6307345

BOOLAROO

Incitec Pivot

13 Main STREET

Other Industry

Contamination formerly regulated under the CLM Act

-32.94803538

151.6302187

BOOLAROO

Bunnings Site - Pasminco Cockle Creek

13a Main ROAD

Metal Industry

Contamination formerly regulated under the CLM Act

-32.94364503

151.6252316

BOOLAROO

Part Lot 2 DP1127713 (proposed Lot G) Pasminco Cockle Creek Smelter site

13a Main ROAD

Metal Industry

Contamination formerly regulated under the CLM Act

-32.94404392

151.6267695

BOOLAROO

Lot 600 DP1228699 (formerly Part Lot 2 DP1127713 & proposed 'Lot D') Pasminco Cockle Creek Smelter site

Main ROAD

Metal Industry

Contamination formerly regulated under the CLM Act

-32.94440875

151.6264143

BOOROWA

Former Mobil Depot

14-16 Brial STREET

Other Petroleum

Regulation under CLM Act not required

-34.43673234

148.7300821

BOOROWA

Mobil Service Station

63-69 Marsden STREET

Service Station

Contamination formerly regulated under the CLM Act

-34.44157331

148.7162391

BOOROWA

Boorowa Service Station

84 Marsden STREET

Service Station

Under assessment

-34.443029

148.715109

BOTANY

Former Aerosols of Australia

1617 Botany ROAD

Chemical Industry

Regulation under CLM Act not required

-33.9529386

151.2037468

BOTANY

Allnex

49-61 Stephen ROAD

Chemical Industry

Contamination currently regulated under CLM Act

-33.9524442

151.2106446

BOTANY

Former Tannery

2 Daniel STREET

Other Industry

Regulation under CLM Act not required

-33.94126194

151.1991087

BOTANY

Botany, Underwood

14a Underwood AVENUE

Unclassified

Contamination being managed via the planning process (EP&A Act)

-33.94508532

151.1947626

BOTANY

Roads and Maritime Service

5 - 9 Lord STREET

Other Industry

Regulation under CLM Act not required

-33.94100279

151.1968763

List current as at 8 March 2022

19 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BOTANY

Former Industrial Site

28 Folkestone PARADE

Unclassified

Contamination being managed via the planning process (EP&A Act)

-33.95187539

151.1960537

BOURKE

Caltex Service Station

82-86 Anson STREET

Service Station

Regulation under CLM Act not required

-30.09500388

145.9414388

BOURKE

Former Shell Bourke Depot

94-106 Anson STREET

Service Station

Regulation under CLM Act not required

-30.09548497

145.9436745

BOWENFELS

Bowenfels Field Support Centre

9-13 Cooerwull ROAD

Other Petroleum

Regulation under CLM Act not required

-33.47514572

150.1323899

BOWRAL

Shell Coles Express Bowral Service Station 430 Bong Bong STREET

Service Station

Regulation under CLM Act not required

-34.48269596

150.417389

BOWRAL

Former Gasworks

Merrigang STREET

Gasworks

Contamination currently regulated under CLM Act

-34.4783957

150.4255053

BOX HILL

Former Waste Management Facility

25 Terry ROAD

Landfill

Regulation under CLM Act not required

-33.65559259

150.8977986

BOX HILL

Former Poultry Farm

27-33 Boundary ROAD

Other Industry

Regulation under CLM Act not required

-33.64866563

150.8815467

BOX HILL

Former Poultry Farm

19-25 Boundary ROAD

Other Industry

Regulation under CLM Act not required

-33.65038071

150.8813725

BRANXTON

Former Service Station Branxton

Part of 70 Maitland STREET

Service Station

Contamination currently regulated under CLM Act

-32.65631582

151.3516243

BRANXTON

Branxton Wastewater Treatment Works

2151 New England HIGHWAY

Other Industry

Regulation under CLM Act not required

-32.66069944

151.3625572

BREWARRINA

Dowell's Fuel

39 Doyle STREET

Service Station

Regulation under CLM Act not required

-29.96152786

146.8612561

BRIGHTON-LE-SANDS

Shell Service Station Brighton Le Sands & adjacent land

2 General Holmes DRIVE

Service Station

Contamination formerly regulated under the CLM Act

-33.95791132

151.1576486

BRIGHTON-LE-SANDS

Cook Park

General Holmes DRIVE

Service Station

Contamination formerly regulated under the CLM Act

-33.9581072

151.1579572

BROADMEADOW

Former Industrial Site

16 Broadmeadow ROAD

Service Station

Regulation under CLM Act not required

-32.91444096

151.7300112

List current as at 8 March 2022

20 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

BROADMEADOW

Nineways Broadmeadow Coles Express SS Corner Brunker Road and Lambton ROAD Service Station

Regulation under CLM Act not required

BROADMEADOW

2 Georgetown Road, Broadmeadow NSW 2292 2 Georgetown ROAD

Metal Industry

Under assessment

BROKEN HEAD

South Byron Sewage Treatment Works

Broken Head ROAD

Other Industry

BROKEN HILL

Former Caltex Depot

3 Kanandah ROAD

BROKEN HILL

Former Caltex Service Station

BROKEN HILL

Latitude

Longitude

-32.92511185

151.7364247

-35.085626

147.403807

Regulation under CLM Act not required

-28.67233626

153.6148974

Service Station

Regulation under CLM Act not required

-31.98341823

141.4332211

167-173 Argent STREET

Service Station

Regulation under CLM Act not required

-31.96066663

141.4624175

Caltex Service Station

535 Argent STREET

Service Station

Regulation under CLM Act not required

-31.95311924

141.4745274

BROKEN HILL

Tasco Petroleum (Former Mobil) Depot

5 Kanandah ROAD

Other Petroleum

Regulation under CLM Act not required

-31.9843986

141.4329127

BROKEN HILL

Former Mobil Aviation Refuelling Facility, Broken Hill Airport Airport ROAD

Other Petroleum

Regulation under CLM Act not required

-31.99928312

141.4685759

BROKEN HILL

Caltex Service Station

73-87 Oxide STREET

Service Station

Contamination formerly regulated under the CLM Act

-31.95519591

141.4658647

BROKEN HILL

Former Mobil Depot

Corner Of Talc Street and Gossan STREET Other Petroleum

Regulation under CLM Act not required

-31.96018102

141.4514752

BROKEN HILL

Former Gasworks

Cornish STREET

Gasworks

Contamination formerly regulated under the CLM Act

-31.96330562

141.4470611

BROKEN HILL

Broken Hill Gas Turbines

76A Pinnacles ROAD

Unclassified

Under assessment

-31.986401

141.420435

BROKEN HILL

Broken Hill Railway Yard

Crystal STREET

Landfill

Under assessment

-31.971951

141.452863

BROOKLYN

Former Oyster Farm

139 Brooklyn (Off Government) ROAD

Unclassified

Regulation under CLM Act not required

-33.54716867

151.2229744

BROOKVALE

Coles Express Service Station Brookvale

198 Harbord ROAD

Service Station

Regulation under CLM Act not required

-33.76332299

151.2794028

List current as at 8 March 2022

21 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BROOKVALE

Woolworths Petrol Brookvale

756 Pittwater ROAD

Service Station

Regulation under CLM Act not required

-33.76170587

151.2762411

BROOKVALE

Caltex Service Station Brookvale

740-742 Pittwater ROAD

Service Station

Regulation under CLM Act not required

-33.76146721

151.2745358

BROOKVALE

Harrison Manufacturing

75 Old Pittwater ROAD

Other Industry

Regulation under CLM Act not required

-33.76497282

151.2637961

BROOKVALE

Brookvale Bus Depot

630-636 Pittwater ROAD

Other Petroleum

Regulation under CLM Act not required

-33.76641698

151.2705659

BROOKVALE

Warringah Mall

Cnr Condamine Street, Old Pittwater Rd & Cross STREET Other Industry

Regulation under CLM Act not required

-33.76729923

151.2657272

BROOKVALE

Littles Dry Cleaning

123 Old Pittwater ROAD

Other Industry

Regulation under CLM Act not required

-33.76759121

151.2625932

BROOMS HEAD

Former Brooms Head General Store and Service Station

92 Ocean ROAD

Service Station

Regulation under CLM Act not required

-29.60711599

153.3346312

BROWNSVILLE

Caltex Service Station

342 Kanahooka ROAD

Service Station

Regulation under CLM Act not required

-34.48591734

150.8064373

BRUNSWICK HEADS

Caltex Service Station

5 Tweed STREET

Service Station

Regulation under CLM Act not required

-28.5381619

153.5487135

BUDGEWOI

Colongra Power Station

Off Scenic DRIVE

Other Industry

Under assessment

-33.21463137

151.5529338

BULAHDELAH

Caltex Service Station

8 Red Gum Road, Corner Mahogany STREET

Service Station

Regulation under CLM Act not required

-32.39837094

152.2106015

BULAHDELAH

Former Caltex Service Station

53-59 Bulahdelah WAY

Service Station

Regulation under CLM Act not required

-32.40721638

152.2110291

BULAHDELAH

BP-branded (former Mobil) Service Station

73-75 Bulahdelah WAY

Service Station

Regulation under CLM Act not required

-32.40971018

152.2105785

BULLABURRA

Former Burmah Bullaburra Service Station 367 - 369 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.72482995

150.4124537

BULLI

Scrap Yard

Other Industry

Contamination formerly regulated under the CLM Act

-34.33663195

150.9131154

List current as at 8 March 2022

7 Molloy STREET

22 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

BULLI

Bulli Brickworks

Quilkey PLACE

Other Industry

Regulation under CLM Act not required

-34.33263113

150.9086247

BUNGALORA

Former landfill area

Part of 840 Terranora ROAD

Other Industry

Regulation under CLM Act not required

-28.2424318

153.4789209

BUNGENDORE

Former Timber Treatment Plant

Corner King Street and Butmaroo STREET Other Industry

Contamination formerly regulated under the CLM Act

-35.26151273

149.4434907

BUNGENDORE

Bungendore Railway Station and Rail Corridor

Bungendore STREET

Unclassified

Under assessment

-35.25574

149.446405

BURONGA

Caltex Service Station

Sturt Hwy Cnr Silver City HIGHWAY

Service Station

Regulation under CLM Act not required

-34.17056496

142.1813847

BURWOOD

Burwood STA Depot

Cnr Shaftesbury and Parramatta ROADS

Other Industry

Contamination formerly regulated under the CLM Act

-33.86982934

151.1089057

BYRON BAY

Residential Development

Lot 15 Seaview STREET

Unclassified

Regulation under CLM Act not required

-28.65214464

153.6165573

BYRON BAY

Butler Street Reserve Byron Bay

Butler STREET

Landfill

Under assessment

-28.64340617

153.6099674

CABARITA

Dulux (Orica Australia)

Cabarita ROAD

Chemical Industry

Contamination formerly regulated under the CLM Act

-33.84643972

151.1157115

CABARITA

Wellcome Soil Containment Cells Cabarita 47 and 48 Phillips STREET

Other Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.85250251

151.1176366

CABRAMATTA

Caltex (former Mobil) Lansvale Service Station

141 Hume HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-33.89442261

150.9571507

CABRAMATTA

Caltex Service Station Cabramatta

168 John STREET

Service Station

Regulation under CLM Act not required

-33.89422314

150.9279279

CABRAMATTA

Cabramatta Creek

17 A and 19A Liverpool Street STREET

Unclassified

Regulation under CLM Act not required

-33.90284952

150.9415616

CABRAMATTA WEST

BP Lansvale

115-119 Hume HIGHWAY

Service Station

Regulation being finalised

-33.89373753

150.9587201

CABRAMURRA

Selwyn Snowfields / Selwyn Snow Resort

213A Kings Cross ROAD

Other Industry

Regulation under CLM Act not required

-35.90578

148.4501785

List current as at 8 March 2022

23 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

CALGA

Former service station

101 Peats Ridge ROAD

Service Station

Contamination formerly regulated under the CLM Act

CALLALA BEACH

Callala Beach General Store

(formerly 1 Quay Rd) 114A Quay ROAD

Service Station

CAMBRIDGE GARDENS

Caltex Cambridge Park

1 Boomerang PLACE

CAMDEN

Camden High School (former)

CAMDEN

Latitude

Longitude

-33.37592138

151.2254951

Regulation under CLM Act not required

-35.0101817

150.6964322

Service Station

Regulation under CLM Act not required

-33.74068794

150.717174

John STREET

Gasworks

Regulation under CLM Act not required

-34.05114079

150.6951285

Caltex Camden Service Station

21 Barsden STREET

Service Station

Regulation under CLM Act not required

-34.05808413

150.6914744

CAMDEN SOUTH

Coles Express Service Station Camden South

273 Old Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-34.08660995

150.6945444

CAMELLIA

Hymix Concrete

14 Grand AVENUE

Metal Industry

Contamination currently regulated under CLM Act

-33.82243454

151.044789

CAMELLIA

Mauri Foods

15 Grand AVENUE

Other Industry

Regulation being finalised

-33.81996985

151.0335725

CAMELLIA

James Hardie Factory (former, eastern portion)

1 Grand AVENUE

Other Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.81822448

151.0260958

CAMELLIA

Bitumen Manufacturer

12 Grand AVENUE

Other Industry

Contamination currently regulated under CLM Act

-33.82189695

151.0429251

CAMELLIA

Hambear

14 Thackeray STREET

Metal Industry

Regulation under CLM Act not required

-33.81920482

151.0419394

CAMELLIA

Former Asciano Properties

37A and 39 Grand AVENUE

Chemical Industry

Contamination currently regulated under CLM Act

-33.82056014

151.0443331

CAMELLIA

Railway Land

27 Grand AVENUE

Other Industry

Regulation under CLM Act not required

-33.81910822

151.0382483

CAMELLIA

Wrigg

13 Grand AVENUE

Metal Industry

Under preliminary investigation order

-33.81971361

151.0321525

CAMELLIA

Former Akzo Nobel site

6 Grand AVENUE

Chemical Industry

Contamination currently regulated under CLM Act

-33.82238826

151.0319264

List current as at 8 March 2022

24 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

CAMELLIA

Former Shell Clyde Refinery

Durham STREET

Other Industry

Contamination currently regulated under POEO Act

-33.82804924

151.0378966

CAMELLIA

Council Reserve

11B Grand AVENUE

Metal Industry

Regulation under CLM Act not required

-33.81850502

151.0302425

CAMELLIA

Veolia

37 Grand AVENUE

Chemical Industry

Contamination currently regulated under CLM Act

-33.81980027

151.0430689

CAMELLIA

Sydney Water

41 Grand AVENUE

Chemical Industry

Contamination formerly regulated under the CLM Act

-33.8217493

151.0453367

CAMELLIA

Maritime Services Board

33A Grand AVENUE

Metal Industry

Regulation under CLM Act not required

-33.81836086

151.0401249

CAMMERAY

Tunks Park

Brothers AVENUE

Landfill

Contamination formerly regulated under the CLM Act

-33.81734704

151.2113338

CAMMERAY

Coles Express Cammeray

477-483 Miller STREET

Service Station

Regulation under CLM Act not required

-33.82141124

151.2108658

CAMPBELLTOWN

Mobil Service Station

96-98 Queen STREET

Service Station

Regulation under CLM Act not required

-34.06407588

150.8170082

CAMPBELLTOWN

BP Macarthur Service Station

Cnr Blaxland ROAD and Campbelltown ROAD

Service Station

Regulation under CLM Act not required

-34.05312872

150.8234349

CAMPBELLTOWN

Former vehicle wrecking yard

38 Blaxland ROAD

Other Industry

Regulation under CLM Act not required

-34.06055735

150.8130598

CAMPERDOWN

Former Gee Graphics

27 Church STREET

Other Industry

Regulation under CLM Act not required

-33.88737747

151.1773616

CAMPERDOWN

O'Dea Reserve

Salisbury LANE

Landfill

Contamination formerly regulated under the CLM Act

-33.89072786

151.1736948

CAMPERDOWN

The Spruce

12-14 Marsden STREET

Other Industry

Regulation under CLM Act not required

-33.88720632

151.1784514

CAMPSIE

Budget Petroleum and adjacent property 403 Canterbury Road and 1 Una STREET

Service Station

Contamination currently regulated under CLM Act

-33.91605617

151.1086596

CAMPSIE

Former Sunbeam factory

Other Industry

Contamination formerly regulated under the CLM Act

-33.92254225

151.1025796

List current as at 8 March 2022

60 Charlotte STREET

25 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

CANLEY HEIGHTS

Former Caltex Canley Heights

368 Canley Vale ROAD

Service Station

Regulation under CLM Act not required

-33.88271081

150.9154176

CANLEY HEIGHTS

Caltex Canley Heights Service Station

280-286 Canley Vale ROAD

Service Station

Regulation under CLM Act not required

-33.88393501

150.9241656

CANLEY VALE

Coles Express Lansvale

99 Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-33.89295753

150.9606136

CANLEY VALE

Former Mobil Service Station

96 Canley Vale ROAD

Service Station

Regulation under CLM Act not required

-33.88591573

150.9369801

CANOWINDRA

BP-branded Jasbe Service Station

76 Rodd STREET

Service Station

Regulation under CLM Act not required

-33.56131773

148.6682805

CANTERBURY

Metro Petroleum Service Station

13-19 Canterbury ROAD

Service Station

Contamination currently regulated under CLM Act

-33.90783455

151.125207

CAPTAINS FLAT

Rail corridor adjacent to Lake George Mine

1 Copper Creek Road ROAD

Other Industry

Contamination currently regulated under CLM Act

-35.589869

149.437657

CAPTAINS FLAT

Captains Flat former Station Masters Cottage

2 Copper Creek ROAD

Other Industry

Under assessment

-35.59027127

149.4384122

CARDIFF

7-Eleven Service Station

399 Main ROAD

Service Station

Regulation under CLM Act not required

-32.93391137

151.6562111

CARDIFF

Former Caltex Service Station

367 Main ROAD

Service Station

Regulation under CLM Act not required

-32.93761223

151.6577781

CARDIFF

Maneela Oval

Main ROAD

Other Industry

Regulation under CLM Act not required

-32.93018443

151.6435559

CARDIFF

Former Mobil Depot

7 Ranton STREET

Other Petroleum

Regulation under CLM Act not required

-32.94516764

151.6470387

CARDIFF

BP Service Station (Reliance Petroleum)

Corner Sturt and Main ROADS

Service Station

Regulation under CLM Act not required

-32.93792229

151.6569905

CARDIFF

Woolworths (former Mobil) Cardiff Service Station

43 Macquarie ROAD

Service Station

Regulation under CLM Act not required

-32.94118246

151.6578195

CARINGBAH

Adjacent to Spirent Australia

101-103 Cawarra ROAD

Other Industry

Contamination formerly regulated under the CLM Act

-34.03360747

151.1245577

List current as at 8 March 2022

26 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

CARINGBAH

Former Consumer Health Products Manufacturer

32-40 Cawarra ROAD

Other Industry

Regulation under CLM Act not required

-34.03024369

151.1277755

CARINGBAH

Caltex Lilli Pilli Service Station

477-481 Port Hacking ROAD

Service Station

Regulation under CLM Act not required

-34.05243807

151.1216353

CARINGBAH

7-Eleven Service Station

367 The KINGSWAY

Service Station

Regulation under CLM Act not required

-34.03948677

151.1203268

CARINGBAH

Spirent Australia

105 Cawarra ROAD

Other Industry

Contamination formerly regulated under the CLM Act

-34.03425343

151.1245092

CARINGBAH

BP Service Station Caringbah

54 Captain Cook DRIVE

Service Station

Regulation under CLM Act not required

-34.032986

151.1250656

CARLINGFORD

Caltex Service Station Carlingford

131 Pennant Hills ROAD

Service Station

Regulation under CLM Act not required

-33.78762398

151.0279422

CARLINGFORD

Caltex Service Station

797 Pennant Hills ROAD

Service Station

Regulation under CLM Act not required

-33.7757819

151.0516532

CARLTON

Shell Coles Express Service Station

277 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-33.9748579

151.1272732

CARRINGTON

Commercial Metals Company (CMC) Australia Pty Ltd

117-121 Bourke STREET

Other Industry

Regulation under CLM Act not required

-32.9148832

151.7677193

CARRINGTON

Carrington redevelopment site

11 Howden STREET

Other Industry

Regulation under CLM Act not required

-32.91309509

151.7625341

CARRINGTON

Forgacs Dockyard

81 Denison STREET

Other Industry

Regulation under CLM Act not required

-32.9207441

151.764816

CARRINGTON

NAT vacant land

Bourke STREET

Unclassified

Regulation under CLM Act not required

-32.91276029

151.7685894

CARRINGTON

Dyke Point Containment Cell

Dyke ROAD

Other Industry

Regulation under CLM Act not required

-32.91763422

151.7727101

CARRINGTON

Carrington Coal Tar Pavements

Bourke Street to Dyke ROAD

Other Industry

Regulation under CLM Act not required

-32.91441348

151.770271

CARRINGTON

Pasminco Ship Loader

Dyke Berth 2 (off Bourke Street) OTHER

Metal Industry

Regulation under CLM Act not required

-32.9148698

151.7716837

List current as at 8 March 2022

27 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

CARSS PARK

Vacant Property

334 Princes HIGHWAY

Other Industry

Regulation under CLM Act not required

CARSS PARK

Kogarah War Memorial Pool

78 Carwar AVENUE

Other Industry

Under assessment

CARWELL

Cement Australia Carwell Creek Quarries

Quarry ROAD

Other Industry

CASINO

Caltex Service Station and Depot Casino

28 & 32 Dyraaba STREET

CASINO

Caltex Service Station

CASINO

Latitude

Longitude

-33.98628486

151.1133908

-33.989419

151.12005

Regulation under CLM Act not required

-32.85570277

149.9170908

Service Station

Regulation under CLM Act not required

-28.85488567

153.044806

96 Centre STREET

Service Station

Regulation under CLM Act not required

-28.86539567

153.0450654

Former Gasworks

134-136 North STREET

Gasworks

Regulation under CLM Act not required

-28.86080712

153.0526043

CASINO

Woolworths Service Station Casino

130 Canterbury STREET

Service Station

Regulation under CLM Act not required

-28.86231341

153.0464642

CASINO

18 Beith Street, Casino

18 Beith STREET

Unclassified

Regulation under CLM Act not required

-28.84951426

153.0446585

CASINO

Corner Store

30 Barker STREET

Service Station

Regulation under CLM Act not required

-28.86316792

153.0389124

CASINO

Casino Roadhouse

86 Johnston STREET

Service Station

Contamination currently regulated under CLM Act

-28.85960698

153.0562429

CASULA

Caltex Casula Service Station

646 Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-33.95641262

150.8934783

CATHERINE HILL BAY

Catherine Hill Bay Coal Handling and Preparation Plant

1A Keene STREET

Other Industry

Regulation under CLM Act not required

-33.16120556

151.6302456

CESSNOCK

Caltex Cessnock Service Station

103-105 Wollombi (Cnr James Street) ROAD

Service Station

Regulation under CLM Act not required

-32.83936243

151.3430078

CESSNOCK

Former Mobil Service Station

102 Wollombi ROAD

Service Station

Regulation under CLM Act not required

-32.83844074

151.3436022

CESSNOCK

Former Service Station

2-4 Allandale ROAD

Service Station

Regulation under CLM Act not required

-32.83118911

151.3560677

List current as at 8 March 2022

28 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

CHARBON

Charbon Colliery

Charbon ROAD

Other Industry

Regulation under CLM Act not required

-32.92390131

149.9839098

CHARLESTOWN

7-Eleven Charlestown

273 Charlestown ROAD

Service Station

Regulation under CLM Act not required

-32.95797076

151.6896275

CHARLESTOWN

Caltex Service Station

81 Pacific HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-32.96715274

151.6955462

CHARLESTOWN

Caltex Woolworths (Former BP)

91-93 Pacific HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-32.96631255

151.6959086

CHARLESTOWN

Ausgrid Powell Street Depot

8 Powell STREET

Other Industry

Regulation under CLM Act not required

-32.95912375

151.6944136

CHARMHAVEN

Caltex Charmhaven Service Station

13-15 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.21655768

151.5091452

CHATSWOOD

Former Caltex Chatswood Service Station 607 Pacific HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-33.80396472

151.1795766

CHATSWOOD

Woolworths Chatswood

364-366 Eastern Valley WAY

Service Station

Regulation under CLM Act not required

-33.78667419

151.2010828

CHATSWOOD

Caltex Service Station Chatswood

572 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.80381271

151.1789656

CHATSWOOD

Auto Repairs

2 Devonshire STREET

Service Station

Regulation under CLM Act not required

-33.8015482

151.1859632

CHATSWOOD

Coles Express Service Station Chatswood

877-879 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.79182176

151.1804867

CHATSWOOD

Chatswood Toyota

728 Pacific HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-33.79654247

151.1776136

CHERRYBROOK

Caltex Service Station

67 Shepherds DRIVE

Service Station

Regulation under CLM Act not required

-33.72069183

151.0451415

CHESTER HILL

Former Orica, Chester Hill

127 Orchard ROAD

Chemical Industry

Contamination formerly regulated under the CLM Act

-33.8869823

150.9952873

CHESTER HILL

Various industrial premises

191 Miller ROAD

Chemical Industry

Under assessment

-33.884091

150.995073

List current as at 8 March 2022

29 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

CHESTER HILL

Integrated Packaging

149 Orchard ROAD

Other Industry

Under assessment

CHIPPENDALE

Cnr Regent Street & Wellington Street, Chippendale

Wellington STREET

Chemical Industry

CHIPPING NORTON

Former Solchem (Mobil) Depot Chipping Norton

49-51 Riverside ROAD

CHIPPING NORTON

Former ACR

CHISWICK

Latitude

Longitude

-33.885645

150.995148

Contamination currently regulated under CLM Act

-33.88668912

151.2015246

Other Petroleum

Regulation under CLM Act not required

-33.91621314

150.9696948

85-107 Alfred STREET

Chemical Industry

Contamination currently regulated under CLM Act

-33.92226795

150.9586496

Former Sydney Wiremills (BHP) site

Blackwall Point ROAD

Other Industry

Regulation under CLM Act not required

-33.85131849

151.1369131

CHITTAWAY BAY

Former Caltex Chittaway Point

100 Chittaway ROAD

Service Station

Regulation under CLM Act not required

-33.32707555

151.4293546

CHULLORA

Chullora Railway Workshops

Worth STREET

Other Industry

Regulation under CLM Act not required

-33.88639388

151.0598201

CLANDULLA

Brogans Creek Quarry

Brogans Creek ROAD

Other Industry

Under assessment

-32.997442

149.960912

CLARENCE

Clarence Colliery

Chifley ROAD

Other Industry

Regulation under CLM Act not required

-33.46450217

150.2522729

CLARENDON

Coles Express Clarendon Service Station

244 Hawkesbury Valley WAY

Service Station

Regulation under CLM Act not required

-33.6083729

150.7890956

CLEARFIELD

Former Pamplings Dip Site

Off Clearfield ROAD

Cattle Dip

Regulation under CLM Act not required

-29.16287185

152.882974

CLYBUCCA

BP Service Station

2171 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-30.93845014

152.9422791

CLYDE

7-Eleven Clyde

3 Parramatta Road, corner Harbord STREET

Service Station

Regulation under CLM Act not required

-33.83494433

151.0222628

CLYDE

4 Tennyson Street, Clyde NSW 2142

4 Tennyson STREET

Other Industry

Regulation under CLM Act not required

-33.83268843

151.0267361

COBAR

Former Caltex (Bogas) Service Station Cobar

56-58 Marshall STREET

Service Station

Regulation under CLM Act not required

-31.49793339

145.8346684

List current as at 8 March 2022

30 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

COBAR

Mckinnons Gold Mine

Cobar ROAD

Metal Industry

Regulation under CLM Act not required

-31.78179755

145.693

COBAR

Caltex Service Station Cobar

99 Marshall (formerly Cnr Barrier Highway and Bathurst Street) STREET Service Station

Regulation under CLM Act not required

-31.49631924

145.8275727

COBAR

Caltex Service Station

Lot 10 Railway PARADE

Service Station

Regulation under CLM Act not required

-31.49350124

145.8442372

COFFS HARBOUR

BP Service Station

134-136 Pacific HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-30.29187037

153.1182106

COFFS HARBOUR

Dan Murphy's Coffs Harbour

10 Elbow STREET

Service Station

Regulation under CLM Act not required

-30.29439262

153.115069

COFFS HARBOUR

Mobil Service Station

314-316 Harbour DRIVE

Service Station

Contamination formerly regulated under the CLM Act

-30.3056983

153.131966

COFFS HARBOUR

Mobil Coffs Harbour Airport

Aviation DRIVE

Other Petroleum

Contamination formerly regulated under the CLM Act

-30.313385

153.1175018

COFFS HARBOUR

Woolworths Petrol

Park Beach Plaza, Arthur STREET

Service Station

Regulation under CLM Act not required

-30.28101154

153.132027

COFFS HARBOUR

Caltex Service Station

157 Orlando STREET

Service Station

Regulation under CLM Act not required

-30.28975334

153.1306354

COFFS HARBOUR

Coffs Harbour Slipway

38 Marina DRIVE

Other Industry

Regulation under CLM Act not required

-30.30325637

153.1441437

COFFS HARBOUR

Aussitel Backpackers Hostel

312 Harbour DRIVE

Service Station

Contamination formerly regulated under the CLM Act

-30.30585731

153.131645

COLEAMBALLY

Former Mobil Coleambally Depot

19 Bencubbin AVENUE

Other Petroleum

Regulation under CLM Act not required

-34.80279552

145.8945239

COLLARENEBRI

Former Shell Depot

Corner Narran Street and Queen STREET

Other Petroleum

Regulation under CLM Act not required

-29.54114772

148.5789365

COLONGRA

Munmorah Colliery

Scenic DRIVE

Other Industry

Regulation under CLM Act not required

-33.21297737

151.5416882

COLONGRA

Endeavour Colliery

Scenic DRIVE

Other Industry

Regulation under CLM Act not required

-33.21297737

151.5416882

List current as at 8 March 2022

31 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

COLYTON

Coles Express (former Ampol) Service Station

86-88 Great Western HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-33.77552363

150.7953105

CONCORD

Caltex Service Station

89 Parramatta ROAD

Service Station

Regulation under CLM Act not required

-33.86785624

151.0993769

CONCORD WEST

Caltex Service Station - 369 -375 Concord Road, Concord West 369-375 Concord ROAD

Service Station

Regulation under CLM Act not required

-33.84113835

151.0888843

CONDOBOLIN

BP-Branded Service Station

38 Denison Street, corner Molong STREET Service Station

Regulation under CLM Act not required

-33.08520378

147.1524976

CONDOBOLIN

Former Mobil Depot

6 Burnett STREET

Other Petroleum

Contamination formerly regulated under the CLM Act

-33.08010515

147.1642972

CONDOBOLIN

Former Ampol Depot

Cnr Parkes Road and Goobang STREET

Service Station

Regulation under CLM Act not required

-33.08034753

147.1642436

CONDOBOLIN

Former Caltex Depot

Parkes ROAD

Service Station

Regulation under CLM Act not required

-33.08255593

147.1585922

CONDOBOLIN

Mobil Condobolin Depot Railway Siding

Railway Siding behind 6 Burnett STREET

Other Petroleum

Regulation under CLM Act not required

-33.08058612

147.164225

CONSTITUTION HILL

Sydney Water Land

Caloola ROAD

Unclassified

Regulation under CLM Act not required

-33.79781738

150.9697436

COOGEE

Caltex Coogee Service Station

146-148 Coogee Bay Road, corner Mount STREET Service Station

Regulation under CLM Act not required

-33.91989232

151.2517454

COOKS HILL

Former Council Depot Cooks Hill

152 Bruce Street and 115 Corlette STREET Other Industry

Regulation under CLM Act not required

-32.93525537

151.7641074

COOLAC

Coolac Service Station

Corner Hume Highway and Coleman STREET

Service Station

Regulation under CLM Act not required

-34.95435052

148.1595525

COOLAH

BP Depot (Reliance Petroleum)

72 (formerly 17-23) Cunningham STREET

Other Petroleum

Regulation under CLM Act not required

-31.82275896

149.7243171

COOLONGOLOOK

Caltex Service Station

Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-32.21648325

152.322813

COOMA

Caltex Cooma Service Station

44 Sharp Street, corner Baron STREET

Service Station

Regulation under CLM Act not required

-36.23323489

149.1304134

List current as at 8 March 2022

32 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

COOMA

Former Mobil Cooma Depot

2 Commissioner STREET

Other Petroleum

Regulation under CLM Act not required

-36.23266081

149.1346674

COOMA

Former Caltex Cooma Depot

2 Short STREET

Service Station

Regulation under CLM Act not required

-36.2338672

149.1348862

COOMA

Lowes Petroleum Cooma Depot and Service Station (Former BP Reliance Petroleum)

2-4 Sharp STREET

Other Petroleum

Regulation under CLM Act not required

-36.22819468

149.1357696

COOMA

Woolworths Caltex Cooma Service Station Bombala Street Cnr Massie STREET

Service Station

Regulation under CLM Act not required

-36.23364626

149.1267469

COOMA

Former Shell Depot

48-50 Bradley STREET

Other Petroleum

Regulation under CLM Act not required

-36.23448955

149.1347987

COOMA

Former Shell Service Station

48-52 Sharp STREET

Service Station

Contamination formerly regulated under the CLM Act

-36.23350402

149.1299514

COONABARABRAN

Former Mobil Depot

49 Cowper STREET

Other Petroleum

Regulation under CLM Act not required

-31.27096226

149.2818461

COONABARABRAN

Shell Coles Express Service Station

2-6 John STREET

Service Station

Regulation under CLM Act not required

-31.27706775

149.27836

COONABARABRAN

Former Shell Coonabarabran CVRO

Corner Cowper St and Dawson St, formerly 51 Cowper STREET

Other Petroleum

Regulation under CLM Act not required

-31.27003745

149.281788

COONABARABRAN

Caltex Service Station

Cnr Dawson & Drummond STREET

Service Station

Regulation under CLM Act not required

-31.26994941

149.28183

COONABARABRAN

Caltex Service Station

85-87 John STREET

Service Station

Regulation under CLM Act not required

-31.27231215

149.2771297

COONAMBLE

Former Shell Coonamble Depot

Corner Aberford Street and Quambone ROAD

Other Petroleum

Regulation under CLM Act not required

-30.95349182

148.3793432

COONAMBLE

Caltex Service Station

Quambone ROAD

Service Station

Regulation under CLM Act not required

-30.95410067

148.3792167

COORANBONG

Former Poultry Farm - 91 Alton Road, Cooranbong

64 - 98 Alton ROAD

Unclassified

Regulation under CLM Act not required

-33.06860138

151.4512156

COORANBONG

Avondale Auto Centre

679 Freemans DRIVE

Service Station

Regulation under CLM Act not required

-33.06968809

151.4636293

List current as at 8 March 2022

33 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

COOTAMUNDRA

Former BP Depot

1-5 Murray STREET

Other Petroleum

Regulation under CLM Act not required

-34.62915841

148.0306962

COOTAMUNDRA

Caltex Service Station

26-34 Hovell STREET

Service Station

Regulation under CLM Act not required

-34.63624703

148.0347479

COOTAMUNDRA

Former Caltex Depot

219 Sutton STREET

Other Petroleum

Regulation under CLM Act not required

-34.65126548

148.0145283

COOTAMUNDRA

Former Ampol Service Station

72 Parker STREET

Service Station

Regulation under CLM Act not required

-34.63471008

148.0296112

COOTAMUNDRA

Cootamundra Gasworks

140-146 Hovell STREET

Gasworks

Contamination currently regulated under CLM Act

-34.64572841

148.0255049

COOTAMUNDRA

Former Amoco Depot

68-72 Hovell STREET

Other Petroleum

Contamination currently regulated under CLM Act

-34.63871124

148.0321134

COOTAMUNDRA

Former Ampol Cootamundra Rail Siding

Back Brawlin ROAD

Other Petroleum

Regulation under CLM Act not required

-34.65326425

148.0143068

CORAMBA

Martin Street

End of Martin Street and adjacent car park OTHER

Service Station

Ongoing maintenance required to manage residual contamination (CLM Act)

-30.22125208

153.0156997

CORNWALLIS

532 Cornwallis Road, Cornwallis

532 Cornwallis ROAD

Other Industry

Regulation under CLM Act not required

-33.57473895

150.7792839

COROWA

Corowa Shire Council Works Depot

24 Poseidon ROAD

Other Petroleum

Regulation under CLM Act not required

-35.98807923

146.3652266

COROWA

Former Ampol Corowa

10 Bow STREET

Service Station

Regulation under CLM Act not required

-35.99364786

146.3901259

COROWA

Cignall Corowa

280 Hume STREET

Service Station

Under preliminary investigation order

-36.00996015

146.3760437

CORRIMAL

Woolworths Petrol - Corrimal

275 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.37527426

150.8962637

CORRIMAL

7-Eleven Corrimal

138-146 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.36986818

150.8978241

COWRA

Landmark Fertiliser Storage Facility

Corner Young Road & Waratah STREET

Chemical Industry

Regulation under CLM Act not required

-33.84321832

148.6722578

List current as at 8 March 2022

34 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

COWRA

Lowes Petroleum (former BP Cowra Depot)

12 Campbell STREET

Other Petroleum

Regulation under CLM Act not required

COWRA

Former Gasworks

30 Brougham STREET

Gasworks

COWRA

Shell Depot

34 Brougham STREET

COWRA

Cowra Residential Site

CRANGAN BAY

Latitude

Longitude

-33.83803706

148.6977873

Contamination currently regulated under CLM Act

-33.8389659

148.6963482

Other Petroleum

Contamination formerly regulated under the CLM Act

-33.83913341

148.6973491

32 Brougham STREET

Landfill

Under assessment

-33.839137

148.697044

Big T Roadhouse

555 and 565 Pacific HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-33.17306517

151.6084446

CREMORNE

Shell Coles Express Service Station

225 Military ROAD

Service Station

Regulation under CLM Act not required

-33.83063306

151.226223

CRESTWOOD

Former Caltex Depot Queanbeyan

36 Kendall (Cnr Stephens Rd) AVENUE

Other Petroleum

Regulation under CLM Act not required

-35.34615546

149.207807

CRESTWOOD

Former BP Queanbeyan

64 Uriarra ROAD

Service Station

Regulation under CLM Act not required

-35.34646177

149.2246263

CRONULLA

Breen Holdings

Bate Bay ROAD

Other Industry

Regulation under CLM Act not required

-34.03861737

151.1614114

CROWS NEST

Caltex Service Station

111-121 Falcon STREET

Service Station

Regulation under CLM Act not required

-33.82868236

151.2060317

CROYDON

Caltex Service Station

404-410 Liverpool ROAD

Service Station

Regulation under CLM Act not required

-33.88853994

151.115879

CROYDON

BP Ashfield

584 Parramatta ROAD

Service Station

Regulation under CLM Act not required

-33.87399409

151.1267296

CROYDON PARK

Mobil Service Station

334 Georges River ROAD

Service Station

Regulation under CLM Act not required

-33.89771626

151.0999194

CULCAIRN

Caltex Service Station

2883 Olympic HIGHWAY

Service Station

Regulation under CLM Act not required

-35.67441635

147.0356845

CULLEN BULLEN

Baal Bone Colliery

Castlereagh HIGHWAY

Other Industry

Regulation under CLM Act not required

-33.27193875

150.0587194

List current as at 8 March 2022

35 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

CUNDLETOWN

Caltex Service Station (1 Manning River Drive)

Old Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-31.89329598

152.5068225

CURL CURL

John Fisher Park

Corner Harbord and Abbott ROADS

Landfill

Regulation under CLM Act not required

-33.76622613

151.2860705

DACEYVILLE

Astrolabe Park

Cook AVENUE

Landfill

Regulation under CLM Act not required

-33.92963704

151.221773

DAPTO

7-Eleven Dapto

125 Princes HIGHWAY

Service Station

Under assessment

-34.4983106

150.7912911

DAPTO

RailCorp Dapto

(Rear of property) 12-14 Hamilton STREET Other Industry

Regulation under CLM Act not required

-34.50045405

150.787353

DAPTO

Nicheinvest Pty Ltd (Former service station)

133-139 Lakelands DRIVE

Service Station

Regulation under CLM Act not required

-34.503453

150.80323

DARLINGHURST

Proposed Retail Unit

139-155 Palmer STREET

Unclassified

Regulation under CLM Act not required

-33.87504688

151.2168106

DARLINGHURST

Cross City Tunnel

Riley Street and William STREET

Service Station

Contamination was addressed via the planning process (EP&A Act)

-33.87424636

151.2158305

DARLINGHURST

18-28 Neild Avenue, Darlinghurst

18-28 Neild AVENUE

Landfill

Regulation under CLM Act not required

-33.87876581

151.2276546

DEE WHY

United Dee Why

148 Pacific Parade STREET

Service Station

Contamination currently regulated under CLM Act

-33.75569536

151.295963

DEE WHY

United Dee Why Pittwater

625 Pittwater (Cnr Mooramba Road) ROAD

Service Station

Under assessment

-33.7549455

151.2828442

DEE WHY

Caltex Service Station

793-797 Pittwater ROAD

Service Station

Regulation under CLM Act not required

-33.74566596

151.2920719

DEE WHY

Dee Why Town Centre

Pittwater ROAD

Other Industry

Regulation under CLM Act not required

-33.753169

151.2875805

DEE WHY

Roche Products Dee Why Facility

Inman ROAD

Other Industry

Contamination currently regulated under CLM Act

-33.73893118

151.2870389

DENHAM COURT

Denham Court Caravan Park and Service Station

505 Campbelltown ROAD

Service Station

Contamination currently regulated under CLM Act

-33.98208395

150.8459471

List current as at 8 March 2022

36 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

DENILIQUIN

Shell Coles Express Service Station

336 Victoria STREET

Service Station

Contamination formerly regulated under the CLM Act

-35.52373613

144.9807345

DENILIQUIN

Former Deniliquin Gasworks

365, 369 and 329-331 George and 380 and 386 Charlotte STREET

Gasworks

Under assessment

-35.52670898

144.9634996

DENILIQUIN

Landmark Fertiliser Storage Facility

99-101 Davidson STREET

Chemical Industry

Regulation under CLM Act not required

-35.52534735

144.975142

DENILIQUIN

Former Deniliquin Caltex Depot

116-118 Hardinge (Cnr Wood St) STREET

Service Station

Regulation under CLM Act not required

-35.53196985

144.9544597

DENILIQUIN

BP Depot (Reliance Petroleum)

125 - 127 Hardinge STREET

Service Station

Regulation under CLM Act not required

-35.53222124

144.9517397

DENILIQUIN

Former Shell Depot

143-147 Napier STREET

Other Petroleum

Regulation under CLM Act not required

-35.5342355

144.953169

DENILIQUIN

Previous Council depot site

392 - 394 Hay ROAD

Unclassified

Under assessment

-35.518857

144.977947

DENMAN

Former Industrial Site

10 Fontana WAY

Metal Industry

Regulation under CLM Act not required

-32.37945456

150.6868239

DENMAN

Former Industrial Site

9 Fontana WAY

Metal Industry

Regulation under CLM Act not required

-32.37911159

150.6869866

DORA CREEK

Former Service Station

4 Doree PLACE

Service Station

Regulation under CLM Act not required

-33.08452746

151.502415

DOUBLE BAY

64 Suttie Road, Double Bay NSW 2028

64 Suttie ROAD

Other Industry

Regulation under CLM Act not required

-33.885034

151.247311

DOYALSON

Part Lot 3 DP 259306

Off David STREET

Other Industry

Regulation under CLM Act not required

-33.20436131

151.5232558

DOYALSON

Munmorah Power Station

(Central Coast Highway) Scenic DRIVE

Other Industry

Under assessment

-33.20678347

151.540795

DOYALSON

Mannering Colliery (formerly Wyee)

Rutleys ROAD

Other Industry

Regulation under CLM Act not required

-33.17179576

151.5419248

DOYALSON NORTH

Caltex Service Station

235 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.18501024

151.5526114

List current as at 8 March 2022

37 of 129


Suburb

SiteName

DOYALSON NORTH

Shell Coles Express Service Station

DRUMMOYNE

Address

ManagementClass

Latitude

Longitude

Service Station

Regulation under CLM Act not required

-33.18636608

151.5482399

Coles Express Service Station Drummoyne (Eastbound) 36-46 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.85576628

151.1593519

DRUMMOYNE

Former Dry Cleaners

Chemical Industry

Regulation under CLM Act not required

-33.8507152

151.1537113

DRUMMOYNE

Coles Express Service Station Drummoyne South (Westbound) 39-45 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.85606575

151.1589061

DRUMMOYNE

Caltex Service Station

191-195 Lyons ROAD

Service Station

Regulation under CLM Act not required

-33.85699216

151.1460356

DUBBO

BP Reliance Petroleum Service Station (Former Mobil Depot)

107 Erskine STREET

Other Petroleum

Regulation under CLM Act not required

-32.24441287

148.6111704

DUBBO

Dubbo Police Station

143 Brisbane STREET

Other Petroleum

Regulation under CLM Act not required

-32.24652288

148.6034702

DUBBO

Shell Coles Express Service Station

131-133 Cobra STREET

Service Station

Regulation under CLM Act not required

-32.25511317

148.6126147

DUBBO

Shell Coles Express Service Station

45-49 Whylandra STREET

Service Station

Regulation under CLM Act not required

-32.2474598

148.5932769

DUBBO

Former Mobil depot

40-44 Morgan STREET

Other Petroleum

Regulation under CLM Act not required

-32.23912277

148.6182711

DUBBO

Caltex Service Station, Dubbo

60 Windsor PARADE

Service Station

Regulation under CLM Act not required

-32.25459322

148.6318

DUBBO

BP-Branded Service Station Dubbo West

51-63 Whylandra STREET

Service Station

Regulation under CLM Act not required

-32.24827657

148.5927084

DUBBO

Lowes Petroleum (BP-Branded) Depot, Dubbo

105 Erskine STREET

Service Station

Regulation under CLM Act not required

-32.24423247

148.6101676

DUBBO

Inland Petroleum (Former Shell) Depot

109 Erskine STREET

Other Petroleum

Regulation under CLM Act not required

-32.24470512

148.6124108

DUBBO

Former Caltex Depot

Phillip (corner Fitzroy) STREET

Service Station

Regulation under CLM Act not required

-32.24534863

148.6150144

List current as at 8 March 2022

260-270 Pacific HIGHWAY

ContaminationActivityType

225 Victoria ROAD

38 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

DUBBO

Caltex Service Station

119 Bourke STREET

Service Station

Regulation under CLM Act not required

-32.24336464

148.6091931

DUBBO

Former Ambulance Station

165 Brisbane STREET

Other Petroleum

Contamination formerly regulated under the CLM Act

-32.24850755

148.6031749

DUBBO

United (former Volume Plus) Service Station

219-223 Cobra STREET

Service Station

Regulation under CLM Act not required

-32.2565155

148.6228586

DUBBO

Ampol Service Station, Dubbo

Cnr Brisbane Street and Cobra STREET

Service Station

Contamination currently regulated under CLM Act

-32.25322183

148.603164

DULWICH HILL

Former Tyre Recapping

115-117 Constitution ROAD

Other Industry

Regulation under CLM Act not required

-33.90300876

151.1387724

DULWICH HILL

Denison Road Playground

194 Denison ROAD

Landfill

Regulation under CLM Act not required

-33.90121956

151.1404637

DUNEDOO

Former Shell Depot Dunedoo

Cnr Bolaro and Redbank STREET

Other Petroleum

Regulation under CLM Act not required

-32.01565761

149.3922418

DUNGOG

Lot 54 Common Rd

54 Common ROAD

Unclassified

Regulation under CLM Act not required

-32.39490989

151.739821

DUNGOG

Former HWC Maintenance Depot for Civil Engineering Works 86 Abelard STREET

Other Industry

Regulation under CLM Act not required

-32.40429396

151.7514073

DUNMORE

Equestrian Centre

71 Fig Hill LANE

Unclassified

Regulation under CLM Act not required

-34.62313393

150.8421544

DURAL

Caltex Dural Service Station

917-923 Old Northern ROAD

Service Station

Regulation under CLM Act not required

-33.68312075

151.0287519

DURAL

BP Dural Service Station

580 Old Northern ROAD

Service Station

Regulation under CLM Act not required

-33.69569985

151.0283357

DURAL

Caltex Service Station

530 Old Northern ROAD

Service Station

Regulation under CLM Act not required

-33.69348472

151.0202716

DURAL

Woolworths Service Station

532 Old Northern ROAD

Service Station

Regulation under CLM Act not required

-33.69348472

151.0202716

DURAL

21 John Radley Avenue, Dural

21 John Radley AVENUE

Landfill

Under assessment

-33.717158

151.0332

List current as at 8 March 2022

39 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

DURI

Duri Store

13 Railway AVENUE

Service Station

Contamination currently regulated under CLM Act

-31.21710021

150.8183675

EAGLE VALE

BP Service Station

Corner Eagle Vale Drive and Gould ROAD

Service Station

Regulation under CLM Act not required

-34.03128043

150.816363

EARLWOOD

RTA Land

3 Jackson PLACE

Unclassified

Contamination currently regulated under CLM Act

-33.92724512

151.1433382

EARLWOOD

Wolli Creek Aqueduct

Unwin STREET

Unclassified

Regulation under CLM Act not required

-33.92788788

151.1480807

EARLWOOD

2, 4 & 6 Unwin Street Earlwood

2, 4 & 6 Unwin STREET

Landfill

Regulation under CLM Act not required

-33.92683761

151.149505

EAST BALLINA

Caltex East Ballina Service Station

34 Links AVENUE

Service Station

Regulation under CLM Act not required

-28.85009113

153.5829246

EAST GOSFORD

Presbyterian Aged Care Facility

8-18 Enid CRESCENT

Landfill

Regulation under CLM Act not required

-33.4376675

151.3577947

EAST GOSFORD

Mobil Service Station

44 Victoria STREET

Service Station

Contamination formerly regulated under the CLM Act

-33.43804781

151.353303

EAST GOSFORD

Hylton Moore Park

Althrop STREET

Landfill

Contamination currently regulated under CLM Act

-33.4352203

151.3601193

EAST MAITLAND

United Service Station East Maitland

164 (also known as 250) Newcastle STREET

Service Station

Regulation under CLM Act not required

-32.75245246

151.5869136

EAST MAITLAND

Woolworths Caltex Green Hills

14 Mitchell DRIVE

Service Station

Regulation under CLM Act not required

-32.76182386

151.5927863

EAST MAITLAND

Former Gasworks Site

Corner Melbourne Street and Brisbane STREET

Gasworks

Regulation under CLM Act not required

-32.74939199

151.5788783

EAST MAITLAND

Caltex East Maitland Service Station

Newcastle Road, Corner William STREET

Service Station

Regulation under CLM Act not required

-32.74883712

151.5829296

EAST TAMWORTH

Caltex Service Station

350-362 Armidale ROAD

Service Station

Regulation under CLM Act not required

-31.11401974

150.9613327

EASTERN CREEK

Caltex Service Station

M4 (Eastbound) MOTORWAY

Service Station

Regulation under CLM Act not required

-33.801607

150.8857989

List current as at 8 March 2022

40 of 129


Suburb

SiteName

EASTERN CREEK

Caltex Service Station M4 Motorway Westbound

EASTERN CREEK

Address

ManagementClass

Latitude

Longitude

Service Station

Regulation under CLM Act not required

-33.80255701

150.8829211

Fulton Hogan Industries (formerly Pioneer Road Services) Honeycomb DRIVE

Other Industry

Regulation under CLM Act not required

-33.80231274

150.8288299

EASTGARDENS

130-150 Bunnerong Road Eastgardens

Other Industry

Regulation under CLM Act not required

-33.94230414

151.2248138

EASTLAKES

Former Shell Rosebery service station and adjacent land 275-279 Gardeners ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.92471289

151.2100772

EASTLAKES

Eastlakes Reserve

Evans AVENUE

Service Station

Contamination formerly regulated under the CLM Act

-33.92497291

151.2102725

EASTLAKES

Budget Petroleum Eastlakes

102 Maloney STREET

Service Station

Contamination formerly regulated under the CLM Act

-33.93120382

151.2054267

EASTLAKES

73 Gardeners Road

73 Gardeners ROAD

Unclassified

Regulation under CLM Act not required

-33.92541594

151.2182856

EASTWOOD

Former Mobil Service Station Eastwood

3-5 Trelawney (Cnr Rutledge St) STREET

Service Station

Regulation under CLM Act not required

-33.79273381

151.079584

EDEN

Caltex Service Station

159 Imlay STREET

Service Station

Regulation under CLM Act not required

-37.06324099

149.9044022

EDEN

Former Caltex Eden Depot

80-82 Imlay STREET

Service Station

Contamination currently regulated under CLM Act

-37.0570984

149.9038538

EDENSOR PARK

Caltex Bonnyrigg Service Station, Edensor Park 549 Elizabeth DRIVE

Service Station

Regulation under CLM Act not required

-33.88840816

150.8822609

EDENSOR PARK

7-Eleven (former Mobil) Service Station

615-621 Cowpasture Road, corner Elizabeth DRIVE

Service Station

Regulation under CLM Act not required

-33.88326139

150.865591

EDGECLIFF

BP-branded (former Coles Express) Service Station

73-85A New South Head ROAD

Service Station

Regulation under CLM Act not required

-33.8769602

151.2311617

EDGEWORTH

Caltex Service Station

662 Main ROAD

Service Station

Regulation under CLM Act not required

-32.92566329

151.6278888

EDGEWORTH

Caltex-Woolworths Branded Service Station Edgeworth

738-742 Main ROAD

Service Station

Regulation under CLM Act not required

-32.92455492

151.6202897

List current as at 8 March 2022

M4 (Westbound) MOTORWAY

ContaminationActivityType

130 - 150 Bunnerong ROAD

41 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

EMERALD BEACH

Shell Coles Express Woolgoolga Service Station

1850 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-30.16450856

153.1826673

EMERTON

7-Eleven Emerton

135-137 Popondetta ROAD

Service Station

Regulation under CLM Act not required

-33.74463908

150.8102251

EMPIRE BAY

Empire Bay Marina

16B Sorrento ROAD

Other Industry

Regulation being finalised

-33.492429

151.3631

EMU HEIGHTS

7-Eleven Service Station

126 Old Bathurst ROAD

Service Station

Regulation under CLM Act not required

-33.74299098

150.6547098

EMU HEIGHTS

Woolworths Service Station

132 Old Bathurst ROAD

Service Station

Regulation under CLM Act not required

-33.7429739

150.6559655

EMU PLAINS

Woolworths Service Station

283 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.75371349

150.6530165

ENGADINE

Former Caltex Service Station

995 Old Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.06413459

151.0155734

ENGADINE

BP Service Station

1234 Princes HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-34.07735416

151.01121

ENGADINE

BP Branded Service Station

963 Old Princes HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-34.06428454

151.0167121

EPPING

7-Eleven (former Mobil) Service Station

246 Beecroft ROAD

Service Station

Regulation under CLM Act not required

-33.77073552

151.080581

ERINA

Coles Express Service Station Erina

211 The Entrance ROAD

Service Station

Regulation under CLM Act not required

-33.43547804

151.3850522

ERINA

7-Eleven Erina

214 The Entrance ROAD

Service Station

Regulation under CLM Act not required

-33.43494257

151.3879511

ERINA

7-Eleven Service Station

96 The Entrance ROAD

Service Station

Regulation under CLM Act not required

-33.43786868

151.3729331

ERINA

Jaycar Electronics Store

1 Aston ROAD

Other Petroleum

Contamination currently regulated under CLM Act

-33.434878

151.3845431

ERINA

Caltex Service Station

155 The Entrance ROAD

Service Station

Regulation under CLM Act not required

-33.43824871

151.3801096

List current as at 8 March 2022

42 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

ERMINGTON

Blue Star Ermington

700 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.80859566

151.0660133

ERMINGTON

Caltex Service Station

562 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.81392814

151.0547543

ERSKINE PARK

Western Sydney Service Centre

25-55 Templar ROAD

Other Industry

Regulation under CLM Act not required

-33.81897822

150.7937394

ERSKINEVILLE

Redevelopment Site (Former Industrial Park) Erskineville

36/1A Coulson STREET

Other Industry

Regulation under CLM Act not required

-33.90325501

151.1855668

ERSKINEVILLE

Department of Housing

52 John STREET

Other Industry

Regulation under CLM Act not required

-33.8982925

151.1840284

ERSKINEVILLE

RailCorp land

Coulson STREET

Other Industry

Regulation under CLM Act not required

-33.90483899

151.1838804

ERSKINEVILLE

Lot 4/1A Coulson Street

Coulson STREET

Other Industry

Regulation under CLM Act not required

-33.90316549

151.1867963

ERSKINEVILLE

Area B - Public Domain / The Roadway

1A Coulson STREET

Other Petroleum

Regulation under CLM Act not required

-33.90499999

151.1873028

EUABALONG WEST

BP Euabalong West Depot (Reliance Petroleum)

12 Illewong STREET

Other Petroleum

Regulation under CLM Act not required

-33.05720426

146.3946386

EVANS HEAD

Evans Head Aerodrome

Memorial Airport DRIVE

Other Industry

Regulation under CLM Act not required

-29.10389976

153.4216791

EVANS HEAD

Bundjalung National Park

The Gap ROAD

Unclassified

Regulation under CLM Act not required

-29.24433977

153.3626472

EVANS HEAD

Evans Head Residential subdivision

Bounded by Currajong, Woodburn, Carrabeen Streets and Tuckeroo CRESCENT

Unclassified

Regulation under CLM Act not required

-29.1080969

153.4243577

EVELEIGH

Macdonaldtown Triangle

Burren STREET

Gasworks

Contamination being managed via the planning process (EP&A Act)

-33.89803492

151.186059

EVELEIGH

Australian Technology Park

Henderson ROAD

Other Industry

Regulation under CLM Act not required

-33.89634136

151.1944915

FAIRFIELD

Endeavour Energy Fairfield Zone Substation

22 Hedges STREET

Other Industry

Regulation under CLM Act not required

-33.86133019

150.9555899

List current as at 8 March 2022

43 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

FAIRFIELD EAST

Speedway-Branded Service Station Fairfield

251 The Horsley DRIVE

Service Station

Regulation under CLM Act not required

-33.8711661

150.9630077

FAIRFIELD HEIGHTS

7-Eleven Fairfield Heights

234 Hamilton (Cnr The Boulevarde) ROAD Service Station

Regulation under CLM Act not required

-33.87208474

150.9373134

FAIRY MEADOW

Woolworths Petrol Service Station

47 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.39399705

150.8925369

FAIRY MEADOW

Caltex Fuel Depot and adjoining land

46 Montague STREET

Service Station

Contamination formerly regulated under the CLM Act

-34.40050499

150.8953125

FAIRY MEADOW

Deynal (Seeman)

51-59 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.39437085

150.8924666

FARLEY

Farley Wastewater Treatment Works

Owlpen LANE

Other Industry

Regulation under CLM Act not required

-32.74431314

151.5194217

FASSIFERN

Newstan Colliery

Fassifern ROAD

Other Industry

Regulation under CLM Act not required

-32.97942521

151.5660046

FASSIFERN

Former Arsenic Smelter

Fassifern ROAD

Other Industry

Regulation under CLM Act not required

-32.99649819

151.5618283

FEDERAL

Federal General Store

3-6 Federal DRIVE

Service Station

Contamination formerly regulated under the CLM Act

-28.65190728

153.4552976

FENNELL BAY

Fennell Bay Public School

2 Bay ROAD

Unclassified

Under assessment

-32.991544

151.601637

FERN BAY

Former service station

37 Fullerton (1006 Nelson Bay Road) STREET

Service Station

Regulation under CLM Act not required

-32.87245004

151.7939904

FIVE DOCK

7-Eleven Five Dock Service Station

231-235 Great North ROAD

Service Station

Regulation under CLM Act not required

-33.86488376

151.130002

FIVE DOCK

Caltex Five Dock Service Station

47 Ramsay Road, corner Fairlight STREET

Service Station

Regulation under CLM Act not required

-33.87002804

151.1301835

FORBES

BP (Former Mobil) Depot Forbes

3-15 Union STREET

Other Petroleum

Regulation under CLM Act not required

-33.37751977

148.0101422

FORBES

Former Gasworks

24-26 Union STREET

Gasworks

Contamination currently regulated under CLM Act

-33.37752036

148.0090064

List current as at 8 March 2022

44 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

FORBES

Woolworths (Former Save on Fuel) Service Station

26 Dowling STREET

Service Station

Regulation under CLM Act not required

-33.38148764

148.0109845

FORBES

BP Service Station Forbes

29 Dowling STREET

Service Station

Regulation under CLM Act not required

-33.38121776

148.0100351

FORBES

Former Shell Depot

Stephen STREET

Other Petroleum

Regulation under CLM Act not required

-33.37704755

148.0103001

FORBES

Caltex Service Station Forbes

Parkes ROAD

Service Station

Regulation under CLM Act not required

-33.36333714

148.0223727

FORESTVILLE

BP Service Station, Forestville

632 Warringah ROAD

Service Station

Contamination currently regulated under CLM Act

-33.75997969

151.2142944

FORESTVILLE

Shell Service Station

667 Warringah ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.76035336

151.2184929

FORRESTERS BEACH

Caltex Service Station

The Entrance Rd Cnr Bellevue ROAD

Service Station

Regulation under CLM Act not required

-33.40057818

151.4687631

FORSTER

Caltex Service Station

16-18 Lake STREET

Service Station

Regulation under CLM Act not required

-32.18306967

152.5162492

FORSTER

Shell (Kneebone's) Service Station

2-6 The Lakes WAY

Service Station

Regulation under CLM Act not required

-32.1946108

152.5145662

FORSTER

Enhance (Former Mobil) Service Station

86-88 Macintosh STREET

Service Station

Regulation under CLM Act not required

-32.19079468

152.5154847

FREDERICKTON

Former Service station

2-4 Great North ROAD

Service Station

Regulation under CLM Act not required

-31.03513998

152.8794105

FRENCHS FOREST

Former BP Service Station

Russell AVENUE

Service Station

Regulation under CLM Act not required

-33.75018093

151.2245005

FRENCHS FOREST

Former 7-Eleven / Mobil Beacon Hill Service Station, Frenchs Forest

312 Warringah ROAD

Service Station

Regulation under CLM Act not required

-33.75129647

151.2469656

FRESHWATER

Prime Service Station Freshwater

117 Harbord ROAD

Service Station

Regulation under CLM Act not required

-33.77286748

151.2794354

FRESHWATER

Former Dry Cleaners

121 Wyndora AVENUE

Other Industry

Regulation under CLM Act not required

-33.77425321

151.2821553

List current as at 8 March 2022

45 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

GATESHEAD

7-Eleven Gateshead

13-15 Pacific HIGHWAY

Service Station

Under assessment

GEORGETOWN

Former Caltex Service Station

4 Georgetown ROAD

Service Station

GERRINGONG

Gerringong Cooperative

18 Belinda STREET

GILGANDRA

United (Former Mobil) Service Station

GILGANDRA

Latitude

Longitude

-32.987453

151.691898

Regulation under CLM Act not required

-32.91121105

151.7319693

Other Petroleum

Regulation under CLM Act not required

-34.74518835

150.8181054

13 Castlereagh STREET

Service Station

Regulation under CLM Act not required

-31.71715641

148.6581574

Former Mobil Depot

2 Federation STREET

Other Petroleum

Regulation under CLM Act not required

-31.70937362

148.6522102

GILGANDRA

Former Mobil Depot

20 Federation STREET

Other Petroleum

Regulation under CLM Act not required

-31.70771744

148.6514198

GILGANDRA

Caltex Service Station Gilgandra

6425 Newell HIGHWAY

Service Station

Regulation under CLM Act not required

-31.72545524

148.65281

GILLENBAH

Caltex (Former Mobil) Narrandera Service 16321 - 16335 Newell HIGHWAY Station

Service Station

Regulation under CLM Act not required

-34.76124219

146.5398604

GIRRAWEEN

Industrial Galvanizers Girraween

20-22 Amax AVENUE

Metal Industry

Regulation being finalised

-33.80500693

150.9396743

GIRRAWEEN

Caltex Pendle Hill Service Station Girraween

602 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.80827518

150.9421511

GLADESVILLE

Caltex Service Station

287-295 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.8285374

151.1268639

GLADESVILLE

Road Reserve

Pittwater ROAD

Other Industry

Regulation under CLM Act not required

-33.81603924

151.1355085

GLADESVILLE

Caltex Service Station

116 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.83575319

151.1277863

GLADESVILLE

Glade View Business Park

436-484 Victoria ROAD

Other Industry

Contamination currently regulated under CLM Act

-33.82382382

151.1223941

GLADSTONE

Barbers Auto Port

52-53 Barnard STREET

Service Station

Under assessment

151.691898

152.948223

List current as at 8 March 2022

46 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

GLEBE

The Hill and Jubilee Embankment

12 Maxwell ROAD

Other Industry

Regulation under CLM Act not required

-33.87573032

151.1776027

GLEN INNES

Ambulance Station

106 Bourke STREET

Unclassified

Regulation under CLM Act not required

-29.73805854

151.7313138

GLEN INNES

Telstra Depot Glen Innes

126 Lambeth STREET

Unclassified

Regulation under CLM Act not required

-29.73565341

151.7278271

GLEN INNES

Caltex Glen Innes Service Station

Meade Street, corner Church STREET

Service Station

Regulation under CLM Act not required

-29.73699014

151.7379335

GLEN INNES

Former Shell Depot

Lambeth STREET

Other Petroleum

Regulation under CLM Act not required

-29.7376309

151.7276309

GLEN INNES

Former Caltex Depot, Glen Innes

Lot 1 DP785636 Lambeth STREET

Other Petroleum

Regulation under CLM Act not required

-29.73525485

151.7279167

GLEN INNES

Council-owned Laneway

Lot 2 Lang STREET

Gasworks

Regulation under CLM Act not required

-29.74385432

151.7323049

GLEN INNES

Caltex Service Station

Cnr Taylor Street & Church STREET

Service Station

Regulation under CLM Act not required

-29.73289036

151.739653

GLEN INNES

Caltex Glen Innes Paddock

9979 New England HIGHWAY

Service Station

Regulation under CLM Act not required

-29.75608853

151.7344106

GLENBROOK

Caltex Service Station Glenbrook

78 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.76545234

150.6215447

GLENDALE

Coles Express Glendale

593 Main ROAD

Service Station

Regulation under CLM Act not required

-32.92709242

151.637946

GLENDALE

Settlement Pond

65 Glendale DRIVE

Unclassified

Regulation under CLM Act not required

-32.93411399

151.6483695

GLENDALE

Former Service Station

334-342 Lake ROAD

Unclassified

Regulation under CLM Act not required

-32.92775076

151.6433463

GLENDALE

Woolworths Service Station

Stockland DRIVE

Service Station

Regulation under CLM Act not required

-32.93250548

151.6404097

GLENDENNING

7-Eleven Plumpton Service Station Glendenning

1 Dublin Street, corner Richmond ROAD

Service Station

Regulation under CLM Act not required

-33.73988232

150.8603323

List current as at 8 March 2022

47 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

GLENORIE

Caltex Glenorie Service Station

912 Old Northern ROAD

Service Station

Regulation under CLM Act not required

-33.60550946

151.0126731

GLENTHORNE

Caltex Taree Service Station

Manning River DRIVE

Service Station

Regulation under CLM Act not required

-31.94415251

152.4703511

GLOUCESTER

Caltex Service Station

141 Church STREET

Service Station

Regulation under CLM Act not required

-32.01222514

151.9579521

GOOLMANGAR

Goolmangar General Store

851 Nimbin ROAD

Service Station

Regulation under CLM Act not required

-28.74694441

153.225401

GOONELLABAH

Former Invercauld Road Cattle Dip

161 Invercauld ROAD

Cattle Dip

Contamination formerly regulated under the CLM Act

-28.83098216

153.3097337

GOSFORD

United (former Mobil) Depot

Corner Merinee Road and Bowen CRESCENT

Other Petroleum

Regulation under CLM Act not required

-33.41523225

151.3257069

GOULBURN

Former Goulburn Gasworks

1 Blackshaw ROAD

Gasworks

Ongoing maintenance required to manage residual contamination (CLM Act)

-34.75313166

149.725032

GOULBURN

Goulburn Tannery

13 Gibson STREET

Other Industry

Regulation under CLM Act not required

-34.73756525

149.72059

GOULBURN

Caltex Depot

13 Sloane STREET

Other Petroleum

Regulation under CLM Act not required

-34.77423152

149.7088626

GOULBURN

Metro Goulburn Depot

23 Braidwood ROAD

Other Petroleum

Regulation under CLM Act not required

-34.76217302

149.7170897

GOULBURN

Caltex Service Station

72-74 Clinton STREET

Service Station

Regulation under CLM Act not required

-34.75728157

149.7135824

GOULBURN

Caltex Service Station

68 Goldsmith STREET

Service Station

Regulation under CLM Act not required

-34.75054432

149.7192098

GOULBURN

Former Shell Autoport Service Station

Corner Bruce Street and Lagoon STREET

Service Station

Regulation under CLM Act not required

-34.74807885

149.7266246

GOULBURN

Coles Express Service Station

90 Cowper (Corner Clinton Street) STREET Service Station

Regulation under CLM Act not required

-34.75566648

149.7107831

GOULBURN

Mobil Service Station

129 Lagoon STREET

Contamination formerly regulated under the CLM Act

-34.74618793

149.7330484

List current as at 8 March 2022

Service Station

48 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

GOULBURN

Caltex Service Station

315 Auburn, corner Bradley STREET

Service Station

Regulation under CLM Act not required

-34.74942293

149.7232692

GOULBURN

Former Mobil Service Station Goulburn

422-426 Auburn STREET

Service Station

Regulation under CLM Act not required

-34.74869879

149.7229392

GOULBURN

Goulburn Roundhouse

12 Braidwood ROAD

Other Industry

Under assessment

151.691898

152.948223

GOULBURN

Goulburn JS Hollingworth & Wheat Siding Yards Goulburn STREET

Other Industry

Under assessment

-35.084423

149.637919

GOULBURN

Broken Hill Kanandah Road Refuelling Depot

Kanandah ROAD

Service Station

Under assessment

-31.985103

141.428139

GRAFTON

Former General Store and Service Station Grafton 161 Turf STREET

Service Station

Regulation under CLM Act not required

-29.67412811

152.9336609

GRAFTON

Lowes Petroleum (BP-Branded) Depot, Grafton

13 Orara STREET

Other Petroleum

Regulation under CLM Act not required

-29.67016421

152.918161

GRAFTON

Former Shell Depot

2 Milton STREET

Other Petroleum

Regulation under CLM Act not required

-29.67723019

152.9205374

GRAFTON

Grafton Works Depot

26-28 Bruce STREET

Other Petroleum

Regulation under CLM Act not required

-29.67975507

152.9249357

GRAFTON

Former BP Service Station (Reliance Petroleum)

202 Queen STREET

Service Station

Regulation under CLM Act not required

-29.67645469

152.9423977

GRAFTON

Woolworths Petrol

75 - 77 Fitzroy Street Cnr of Duke STREET Service Station

Regulation under CLM Act not required

-29.69221713

152.9343562

GRAFTON

Caltex Service Station

Corner Villiers St and Fitzroy STREET

Service Station

Regulation under CLM Act not required

-29.69296308

152.9366431

GRAFTON

BP Service Station (Reliance Petroleum)

14 Villiers (Cnr Fitzroy) STREET

Service Station

Regulation under CLM Act not required

-29.69345456

152.9373123

GRAFTON

Former Mobil Depot Grafton

2-16 Bruce STREET

Other Petroleum

Regulation under CLM Act not required

-29.68093591

152.9231289

GRAFTON

Caltex Service Station

179 Prince STREET

Service Station

Regulation under CLM Act not required

-29.68600117

152.9371093

List current as at 8 March 2022

49 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

GRANVILLE

Caltex Service Station

144 Parramatta ROAD

Service Station

Regulation under CLM Act not required

-33.83039605

151.0109216

GRANVILLE

Australand

15-17 Berry STREET

Other Industry

Regulation under CLM Act not required

-33.83600073

151.0211988

GRANVILLE

Woolworths Service Station Granville

158 Clyde STREET

Service Station

Regulation under CLM Act not required

-33.84623338

151.0124885

GRANVILLE

Commercial Property

2B Factory STREET

Other Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.84173556

151.0165687

GRANVILLE

Old Granville Depot

23 Elizabeth STREET

Unclassified

Regulation under CLM Act not required

-33.83765925

151.008528

GRANVILLE

7-Eleven Service Station

154-160 Parramatta ROAD

Service Station

Regulation under CLM Act not required

-33.83022685

151.0101322

GRANVILLE

A'Becketts Creek

Albert STREET

Unclassified

Contamination currently regulated under POEO Act

-33.82735776

151.0112255

GREEN POINT

7-Eleven Green Point

388-390 Avoca DRIVE

Service Station

Under assessment

-33.4623258

151.3627093

GREENACRE

Former Plating Works

12 Claremont STREET

Unclassified

Regulation under CLM Act not required

-33.89992254

151.0386128

GREENACRE

7-Eleven (former Mobil) Service Station

301-305 Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-33.90524488

151.0419971

GREENACRE

Caltex Service Station

87 - 91 Roberts ROAD

Service Station

Regulation under CLM Act not required

-33.90461089

151.0648581

GREENACRE

Coles Greenacre

13-19 Boronia ROAD

Other Industry

Regulation under CLM Act not required

-33.9061123

151.0561759

GREENWICH

Gore Creek Reserve - Drainage Line

St Vincents ROAD

Other Industry

Regulation under CLM Act not required

-33.82888693

151.1819101

GRENFELL

Former SRA Fuel Depot

Grafton STREET

Other Petroleum

Regulation under CLM Act not required

-33.89351237

148.1560188

GRENFELL

Grenfell Gasworks

Corner Gooloogong Road & Bourke STREET

Gasworks

Regulation under CLM Act not required

-33.89006016

148.1615443

List current as at 8 March 2022

50 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

GRETA

Coles Express Greta

122 New England HIGHWAY

Service Station

Regulation under CLM Act not required

-32.67656357

151.3872818

GRETA

redevelopment site

112-114 High STREET

Other Industry

Regulation under CLM Act not required

-32.67706709

151.3876682

GRETA

Former landfill

Hollingshed ROAD

Landfill

Regulation under CLM Act not required

-32.66705287

151.3923474

GREYSTANES

Metro Branded (former Mobil) Service Station

73 Ettalong ROAD

Service Station

Regulation under CLM Act not required

-33.81822648

150.9513946

GRIFFITH

Liberty Depot (former Shell CVRO) Griffith 6-10 Mackay AVENUE

Other Petroleum

Regulation under CLM Act not required

-34.2910045

146.063824

GRIFFITH

Former Murrumbidgee Irrigation Depot

55-77 Banna AVENUE

Other Industry

Regulation under CLM Act not required

-34.28858242

146.0567509

GRIFFITH

Mobil Depot - Griffith Airport

Off Rememberance DRIVE

Other Petroleum

Regulation under CLM Act not required

-34.25618872

146.0620449

GRIFFITH

Former Ampol Depot

32-34 Mackay AVENUE

Other Petroleum

Regulation under CLM Act not required

-34.2933331

146.0679503

GRIFFITH

Caltex Service Station and Depot

2-4 Mackay AVENUE

Service Station

Regulation under CLM Act not required

-34.2908766

146.0630815

GRIFFITH

Former Landmark Fertiliser Storage Facility

2-8 Jensen ROAD

Chemical Industry

Regulation under CLM Act not required

-34.29365599

146.0536413

GRIFFITH

Belford Petroleum (former Mobil) Depot

30 Banna AVENUE

Service Station

Regulation under CLM Act not required

-34.29042827

146.0595497

GRIFFITH

Former BP Service Station (Reliance Petroleum)

81 Banna AVENUE

Service Station

Regulation under CLM Act not required

-34.28851251

146.0540815

GUILDFORD

7-Eleven Service Station Guildford West

176 Fowler ROAD

Service Station

Regulation under CLM Act not required

-33.85149493

150.9722491

GULGONG

Lowes Petroleum (former BP) Depot Gulgong

6 Railway STREET

Other Petroleum

Regulation under CLM Act not required

-32.35950625

149.5461499

GULGONG

The Oval Site

Queen STREET

Unclassified

Regulation under CLM Act not required

-32.36169815

149.531075

List current as at 8 March 2022

51 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

GULMARRAD

BP Service Station Maclean

3976 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-29.48537407

153.2004311

GUMLY GUMLY

Caltex Service Station

3723 Sturt HIGHWAY

Service Station

Regulation under CLM Act not required

-35.13590309

147.4424551

GUMLY GUMLY

Brick Kiln Reserve

Eunony Bridge ROAD

Landfill

Regulation under CLM Act not required

-35.12098411

147.4196309

GUNDAGAI

Former Mobil Depot

98 Mount STREET

Other Petroleum

Regulation under CLM Act not required

-35.08206783

148.096221

GUNNEDAH

Ampol Australia Petroleum Pty Ltd (previously Caltex Australia)

21 Abbott STREET

Service Station

Regulation under CLM Act not required

-30.98021001

150.2561856

GUNNEDAH

Former Shell Depot Gunnedah

85-89 Barber STREET

Other Petroleum

Regulation under CLM Act not required

-30.97949284

150.2507401

GUNNEDAH

Mobil Gunnedah Depot

16-24 Wentworth STREET

Other Petroleum

Regulation under CLM Act not required

-30.98428725

150.260609

GUNNEDAH

BP Depot Gunnedah

103 Mathias ROAD

Other Petroleum

Contamination currently regulated under CLM Act

-30.96665001

150.2326526

GUNNEDAH

BP Service Station

Corner Conadilly Street & Henry STREET

Service Station

Contamination formerly regulated under the CLM Act

-30.98116266

150.2583066

GUNNEDAH

Mobil Service Station

341 Conadilly STREET

Service Station

Contamination formerly regulated under the CLM Act

-30.9807394

150.2578428

GUNNEDAH

Property NSW Site

35-37 Abbott STREET

Other Petroleum

Regulation under CLM Act not required

-30.9789841

150.25737

GUNNEDAH

Former Telstra Line Depot

81 Barber STREET

Other Petroleum

Regulation under CLM Act not required

-30.97933809

150.2503121

GUNNEDAH

Adjacent to Service Station

Intersection of Henry Street and Conadilly STREET Service Station

Contamination formerly regulated under the CLM Act

-30.98072588

150.2582802

GUNNEDAH

Former Caltex Depot

61 Railway AVENUE

Other Petroleum

Contamination formerly regulated under the CLM Act

-30.97953242

150.2494457

GUNNING

Gunning Motors

56 Yass STREET

Service Station

Regulation under CLM Act not required

-34.78159326

149.2684791

List current as at 8 March 2022

52 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

GUYRA

Guyra Fourways Service Centre

87-89 Bradley STREET

Service Station

Regulation under CLM Act not required

-30.21728173

151.6722825

GUYRA

Caltex-branded Service Station

4352 New England HIGHWAY

Service Station

Regulation under CLM Act not required

-30.20601937

151.6757291

GUYRA

StateRail land leased to Incitec

Starr ROAD

Other Industry

Regulation under CLM Act not required

-30.23157011

151.6707135

GWANDALAN

Metro Petroleum Gwandalan (Formerly Gwandalan Auto Care)

47 Orana ROAD

Service Station

Regulation under CLM Act not required

-33.13632941

151.5813396

GWANDALAN

Former Gwandalan Landfill

Kanangra DRIVE

Landfill

Regulation under CLM Act not required

-33.17497722

151.5917107

GYMEA

7-Eleven (former Mobil) Gymea Service Station

110 Gymea Bay ROAD

Service Station

Regulation under CLM Act not required

-34.03745848

151.0848547

GYMEA

Coles Express Kirrawee

470 Princes (Cnr The Boulevarde) HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-34.02735302

151.0845079

GYMEA

Former Shell Service Station Gymea

Gymea Bay ROAD

Service Station

Regulation under CLM Act not required

-34.04129676

151.0841328

HABERFIELD

7-Eleven Haberfield

25-35 Parramatta ROAD

Service Station

Contamination currently regulated under CLM Act

-33.88794591

151.14287

HALEKULANI

Former Halekulani Landfill

Macleay DRIVE

Landfill

Regulation under CLM Act not required

-33.21446301

151.5527625

HAMILTON

SRA Land

10 Maitland ROAD

Unclassified

Regulation under CLM Act not required

-32.91994358

151.7512417

HAMILTON

Taxi Services

116 Tudor STREET

Service Station

Contamination formerly regulated under the CLM Act

-32.92351606

151.7454742

HAMILTON

Caltex Hamilton

59-63 Tudor STREET

Service Station

Regulation under CLM Act not required

-32.92498593

151.7509313

HAMILTON

Newcastle Toyota

65 Tudor STREET

Other Petroleum

Regulation under CLM Act not required

-32.925171

151.7504048

HAMILTON

Hamilton Bus Depot

Cnr Denison Street and Gordon AVENUE

Other Petroleum

Regulation under CLM Act not required

-32.92687413

151.7501743

List current as at 8 March 2022

53 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

HAMILTON NORTH

Shell Newcastle Terminal

5 Chatham ROAD

Other Petroleum

Contamination currently regulated under CLM Act

-32.91630469

151.7408712

HAMILTON NORTH

Former Black and Decker Site

56 Clyde STREET

Metal Industry

Contamination currently regulated under CLM Act

-32.91080413

151.7358236

HAMILTON NORTH

Hamilton Gasworks

1 Chatham ROAD

Gasworks

Contamination currently regulated under CLM Act

-32.91362741

151.7406241

HAMILTON NORTH

Former ELMA Site

54 Clyde STREET

Other Industry

Contamination currently regulated under CLM Act

-32.91145768

151.7367691

HARDEN

SRA Site

31 Aurvill ROAD

Unclassified

Regulation under CLM Act not required

-34.54998656

148.3689577

HARDEN

SRA Site

51 Whitton LANE

Unclassified

Contamination formerly regulated under the CLM Act

-34.55396035

148.3713349

HARDEN

South West Fuel Harden

294 Albury STREET

Service Station

Regulation under CLM Act not required

-34.55007021

148.3513821

HAROLDS CROSS

Lot 59, Vernelly Road, Harolds Cross NSW 2622 Lot 59, Vernelly ROAD

Other Industry

Regulation under CLM Act not required

-35.548621

149.604441

HARRIS PARK

Dalley Street Reserve

2A Dalley STREET

Other Industry

Regulation under CLM Act not required

-33.82749123

151.0097539

HARTLEY VALE

Former Shale Oil Refinery

Lot 52 Hartley Vale ROAD

Unclassified

Contamination currently regulated under CLM Act

-33.52766912

150.2417878

HASTINGS POINT

Coles Express Hastings Point

99 Tweed Coast ROAD

Service Station

Regulation under CLM Act not required

-28.36914103

153.5725676

HAY

SRA Land

429, 431, 435, 437 & 439 Murray STREET

Other Industry

Regulation under CLM Act not required

-34.49965611

144.840976

HAY

SRA Land

443 Murray STREET

Other Industry

Contamination formerly regulated under the CLM Act

-34.49966753

144.8410778

HAY

Former Shell Hay Depot

391 Murray STREET

Other Petroleum

Regulation under CLM Act not required

-34.50028195

144.8463999

HAY

Former Mobil Depot Hay

397-399 Murray STREET

Other Petroleum

Regulation under CLM Act not required

-34.50019184

144.8456578

List current as at 8 March 2022

54 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

HAY SOUTH

Caltex Service Station

429-431 Moama STREET

Service Station

Regulation under CLM Act not required

-34.52001427

144.8380121

HAZELBROOK

Caltex Service Station Hazelbrook

198 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.72106175

150.4520976

HEATHCOTE

Caltex Service Station

1344 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.08841066

151.0072048

HEATHCOTE

Caltex Service Station

1403 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.09059834

151.003752

HEATHCOTE

Shell Coles Express Service Station

1355 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.08780042

151.0069741

HEATHERBRAE

Bogas (Former Caltex) Service Station

3 Speedy Lock LANE

Service Station

Regulation under CLM Act not required

-32.78057822

151.7372135

HEATHERBRAE

Shell Coles Express Motto Farm Service Station

2137 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-32.79835449

151.7176284

HEXHAM

QR National - Hexham Precinct

179 & 3/67 Maitland ROAD

Other Industry

Regulation under CLM Act not required

-32.83474038

151.6821895

HEXHAM

Caltex Diesel Stop

360 Maitland ROAD

Service Station

Regulation under CLM Act not required

-32.82844873

151.6851063

HEXHAM

Cummins Newcastle Facility Hexham

21 Galleghan STREET

Other Industry

Regulation under CLM Act not required

-32.83186739

151.686709

HEXHAM

BP Service Station (Reliance Petroleum)

Corner Pacific Highway and Old Maitland ROAD Service Station

Regulation under CLM Act not required

-32.82756403

151.6846929

HEXHAM

Former Forgacs Site

21 Sparke STREET

Chemical Industry

Contamination currently regulated under CLM Act

-32.85464558

151.6988053

HEXHAM

Caltex-Bogas Warehouse

239 Old Maitland ROAD

Service Station

Regulation under CLM Act not required

-32.82899942

151.6861849

HEXHAM

Industrial Galvanizers

312 Pacific HIGHWAY

Metal Industry

Contamination currently regulated under POEO Act

-32.83457186

151.6884941

HEXHAM

14 Sparke St Hexham

14 Sparke STREET

Metal Industry

Under assessment

-32.85394328

151.6960863

List current as at 8 March 2022

55 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

HILLSTON

Former BP Depot Hillston

141-143 Cowper STREET

Other Petroleum

Regulation under CLM Act not required

-33.48823546

145.5381623

HOLBROOK

Caltex Truckstop

Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-35.71332625

147.3207237

HOMEBUSH

Ausgrid Mason Park Substation

1 Underwood ROAD

Other Industry

Regulation under CLM Act not required

-33.85674677

151.0747044

HOMEBUSH BAY

SUEZ Waste Recycling Centre (WRC) and Cleanaway Liquid Waste Treatment Plant (LWTP) Corner Pondage Link and Hill ROAD

Landfill

Regulation under CLM Act not required

-33.84359299

151.0593656

HOMEBUSH WEST

Caltex Service Station Homebush West

334-336 Parramatta ROAD

Service Station

Regulation under CLM Act not required

-33.8581543

151.0681261

HOMEBUSH WEST

Former Ford Landfill and Adjacent Land

22 Mandemar AVENUE

Landfill

Regulation under CLM Act not required

-33.86142424

151.0625556

HORNSBY

Midas Car Care Centre Hornsby

2A Linda STREET

Other Industry

Regulation under CLM Act not required

-33.70052215

151.1004786

HORNSBY

Coles Express Hornsby

194- 206 Pacific HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-33.7071993

151.0991452

HORNSBY

Hornsby Train Maintenance Centre

1B Stephen STREET

Other Industry

Regulation under CLM Act not required

-33.69370022

151.1035939

HOXTON PARK

Endeavour Energy Hoxton Park

490 Hoxton Park ROAD

Other Industry

Regulation under CLM Act not required

-33.92766437

150.8689069

HUNTERS HILL

Coles Express Hunters Hill

4 Ryde ROAD

Service Station

Regulation under CLM Act not required

-33.8317985

151.141655

HUNTERS HILL

Foreshore Land

Rear of 7, 9 & 11 Nelson PARADE

Other Industry

Contamination currently regulated under CLM Act

-33.84248362

151.1649249

HUNTERS HILL

7, 9 and 11 Nelson Parade Hunters Hill

7, 9 and 11 Nelson PARADE

Other Industry

Regulation under CLM Act not required

-33.84220148

151.1649724

HURLSTONE PARK

Former Telstra Depot

82 Canterbury ROAD

Service Station

Regulation under CLM Act not required

-33.90803171

151.1258121

HURLSTONE PARK

Former Speedway Petroleum Service Station

610 - 618 New Canterbury ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.90541228

151.1322009

List current as at 8 March 2022

56 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

HURLSTONE PARK

7-Eleven Hurlstone Park

670 New Canterbury ROAD

Service Station

Regulation under CLM Act not required

-33.90510388

151.1299825

HURSTVILLE GROVE

Moore Reserve

Morshead DRIVE

Landfill

Contamination currently regulated under CLM Act

-33.97920603

151.0873578

INGLEBURN

7-Eleven Ingleburn

72 Cumberland Road, corner Oxford ROAD

Service Station

Regulation under CLM Act not required

-34.00041505

150.8679742

INVERELL

Former Shell Depot

25 Edward STREET

Other Petroleum

Regulation under CLM Act not required

-29.76151684

151.1182033

INVERELL

Former Service Station

20 Oliver STREET

Service Station

Regulation under CLM Act not required

-29.77229743

151.1152692

INVERELL

Former Caltex Depot Inverell

4 Edward STREET

Service Station

Regulation under CLM Act not required

-29.76123104

151.1147983

INVERELL

Former Mobil Inverell Depot

29-33 Edward STREET

Other Petroleum

Regulation under CLM Act not required

-29.76135322

151.1171412

INVERELL

Caltex Service Station

55-59 Ring STREET

Service Station

Regulation under CLM Act not required

-29.76204512

151.1141737

INVERELL

Former Mobil Service Station

Corner Otho Street and Henderson STREET

Service Station

Regulation under CLM Act not required

-29.7786926

151.1149921

INVERELL

Former Caltex Service Station

141 Otho STREET

Service Station

Regulation under CLM Act not required

-29.77819403

151.1145699

ISLINGTON

Caltex Service Station

240 Maitland ROAD

Service Station

Regulation under CLM Act not required

-32.91138644

151.7457701

ISLINGTON

Shell Pipeline Easement (vacant land)

24 Fern STREET

Other Petroleum

Regulation under CLM Act not required

-32.91706254

151.7473809

JAMISONTOWN

BP Service Station Jamisontown

124 - 128 Mulgoa ROAD

Service Station

Regulation under CLM Act not required

-33.76978323

150.6764977

JAMISONTOWN

Former Caltex Jamisontown

229-231 Mulgoa ROAD

Service Station

Regulation under CLM Act not required

-33.76661447

150.6784735

JAMISONTOWN

7-Eleven Service Station

92 Mulgoa ROAD

Service Station

Contamination currently regulated under CLM Act

-33.7667231

150.6796488

List current as at 8 March 2022

57 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

JANNALI

Former Mobil Service Station

121 Georges River ROAD

Service Station

Regulation under CLM Act not required

-34.01614613

151.0681921

JANNALI

Former IGA

541 Box ROAD

Other Industry

Regulation under CLM Act not required

-34.01602134

151.0660384

JENNINGS

Jennings Former Arsenic Poison Factory

Duke Street, Manor Street, and Ballandean STREET

Chemical Industry

Contamination currently regulated under CLM Act

-28.929342

151.9298622

JENNINGS

United Jennings Service Station

1823 New England HIGHWAY

Service Station

Regulation under CLM Act not required

-28.9323235

151.9260334

JESMOND

Caltex Service Station

27 Bluegum ROAD

Service Station

Regulation under CLM Act not required

-32.9029287

151.691164

JINDABYNE

BP Service Station (Reliance Petroleum)

8 Kosciuszko ROAD

Service Station

Regulation under CLM Act not required

-36.41478692

148.6178882

JINDABYNE

Caltex Service Station

50 Kosciuszko ROAD

Service Station

Regulation under CLM Act not required

-36.41395847

148.6225113

JINGELLIC

Former Jingellic School

3179 River ROAD

Other Industry

Regulation under CLM Act not required

-35.92649487

147.7010655

JUNEE

Subdivision Proposal

5858 Gundagai ROAD

Unclassified

Regulation under CLM Act not required

-34.87783587

147.6067578

JUNEE

United Junee Service Station

No. 118-134 BROADWAY

Service Station

Regulation under CLM Act not required

-34.86808328

147.5834883

JUNEE

Junee Railway Workshops

92 Harold STREET

Other Industry

Under assessment

-34.883768

147.579525

KANAHOOKA

Former Dapto Smelter Site, Kanahooka (redeveloped)

Off Kanahooka ROAD

Metal Industry

Regulation under CLM Act not required

-34.4941348

150.8224482

KANDOS

Cement Australia Kandos Cement Works

1 Jamison STREET

Other Industry

Regulation under CLM Act not required

-32.86399912

149.9779259

KANWAL

Kanwal General Store and Fuel Supplies and Adjacent Land

68 and part of 70 Craigie AVENUE

Service Station

Contamination currently regulated under CLM Act

-33.26310031

151.4817395

KANWAL

Former Bus and Truck Rental Yard

645-647 Pacific Highway HIGHWAY

Other Petroleum

Regulation under CLM Act not required

-33.26233802

151.4825469

List current as at 8 March 2022

58 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

KARIONG

Coles Express Kariong

6 Central Coast HIGHWAY

Service Station

Regulation under CLM Act not required

-33.43443192

151.2963401

KARIONG

Caltex Service Station

Lot 2 Langford DRIVE

Service Station

Regulation under CLM Act not required

-33.43934827

151.2935447

KARUAH

BP Roadhouse Karuah

403 Tarean ROAD

Service Station

Regulation under CLM Act not required

-32.65371781

151.9629963

KATOOMBA

Aldi Stores

201 Katoomba STREET

Service Station

Regulation under CLM Act not required

-33.71756625

150.3101649

KATOOMBA

Former Katoomba/Leura Gasworks

Megalong STREET

Gasworks

Contamination currently regulated under CLM Act

-33.71304308

150.3194624

KELLYVILLE

Caltex Service Station

3-5 Windsor ROAD

Service Station

Regulation under CLM Act not required

-33.71436125

150.9602175

KELLYVILLE

BP Service Station Kellyville

19-23 Windsor ROAD

Service Station

Regulation under CLM Act not required

-33.71280997

150.9590756

KELSO

Caltex Service Station Kelso

19 Sydney ROAD

Service Station

Regulation under CLM Act not required

-33.41904247

149.6023985

KELSO

BP Service Station (Reliance Petroleum)

63 Sydney ROAD

Service Station

Regulation under CLM Act not required

-33.41925328

149.6076677

KELSO

23 Zagreb Street, Kelso NSW

23 Zagreb STREET

Other Industry

Under assessment

-33.427135

149.609708

KEMBLA GRANGE

ShawCor Australia

66 West Dapto ROAD

Other Petroleum

Regulation under CLM Act not required

-34.46875328

150.8106326

KEMBLAWARRA

Griffins Bay, Lake Illawarra

Shellharbour ROAD

Landfill

Regulation under CLM Act not required

-34.49653984

150.8943776

KEMPS CREEK

Caltex-branded Service Station

1163 Mamre ROAD

Service Station

Regulation under CLM Act not required

-33.86972102

150.7966074

KEMPSEY

Kempsey Showground

19 Sea STREET

Unclassified

Contamination being managed via the planning process (EP&A Act)

-31.07334836

152.8308795

KEMPSEY

Former Shell Depot

43-51 Gladstone STREET

Other Petroleum

Regulation under CLM Act not required

-31.07500944

152.8346699

List current as at 8 March 2022

59 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

KEMPSEY

Former Mobil Depot

14 Hopetoun STREET

Other Petroleum

Regulation under CLM Act not required

-31.07603107

152.8350132

KEMPSEY

Shell Coles Express Service Station Kempsey

165 Smith STREET

Service Station

Regulation under CLM Act not required

-31.07036743

152.8461571

KEMPSEY

Mobil Depot

154 Belgrave STREET

Service Station

Regulation under CLM Act not required

-31.07965043

152.8326303

KEMPSEY

Liberty (Former Mobil) Service Station

108-112 Smith STREET

Service Station

Regulation under CLM Act not required

-31.07492508

152.8431945

KENSINGTON

7-Eleven Kensington

135 Anzac PARADE

Service Station

Regulation under CLM Act not required

-33.91035885

151.2228537

KENSINGTON

Former Ampol Service Station

76-82 Anzac PARADE

Service Station

Regulation under CLM Act not required

-33.9059246

151.2242891

KENSINGTON

Footpath adjacent to 10-20 Anzac Parade 10-20 Anzac PARADE

Service Station

Regulation under CLM Act not required

-33.9032124

151.2237836

KENSINGTON

Caltex Service Station

211-213 Anzac PARADE

Service Station

Regulation under CLM Act not required

-33.91460752

151.2251266

KENTHURST

Vacant Land

259 McCylmonts ROAD

Unclassified

Regulation under CLM Act not required

-33.61283529

150.9425303

KHANCOBAN

Khancoban Tip

Alpine WAY

Landfill

Regulation under CLM Act not required

-36.21994191

148.1542718

KIAMA

Former Gasworks

105 to 109 and 113 Shoalhaven STREET

Gasworks

Regulation under CLM Act not required

-34.67416881

150.8504143

KIAMA HEIGHTS

Former Mobil Service Station Kiama

7-9 South Kiama DRIVE

Service Station

Regulation under CLM Act not required

-34.69553931

150.8437977

KILLARA

7-Eleven Service Station (Former Mobil)

496 Pacific HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-33.77146554

151.1606903

KILLARA

Former Caltex Service Station

692B-694 Pacific HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-33.76306802

151.1550109

KILLARA

Killara Garage

544 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.76974164

151.1599696

List current as at 8 March 2022

60 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

KILLARA

Former BP Service Station Lindfield

478 Pacific HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-33.7719298

151.1613874

KILLARA

Land Adjacent to Former Service Station Site

684-684a, 690, 692 and 696 Pacific HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-33.7631019

151.1548963

KINCUMBER

Frost Reserve

Avoca DRIVE

Landfill

Contamination currently regulated under CLM Act

-33.47065695

151.3909044

KINGS PARK

Multi-Fill

14 Garling ROAD

Chemical Industry

Under assessment

-33.74478046

150.9111964

KINGS PARK

Former Dow Corning Factory

21 Tattersall ROAD

Chemical Industry

Contamination formerly regulated under the CLM Act

-33.75012653

150.9138477

KINGSFORD

Caltex Service Station

603-611 Anzac PARADE

Service Station

Regulation under CLM Act not required

-33.93435787

151.2371198

KINGSFORD

Coles Express Service Station Kingsford

58 Gardeners ROAD

Service Station

Regulation under CLM Act not required

-33.9250054

151.2257601

KINGSGROVE

Shell Coles Express Service Station

137 Kingsgrove ROAD

Service Station

Regulation under CLM Act not required

-33.93276948

151.099026

KINGSGROVE

Caltex Kingsgrove

351-357 Stoney Creek ROAD

Service Station

Regulation under CLM Act not required

-33.95132175

151.0926872

KINGSGROVE

State Transit Authority Depot

17-23 Richland STREET

Other Petroleum

Regulation under CLM Act not required

-33.93646086

151.0973617

KIRRAWEE

Ingal Civil Products

127-141 Bath ROAD

Metal Industry

Regulation under CLM Act not required

-34.03029516

151.0754469

KIRRAWEE

7-Eleven (former Mobil) Service Station

542-546 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.03238179

151.0758071

KIRRAWEE

Caltex-branded Kirrawee Service Station

(1-3 Waratah Street) 487 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.02915971

151.0808279

KOGARAH

Scarborough Park South

184R Production AVENUE

Landfill

Regulation being finalised

-33.97922253

151.140276

KOGARAH

Caltex Service Station

29 President AVENUE

Service Station

Regulation under CLM Act not required

-33.96516866

151.141145

List current as at 8 March 2022

61 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

KOGARAH

Former 7-Eleven Kogarah

734 Princes HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-33.96406472

151.1376011

KOGARAH

Woolworths Petrol Service Station

69 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-33.96330397

151.1371182

KOOLKHAN

Former Koolkhan Power Station

Summerland WAY

Other Industry

Regulation under CLM Act not required

-29.61688704

152.9300645

KOORAGANG

NPC, berths 2 and 3

Heron ROAD

Metal Industry

Regulation under CLM Act not required

-32.89260063

151.7742527

KOORAGANG

Kooragang Island Waste Facility

Off Cormorant ROAD

Metal Industry

Contamination currently regulated under POEO Act

-32.86901125

151.7377773

KOORAGANG

Orica Kooragang Island

15 Greenleaf ROAD

Chemical Industry

Contamination currently regulated under CLM Act

-32.89654619

151.7771372

KOORAGANG

Former Boral Timber Export Facility

16 Heron ROAD

Other Industry

Regulation under CLM Act not required

-32.89710295

151.7739966

KOORAGANG

Cleanaway Technical Services

19 Egret STREET

Other Industry

Regulation under CLM Act not required

-32.8812145

151.766282

KOORAGANG

Industrial Facility

39 Heron ROAD

Chemical Industry

Under assessment

-32.89106439

151.7784064

KOORAGANG

Vacant Land

Raven Street and Cormorant ROAD

Unclassified

Regulation under CLM Act not required

-32.88410199

151.7701334

KOORAGANG

Linx Logistics

240 Cormorant ROAD

Other Industry

Regulation under CLM Act not required

-32.87480951

151.7757352

KOORINGAL

Former Shell Wagga Depot

11-15 Lake Albert ROAD

Other Petroleum

Regulation under CLM Act not required

-35.12273113

147.3786005

KOORINGAL

Caltex Service Station

265-267 Lake Albert ROAD

Service Station

Regulation under CLM Act not required

-35.14078443

147.3755442

KOORINGAL

Caltex-branded (former Mobil) Service Station

24 Lake Albert ROAD

Service Station

Regulation under CLM Act not required

-35.12239591

147.3769936

KOSCIUSZKO

Smiggin Holes Snow Clearing Shed

Link ROAD

Landfill

Regulation under CLM Act not required

-36.39098211

148.4304981

List current as at 8 March 2022

62 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

KOSCIUSZKO

Khancoban Spoil Dump

Alpine WAY

Landfill

Regulation under CLM Act not required

-36.21982803

148.1527401

KOSCIUSZKO

Sawpit Creek landfill

13km from Jindabyne, off Kosciuszko ROAD

Landfill

Regulation under CLM Act not required

-36.34858097

148.5673374

KURMOND

BP Service Station

501 Bells Line of road ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.55099195

150.6912536

KURNELL

Former Phillips Imperial Chemicals site

260 Captain Cook DRIVE

Chemical Industry

Regulation under CLM Act not required

-34.02493837

151.1952149

KURNELL

Caltex Kurnell Terminal (refer also to ID23868)

2 Solander STREET

Other Petroleum

Contamination currently regulated under POEO Act

-34.0175214

151.2159572

KURNELL

Abbott Australasia

Captain Cook DRIVE

Chemical Industry

Contamination formerly regulated under the CLM Act

-34.02339937

151.19921

KURNELL

Former Caltex Kurnell Service Station

Corner Captain Cook Drive and Solander STREET

Service Station

Regulation under CLM Act not required

-34.01269846

151.2094347

KURRI KURRI

United Petroleum Service Station Kurri Kurri

279-281 Lang STREET

Service Station

Contamination formerly regulated under the CLM Act

-32.82047175

151.477646

KURRI KURRI

Kurri Kurri Smelter

Hart ROAD

Metal Industry

Regulation under CLM Act not required

-32.7873063

151.4828827

KYOGLE

Caltex Service Station

22-24 Summerland WAY

Service Station

Regulation under CLM Act not required

-28.61806766

153.003862

LAKE HAVEN

Caltex Service Station

Goobarabah Ave Cnr Gorokan DRIVE

Service Station

Regulation under CLM Act not required

-33.24337276

151.5065335

LAKEMBA

Former Lakemba Police Station

59 Quigg STREET

Unclassified

Regulation under CLM Act not required

-33.92199239

151.079412

LAKEMBA

Caltex Service Station - Corner Punchbowl Rd and Wangee Rd 81 Wangee ROAD

Service Station

Regulation under CLM Act not required

-33.91153044

151.073306

LAKEMBA

Caltex Service Station

961-967 Canterbury ROAD

Service Station

Regulation under CLM Act not required

-33.92671102

151.0814905

LAMBTON

Caltex Service Station

422 Newcastle ROAD

Service Station

Regulation under CLM Act not required

-32.9095592

151.7109684

List current as at 8 March 2022

63 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

LAMBTON

4-26 Verulam Road, Lambton NSW 2299

4-26 Verulam ROAD

Metal Industry

Under assessment

-32.91130954

151.7170534

LANE COVE

7-Eleven Service Station

203 Burns Bay ROAD

Service Station

Regulation under CLM Act not required

-33.81458334

151.1543844

LANE COVE

BP-branded Jasbe Service Station

62-70 Epping ROAD

Service Station

Regulation under CLM Act not required

-33.81108427

151.1641531

LANE COVE

Pacific Power

Sirius ROAD

Other Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.80701776

151.1449658

LANE COVE

Coles Express Service Station Burns Bay

254 Burns Bay ROAD

Service Station

Regulation under CLM Act not required

-33.81719214

151.1518774

LANE COVE

331-335 Burns Bay Road, Lane Cove NSW 2066 331 and 333 - 335 Burns Bay ROAD

Other Industry

Contamination currently regulated under CLM Act

-33.8211575

151.1493074

LANE COVE

315-317 Burns Bay Road, Lane Cove

315-317 Burns Bay ROAD

Unclassified

Under preliminary investigation order

-33.82065224

151.1496027

LANE COVE NORTH

Former Caltex Service Station

428-432 Mowbray ROAD

Service Station

Regulation under CLM Act not required

-33.80804563

151.1721538

LANE COVE NORTH

BP Artarmon Service Station, Lane Cove North

432 Pacific HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-33.8112038

151.175547

LANE COVE WEST

Caltex Lane Cove West

235-245 Burns Bay ROAD

Service Station

Regulation under CLM Act not required

-33.81719214

151.1518774

LANE COVE WEST

Ventemans Reach Bushland

Off Mars ROAD

Unclassified

Regulation under CLM Act not required

-33.80499552

151.1450719

LANE COVE WEST

Lovetts Reserve Walking Track

301B Burns Bay ROAD

Unclassified

Contamination currently regulated under CLM Act

-33.82044223

151.1492125

LANSVALE

Mobil Service Station

44 Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-33.89172416

150.9656537

LAURIETON

Camden Haven Tyre and Brake Centre (Former Caltex Service Station)

461 Ocean DRIVE

Service Station

Regulation under CLM Act not required

-31.64367775

152.7977735

LAVENDER BAY

SRA Land

French STREET

Unclassified

Regulation under CLM Act not required

-33.84560621

151.2030148

List current as at 8 March 2022

64 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

LAVINGTON

Former Caltex Service Station

373-375 Wagga ROAD

Service Station

Regulation under CLM Act not required

-36.04797551

146.9385325

LAVINGTON

Caltex Service Station

436 Wagga (corner Dick Road) ROAD

Service Station

Regulation under CLM Act not required

-36.04500034

146.9444932

LAVINGTON

Former ERS liquid waste treatment and storage facility

819 Knights ROAD

Other Industry

Regulation under CLM Act not required

-36.06763885

146.942143

LEETON

Former Mobil Depot

108 Calrose STREET

Other Petroleum

Regulation under CLM Act not required

-34.55813326

146.3921296

LEETON

Caltex Service Station

1 Belah STREET

Service Station

Regulation under CLM Act not required

-34.55421752

146.3998431

LEETON

Yenda Producers (formerly Incitec) Leeton 1 - 2 Canal STREET

Other Petroleum

Regulation under CLM Act not required

-34.55184684

146.3862573

LEETON

Former Fuel Depot, Leeton

1-3 Short STREET

Other Petroleum

Regulation under CLM Act not required

-34.55253237

146.3864507

LEETON

United Leeton Service Station

110 Kurrajong AVENUE

Service Station

Regulation under CLM Act not required

-34.55573364

146.4099077

LEICHHARDT

SRA Land

10-11 Balmain ROAD

Other Industry

Contamination formerly regulated under the CLM Act

-33.8776803

151.1591041

LEICHHARDT

Former Kolotex site

22 George STREET

Other Industry

Contamination currently regulated under CLM Act

-33.88855307

151.1482106

LEICHHARDT

Former Labelcraft Site

30-40 George STREET

Chemical Industry

Contamination currently regulated under CLM Act

-33.88778798

151.1484773

LEICHHARDT

Leichhardt Bus Depot Area E

240 Balmain Road, corner City West LINK Other Industry

Regulation under CLM Act not required

-33.87589727

151.1598073

LEICHHARDT

RailCorp Leichhardt

7 Darley ROAD

Other Industry

Regulation under CLM Act not required

-33.87520846

151.1539012

LENNOX HEAD

Former Caltex Lennox Head

Byron STREET

Service Station

Regulation under CLM Act not required

-28.79189328

153.5883225

LENNOX HEAD

Spoors Dip

13 Fig Tree Hill DRIVE

Cattle Dip

Contamination formerly regulated under the CLM Act

-28.78258175

153.5752527

List current as at 8 March 2022

65 of 129


Suburb

SiteName

Address

LEPPINGTON

Coles Express Leppington

1443 Camden Valley WAY

Service Station

Regulation under CLM Act not required

-33.96631609

150.8154793

LEUMEAH

Caltex Service Station

6 Rudd ROAD

Service Station

Regulation under CLM Act not required

-34.05398325

150.8299209

LEURA

Former Leura Garage

126-128 Leura MALL

Service Station

Regulation under CLM Act not required

-33.7125311

150.3315386

LIDCOMBE

Metro Lidcombe (former Liberty)

134 John STREET

Service Station

Contamination currently regulated under POEO Act

-33.85456019

151.0468136

LIDDELL

Liddell Power Station

New England HIGHWAY

Other Industry

Regulation under CLM Act not required

-32.37393962

150.9756283

LIDSDALE

Angus Place Colliery

Wolgan ROAD

Other Industry

Regulation under CLM Act not required

-33.35274573

150.0996773

LIDSDALE

Kerosene Vale Colliery

Wolgan ROAD

Other Industry

Regulation under CLM Act not required

-33.38232515

150.0943561

LIDSDALE

Kerosene Vale Ash Repository

110 Skelly ROAD

Other Industry

Under assessment

-33.395693

150.086435

LIGHTNING RIDGE

Former Ambulance Station

18 - 42 Pandora STREET

Other Industry

Regulation under CLM Act not required

-29.43133877

147.9812981

LIGHTNING RIDGE

Caltex Service Station

Onyx Street, corner Morilla STREET

Service Station

Regulation under CLM Act not required

-29.42922885

147.9747954

LILLIAN ROCK

Former 'Peters Dip' Cattle Tick Dip Site

427 Lillian Rock ROAD

Cattle Dip

Regulation under CLM Act not required

-28.5314327

153.1556392

LINDFIELD

7-Eleven (former Mobil) Service Station

238 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.7788603

151.1689594

LISAROW

OneSteel Recycling

902A Pacific HIGHWAY

Metal Industry

Regulation under CLM Act not required

-33.38420179

151.3655856

LISMORE

Caltex Lismore Service Station

136 Woodlark STREET

Service Station

Regulation under CLM Act not required

-28.80807597

153.2807591

LISMORE

Shell Coles Express Service Station

100 Dawson STREET

Service Station

Regulation under CLM Act not required

-28.81140865

153.2800472

List current as at 8 March 2022

ContaminationActivityType

ManagementClass

Latitude

Longitude

66 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

LISMORE

Former Shell Depot

116 Wilson STREET

Other Petroleum

Regulation under CLM Act not required

-28.81070081

153.2621577

LISMORE

Caltex Service Station

73-75 Dawson STREET

Service Station

Regulation under CLM Act not required

-28.80894415

153.2809619

LISMORE

Lismore Gasworks

Cnr John Street & Keen STREET

Gasworks

Contamination formerly regulated under the CLM Act

-28.81764489

153.2710196

LISMORE

SRA Land

Norco LANE

Unclassified

Regulation under CLM Act not required

-28.810742

153.2702306

LISMORE HEIGHTS

Coles Express Lismore Heights

426 Ballina ROAD

Service Station

Contamination currently regulated under CLM Act

-28.81068067

153.3053065

LISMORE HEIGHTS

Impacted land, below Beardow Street landslide

22 New Ballina ROAD

Unclassified

Regulation under CLM Act not required

-28.80410458

153.2939349

LISMORE HEIGHTS

Roadside Embankment (Beardow Street)

Between Beardow and 22 New Ballina ROAD

Unclassified

Regulation under CLM Act not required

-28.81346

153.276493

LITHGOW

Former Shell CVRO and Depot

77 Bridge Street and 6 Gas Works LANE

Other Petroleum

Regulation under CLM Act not required

-33.47995091

150.162216

LITHGOW

Lithgow Thales

4 Martini PARADE

Metal Industry

Contamination formerly regulated under the CLM Act

-33.48988084

150.141366

LITHGOW

Former Mobil Depot

353 Main STREET

Other Petroleum

Regulation under CLM Act not required

-33.48235166

150.1383012

LITHGOW

Former Gasworks

Mort STREET

Gasworks

Regulation under CLM Act not required

-33.47995167

150.1635401

LITHGOW

Jasbe BP-branded Service Station (Former Reliance Petroleum) 1106 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.48426647

150.134992

LITHGOW

Caltex Lithgow (Quota Park)

Adjacent to 1131 Great Western HIGHWAY

Unclassified

Regulation under CLM Act not required

-33.47927554

150.1366238

LIVERPOOL

AC McGrath (Wholesale) Pty Ltd

20 Shepherd Street and 6A & 6B Atkinson STREET Other Industry

Regulation under CLM Act not required

-33.9320192

150.9236862

LIVERPOOL

Former Car Park

4 - 6 Rose STREET

Regulation under CLM Act not required

-33.93258955

150.9157936

List current as at 8 March 2022

Unclassified

67 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

LIVERPOOL

Woolworths Service Station

59-67 Orange Grove ROAD

Service Station

Regulation under CLM Act not required

-33.90711248

150.9178855

LIVERPOOL

68 Speed Street (former gasworks)

2A Mill ROAD

Gasworks

Regulation under CLM Act not required

-33.92992649

150.9224472

LIVERPOOL

Woodward Park

84 Memorial AVENUE

Other Industry

Under assessment

-33.924752

150.917075

LOFTUS

BP Freedom Fuel Service Station Loftus

127 Loftus AVENUE

Service Station

Regulation under CLM Act not required

-34.04570765

151.0508004

LONG JETTY

Metro Petroleum Service Station Long Jetty

326 The Entrance ROAD

Service Station

Under assessment

-33.35897356

151.4847709

LONG JETTY

Caltex Service Station

431 The Entrance ROAD

Service Station

Regulation under CLM Act not required

-33.36022468

151.4826553

LONG JETTY

Westside Petroleum Service Station

290-294 The Entrance ROAD

Service Station

Contamination currently regulated under CLM Act

-33.35686757

151.4861479

LONG JETTY

7-Eleven (former Mobil) Service Station

184-186 The Entrance ROAD

Service Station

Regulation under CLM Act not required

-33.35089363

151.4924904

LONGUEVILLE

Caltex Service Station

5 Northwood ROAD

Service Station

Regulation under CLM Act not required

-33.82427366

151.1724497

LOXFORD

Kurri Kurri Wastewater Treatment Plant

McLeod ROAD

Other Industry

Regulation under CLM Act not required

-32.802024

151.485587

LUCAS HEIGHTS

Harringtons Quarry

access from Little Forest ROAD

Landfill

Contamination currently regulated under CLM Act

-34.03555347

150.9751826

LUCAS HEIGHTS

IWC landfill

Little Forest ROAD

Landfill

Contamination formerly regulated under the CLM Act

-34.03214889

150.9753474

LUDDENHAM

Caltex Service Station

3019-3035 The Northern ROAD

Service Station

Regulation under CLM Act not required

-33.87536093

150.6888872

MACKSVILLE

Caltex Service Station

Pacific (22-24 Cooper Street) HIGHWAY

Service Station

Regulation under CLM Act not required

-30.70977455

152.9198448

MACLEAN

MacLean Outdoors

255 River STREET

Service Station

Regulation under CLM Act not required

-29.45782683

153.1970725

List current as at 8 March 2022

68 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

MACQUARIE FIELDS

Caltex Service Station

68 Harold STREET

Service Station

Regulation under CLM Act not required

-33.98557276

150.8933681

MACQUARIE PARK

Caltex North Ryde Service Station

41-43 Epping ROAD

Service Station

Regulation under CLM Act not required

-33.79138236

151.1312248

MACQUARIE PARK

1-7 Waterloo Road, Macquarie Park

1-7 Waterloo ROAD

Other Petroleum

Regulation under CLM Act not required

-33.78806877

151.1332148

MACQUARIE PARK

Porters Creek Depot - Proposed Operations Centre Site

160 Wicks ROAD

Landfill

Regulation under CLM Act not required

-33.78581579

151.1367075

MACQUARIE PARK

De Burghs Cycleway - Lane Cove National Park Riverside DRIVE

Other Petroleum

Regulation under CLM Act not required

-33.77668985

151.136542

MAITLAND

Maitland Gasworks

Charles STREET

Gasworks

Contamination currently regulated under CLM Act

-32.73603658

151.5578926

MAITLAND

Hannan and High Street

Hannan Street and High STREET

Service Station

Regulation under CLM Act not required

-32.72731682

151.5515673

MAITLAND

Coles Express Service Station

235 High STREET

Service Station

Regulation under CLM Act not required

-32.73923807

151.5620399

MALABAR

ANZAC Rifle Range former landfill

Franklin STREET

Landfill

Regulation being finalised

-33.95792671

151.2566373

MANDALONG

Mandalong Mine

Mandalong ROAD

Other Industry

Regulation under CLM Act not required

-33.11725583

151.4616452

MANGROVE MOUNTAIN

Poultry Litter Containment Pit site

258 Waratah ROAD

Unclassified

Regulation under CLM Act not required

-33.28917947

151.1672284

MANILLA

Tamworth Regional Council Works Depot Manilla 73 River STREET

Other Petroleum

Regulation under CLM Act not required

-30.74879943

150.7181011

MANLY

Caltex Service Station

Service Station

Regulation under CLM Act not required

-33.79306889

151.2858638

MANLY

Open Space at end of Stuart Street (Lot 1 DP544297) End of Stuart STREET

Gasworks

Regulation under CLM Act not required

-33.8078063

151.2898273

MANLY

St Patrick's Estate

Unclassified

Regulation under CLM Act not required

-33.8044568

151.2938595

List current as at 8 March 2022

86 Pittwater ROAD

151 Darley ROAD

69 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

MANLY

Former Little Manly Point Gasworks

Stuart STREET

Gasworks

Ongoing maintenance required to manage residual contamination (CLM Act)

MANLY VALE

Caltex Service Station Manly Vale

236-238 Condamine STREET

Service Station

MANLY VALE

Former Landfill Addiscombe Road

Addiscombe ROAD

MANNERING PARK

Latitude

Longitude

-33.8081596

151.287697

Regulation under CLM Act not required

-33.78508231

151.2674386

Landfill

Contamination currently regulated under CLM Act

-33.78307439

151.2747846

Parkview General Store (a former service station) 2 Vales ROAD

Service Station

Regulation under CLM Act not required

-33.14753814

151.5387832

MANNERING PARK

Mannering Park Mini Mart

70 Vales ROAD

Service Station

Regulation under CLM Act not required

-33.15236501

151.5371767

MARAYONG

7-Eleven (former Mobil Blacktown West) Service Station Marayong

173 Richmond ROAD

Service Station

Regulation under CLM Act not required

-33.75472796

150.8913605

MARAYONG

Woolworths Petrol Service Station Marayong

Corner Vardys Road and Turbo ROAD

Service Station

Regulation under CLM Act not required

-33.7452356

150.9041601

MARDI

Former Mardi Landfill

70-90 McPherson ROAD

Landfill

Regulation under CLM Act not required

-33.29273289

151.4100941

MARKS POINT

Former Mobil Service Station (now 7Eleven)

770-772 Pacific HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-33.05646268

151.6533795

MARKS POINT

Former Mobil Aviation Depot Belmont Airport

864 Pacific HIGHWAY

Other Petroleum

Regulation under CLM Act not required

-33.06657244

151.6497674

MAROUBRA

Coles Express Pagewood Service Station, Maroubra

299 Bunnerong PARADE

Service Station

Regulation under CLM Act not required

-33.94071282

151.2285063

MARRANGAROO

United (Former Mobil) Service Station Marrangaroo

394-398 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.45253322

150.1181023

MARRICKVILLE

Former Mobil Service Station

384 Illawarra ROAD

Service Station

Regulation under CLM Act not required

-33.91534969

151.1506717

MARRICKVILLE

TRW Steering and Suspension

22-28 Carrington ROAD

Other Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.92012667

151.1566181

MARRICKVILLE

Woolworths Petrol Service Station Marrickville

490 Illawarra ROAD

Service Station

Regulation under CLM Act not required

-33.91845177

151.1459951

List current as at 8 March 2022

70 of 129


Suburb

SiteName

Address

MARRICKVILLE

RailCorp

361 Victoria ROAD

MARRICKVILLE

Mackey Park

MARRICKVILLE

ContaminationActivityType

Latitude

Longitude

Regulation under CLM Act not required

-33.91404835

151.1557132

Cnr Richardsons Crescent and Carrington ROAD Landfill

Regulation under CLM Act not required

-33.9220263

151.1547903

Cooks River Aqueduct

Thornley STREET

Unclassified

Contamination formerly regulated under the CLM Act

-33.92224311

151.1479744

MARRICKVILLE

2 Carrington Road

2 Carrington ROAD

Unclassified

Regulation under CLM Act not required

-33.91567088

151.1589931

MARRICKVILLE

Former Dry Cleaners and Loading Dock

Smidmore STREET

Other Industry

Contamination currently regulated under CLM Act

-33.90752498

151.1717761

MARSDEN PARK

226 Grange Avenue

226 Grange AVENUE

Unclassified

Regulation under CLM Act not required

-33.70259609

150.83825

MARSFIELD

Coles Express Service Station Marsfield

189 Epping ROAD

Service Station

Regulation under CLM Act not required

-33.77519246

151.1053691

MARULAN

BP Express Marulan (Northbound)

(Northbound) Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-34.7188332

149.9949547

MARULAN

BP Service Station

(Southbound) Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-34.71932066

150.0014827

MARYVILLE

7-Eleven Service Station

184-188 Hannell STREET

Service Station

Contamination formerly regulated under the CLM Act

-32.91336028

151.7579315

MASCOT

Former Zinc Smelter and Paint Manufacturing Facility

163 O'Riordan STREET

Metal Industry

Regulation under CLM Act not required

-33.92526513

151.1892582

MASCOT

Caltex Service Station

125 O'Riordan STREET

Service Station

Regulation under CLM Act not required

-33.92309169

151.1911539

MASCOT

Mascot Pioneer Plating

25-29 Ricketty STREET

Metal Industry

Contamination currently regulated under CLM Act

-33.92075288

151.1824801

MASCOT

Heritage Business Centre

5-9 Ricketty STREET

Unclassified

Regulation under CLM Act not required

-33.92029202

151.1816656

MASCOT

Telstra Exchange

904-922 Botany ROAD

Other Industry

Regulation under CLM Act not required

-33.9293166

151.1942777

List current as at 8 March 2022

Other Industry

ManagementClass

71 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

MASCOT

Former Shell Service Station Mascot

746 Botany ROAD

Service Station

Contamination formerly regulated under the CLM Act

MASCOT

Former Freight Distribution Facility (now High-Density Residential / Commercial)

19-33 Kent ROAD

Unclassified

Regulation under CLM Act not required

MASCOT

Former Mascot Galvanising

336-348 King STREET

Metal Industry

MASCOT

Sokol Corporation

50-56 Robey STREET

MASCOT

Linear Park

MATRAVILLE

Latitude

Longitude

-33.92352295

151.1955852

-33.9227711

151.1854202

Contamination currently regulated under CLM Act

-33.92902126

151.185874

Other Industry

Regulation under CLM Act not required

-33.93162265

151.1904955

Off O'Riordan STREET

Landfill

Regulation under CLM Act not required

-33.92278693

151.1904751

Port Botany Bus Depot

7 Bumborah Point ROAD

Other Petroleum

Regulation under CLM Act not required

-33.96880413

151.2255889

MATRAVILLE

Former Golden Fleece Terminal No2

151 Beauchamp ROAD

Other Petroleum

Contamination formerly regulated under the CLM Act

-33.95719404

151.2259884

MATRAVILLE

Former Rieco Incinerator

Kain AVENUE

Other Industry

Contamination being managed via the planning process (EP&A Act)

-33.95980534

151.2423679

MATRAVILLE

7-Eleven Service Station Matraville

515 Bunnerong ROAD

Service Station

Contamination currently regulated under CLM Act

-33.95943536

151.2317598

MATRAVILLE

Former Golden Fleece Terminal No1

133 -149 Beauchamp ROAD

Other Petroleum

Contamination formerly regulated under the CLM Act

-33.95759006

151.2252023

MATRAVILLE

Vacant Lot

3 Wilkes AVENUE

Other Industry

Regulation under CLM Act not required

-33.96006406

151.2431087

MATRAVILLE

Eastern Suburbs Memorial Park

12 Military ROAD

Chemical Industry

Regulation under CLM Act not required

-33.9719906

151.2274386

MAYFIELD

7-Eleven (Former Mobil) Service Station

412-416 Maitland ROAD

Service Station

Regulation under CLM Act not required

-32.89292005

151.7300948

MAYFIELD

Shell Coles Express Service Station

63-69 Maud STREET

Service Station

Regulation under CLM Act not required

-32.89358962

151.7221298

MAYFIELD

Hunter River Sediments

Bed Sediments of the Hunter adjacent to Lot 221 DP1013964 RIVER Metal Industry

Contamination formerly regulated under the CLM Act

-32.89203741

151.7646702

List current as at 8 March 2022

72 of 129


Suburb

MAYFIELD

SiteName

Address

ContaminationActivityType

ManagementClass

Australian Tube Mills Newcastle Site

Industrial DRIVE

Metal Industry

Under assessment

MAYFIELD

BHP Steel River

The Buffer Zone' extending directly adjacent to the Hunter River; near the Tourle Street Bridge STREET

Metal Industry

Contamination currently regulated under CLM Act

MAYFIELD

Waratah Steel Mill

23 Frith STREET

Metal Industry

MAYFIELD

OneSteel (BHP)

Industrial DRIVE

MAYFIELD NORTH

BHPB Closure site and bed sediments of the Hunter River

MAYFIELD NORTH

Latitude

Longitude

-32.88835767

151.7450751

-32.8773556

151.7252427

Regulation under CLM Act not required

-32.89426592

151.7257429

Metal Industry

Contamination currently regulated under CLM Act

-32.88365878

151.7448793

Bound by Hunter River, Selwyn Street & Industrial DRIVE

Metal Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-32.89436064

151.7590762

OneSteel - Newcastle Wire, Rod and Bar Mills

141 & 151 Ingall STREET

Metal Industry

Under assessment

-32.89008485

151.752949

MAYFIELD NORTH

Former BHPB Supply site

Industrial DRIVE

Metal Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-32.88583061

151.7386157

MAYFIELD WEST

Stevenson Park landfill

2/559 Maitland ROAD

Landfill

Regulation under CLM Act not required

-32.88472556

151.7224791

MAYFIELD WEST

Koppers Coal Tar

East of Woodstock Street and Tourle STREET

Other Industry

Contamination currently regulated under POEO Act

-32.88592437

151.7361839

MAYFIELD WEST

Tourle Street Bridge Project

Tourle STREET

Landfill

Regulation under CLM Act not required

-32.88075518

151.7330073

MCDOUGALLS HILL

Caltex Service Station

4949 New England HIGHWAY

Service Station

Regulation under CLM Act not required

-32.54484714

151.1490757

MEADOWBANK

Former Council Works Depot

2 Parsonage STREET

Unclassified

Regulation under CLM Act not required

-33.82191421

151.0951974

MENAI

7-Eleven (Former Mobil) Service Station Menai

289 Menai ROAD

Service Station

Regulation being finalised

-34.01579095

151.0131737

MENAI

Caltex Service Station Menai

1 Carter Road ROAD

Service Station

Regulation under CLM Act not required

-34.01654043

151.0124133

MENANGLE

285 Finns Road, Menangle NSW

285 Finns ROAD

Unclassified

Regulation under CLM Act not required

-34.1292

150.700703

List current as at 8 March 2022

73 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

MEREWETHER

Merewether Childcare Centre

2/23 Caldwell STREET

Unclassified

Regulation under CLM Act not required

-32.94249653

151.7504279

MEREWETHER HEIGHTS

Burwood Beach Wastewater Treatment Works

Lot 1, Scenic DRIVE

Other Industry

Regulation under CLM Act not required

-32.954267

151.741358

MERIMBULA

Caltex Service Station

19-25 Merimbula DRIVE

Service Station

Regulation under CLM Act not required

-36.88757881

149.9089159

MERIMBULA

Former Mobil Service Station

27 Market STREET

Service Station

Regulation under CLM Act not required

-36.88941693

149.9103485

MERRYLANDS

Former Timber Yard and Hardware

11-19 Centenary ROAD

Other Petroleum

Regulation under CLM Act not required

-33.83083025

150.9698915

MERRYLANDS

Caltex Service Station

229 Woodville ROAD

Service Station

Regulation under CLM Act not required

-33.84547463

150.9983413

MERRYLANDS

Caltex Service Station Merrylands

148 Woodville ROAD

Service Station

Regulation under CLM Act not required

-33.83818499

150.9997199

MERRYLANDS

Stockland Merrylands Court

249-259 Merrylands ROAD

Service Station

Regulation under CLM Act not required

-33.83560037

150.9869735

MERRYLANDS

7-Eleven Merrylands Service Station

295-297 Merrylands Road, corner Windsor ROAD

Service Station

Regulation under CLM Act not required

-33.83533205

150.9851801

MERRYLANDS

Former Stockfeed Manufacturing Site

1-7 & 9-11 Neil STREET

Other Petroleum

Regulation under CLM Act not required

-33.83390257

150.9947449

MERRYLANDS WEST

Former Mobil Service Station

3 Centenary ROAD

Service Station

Regulation under CLM Act not required

-33.83214226

150.9698958

MILLER

Caltex Service Station

86 Cartwright AVENUE

Service Station

Regulation under CLM Act not required

-33.91878146

150.8827514

MILLERS FOREST

Chichester Trunk Gravity Main

water pipeline ACCESS

Other Industry

Contamination currently regulated under POEO Act

-32.772877

151.6826841

MILLERS POINT

Former AGL Gasworks

30 - 34 Hickson ROAD

Gasworks

Regulation under CLM Act not required

-33.86179594

151.2031726

MILLERS POINT

Moores Wharf UPSS

4 Towns PLACE

Other Petroleum

Regulation under CLM Act not required

-33.85581123

151.2024759

List current as at 8 March 2022

74 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

MILLERS POINT

Former AGL Gasworks

38 Hickson and road reserve ROAD

Gasworks

Contamination being managed via the planning process (EP&A Act)

-33.86280104

151.2032452

MILLERS POINT

Former AGL Gasworks

Berths 5, 6 and 7 (already demolished) and part Hickson ROAD

Gasworks

Contamination formerly regulated under the CLM Act

-33.86239771

151.2024819

MILLERS POINT

Former AGL Gasworks 36 Hickson Road

36 Hickson ROAD

Gasworks

Contamination formerly regulated under the CLM Act

-33.86243824

151.2032514

MILPERRA

Heatcraft Australia Pty Ltd

286 Horsley ROAD

Other Industry

Regulation under CLM Act not required

-33.94031556

150.9958606

MILPERRA

United Group Rail Pty Limited

373 Horsley ROAD

Landfill

Regulation under CLM Act not required

-33.93286283

150.9934071

MILPERRA

Caltex Service Station

264 Milperra ROAD

Service Station

Regulation under CLM Act not required

-33.93018101

150.9910964

MILPERRA

Former Landfill

479 Henry Lawson DRIVE

Landfill

Regulation under CLM Act not required

-33.93394617

150.9776715

MILTON

Former Sanitary Depot

Slaughterhouse ROAD

Other Industry

Regulation under CLM Act not required

-35.33819825

150.4471917

MILTON

Caltex Milton Service Station and Depot

331 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-35.33154474

150.4492852

MINCHINBURY

7-Eleven (former Mobil) Service Station

815 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.78812909

150.8495992

MINCHINBURY

BP Service Station

1055 Great Western Highway corner Archbold ROAD

Service Station

Regulation under CLM Act not required

-33.78211857

150.8244185

MINTO

Land adjacent to Former Shell depot

Airds Road and Essex STREET

Other Petroleum

Regulation under CLM Act not required

-34.02140447

150.8415134

MINTO

Shell Coles Express Service Station

73 Pembroke STREET

Service Station

Regulation under CLM Act not required

-34.02316454

150.8503118

MINTO

Former Endeavour Energy Depot

Pembroke ROAD

Other Petroleum

Regulation under CLM Act not required

-34.0408973

150.8451837

MINTO

Logistics Hub - Culverston Road, Minto

Culverston ROAD

Other Petroleum

Regulation under CLM Act not required

-34.0421711

150.833825

List current as at 8 March 2022

75 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

MIRANDA

Woolworths Service Station

455 Kingsway OTHER

Service Station

Contamination currently regulated under CLM Act

-34.03492814

151.1124681

MITTAGONG

Enhance (former Coles Express) Service Station

224 Old Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-34.44746118

150.4326183

MITTAGONG

Lots 1 and 2 Alfred St.

Alfred STREET

Other Petroleum

Contamination formerly regulated under the CLM Act

-34.44738105

150.4565159

MITTAGONG

Caltex Mittagong Service Station

65 Bowral ROAD

Service Station

Regulation under CLM Act not required

-34.45245915

150.4381291

MOAMA

Caltex Moama Service Station

73 Meninya (Cnr Regent St) STREET

Service Station

Regulation under CLM Act not required

-36.10815134

144.752849

MOLONG

Cabonne BP Service Station

2 Gidley STREET

Service Station

Contamination currently regulated under CLM Act

-33.09026307

148.8695809

MOLONG

Former Gasworks

Hill STREET

Gasworks

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.09074595

148.8703262

MONA VALE

Mona Vale Bus Depot

58 Darley STREET

Other Petroleum

Contamination currently regulated under CLM Act

-33.67452414

151.3074246

MONA VALE

Former Caltex service station and adjacent properties

79 Barrenjoey Road, 2 Polo Avenue, 6 Polo Avenue, 45 Bassett STREET

Service Station

Contamination formerly regulated under the CLM Act

-33.6743659

151.3096932

MONA VALE

7-Eleven (former Mobil) Service Station

24 Barrenjoey ROAD

Service Station

Regulation under CLM Act not required

-33.676909

151.3082515

MONA VALE

BP Peninsula Express Service Station

Corner Barrenjoey Road and Darley Street East STREET Service Station

Regulation under CLM Act not required

-33.67670799

151.3090068

MONA VALE

BP Service Station Mona Vale

1721 Pittwater ROAD

Service Station

Regulation under CLM Act not required

-33.68043443

151.3023553

MONA VALE

Caltex Investigation Area

Polo Ave, Perak STREET

Service Station

Contamination formerly regulated under the CLM Act

-33.67431333

151.3091148

MONA VALE

Taronga Place Mona Vale properties

Taronga PLACE

Other Petroleum

Contamination currently regulated under CLM Act

-33.67422848

151.3066972

MOOBALL

Mooball General Store

5913 Tweed Valley WAY

Service Station

Regulation under CLM Act not required

-28.44204594

153.4887648

List current as at 8 March 2022

76 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

MOONBI

Caltex Moonbi Service Station

New England HIGHWAY

Service Station

Regulation under CLM Act not required

-31.02264369

151.069094

MOORE PARK

Area 2, Moore Park

Driver AVENUE

Unclassified

Regulation under CLM Act not required

-33.89426868

151.2226839

MOOREBANK

Caltex Service Station

216 Newbridge ROAD

Service Station

Regulation under CLM Act not required

-33.92930835

150.9551469

MOOREBANK

Joyce Foam Products

5-9 Bridges ROAD

Chemical Industry

Regulation under CLM Act not required

-33.92596302

150.9335273

MOOREBANK

ABB Australia Pty Ltd

(a) 1 Bapaume ROAD

Other Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.94143741

150.9208754

MOOREBANK

Caltex Service Station Moorebank

2 Bridges ROAD

Service Station

Regulation under CLM Act not required

-33.92839682

150.9327012

MOOREBANK

Former Concrete Recyclers property, Newbridge Road, Moorebank

Newbridge ROAD

Landfill

Contamination being managed via the planning process (EP&A Act)

-33.9390295

150.9653979

MOOREBANK

Helles Park

Helles AVENUE

Landfill

Under assessment

-33.935917

150.92196

MOORLAND

Caltex Service Station

99 Jericho ROAD

Service Station

Regulation under CLM Act not required

-31.79436622

152.6514849

MOREE

Former Freedom Service Station Site Moree

1 Dover STREET

Service Station

Contamination formerly regulated under the CLM Act

-29.4715814

149.8440279

MOREE

Caltex Depot

101 Gosport STREET

Other Petroleum

Regulation under CLM Act not required

-29.47603684

149.8476728

MOREE

Former Golden Fleece Depot

Gosport STREET

Other Petroleum

Contamination formerly regulated under the CLM Act

-29.47698315

149.8477108

MOREE

Former Mobil Depot

Gosport STREET

Other Petroleum

Contamination formerly regulated under the CLM Act

-29.47764104

149.8478284

MOREE

Moree Airport Evaporation Pond

Newell HIGHWAY

Unclassified

Regulation under CLM Act not required

-29.50289837

149.8411301

MOREE

Caltex Service Station

54 Alice STREET

Service Station

Contamination currently regulated under CLM Act

-29.47158492

149.8433182

List current as at 8 March 2022

77 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

MOREE

Former Shell Depot

Adelaide STREET

Other Petroleum

Contamination formerly regulated under the CLM Act

-29.47655335

149.8465698

MOREE

Shell Coles Express Service Station

Corner Gwydir and Balo STREET

Service Station

Regulation under CLM Act not required

-29.46081826

149.8419975

MOREE

BP Truckstop and Depot Moree

Newell Highway - 423 Frome STREET

Service Station

Regulation under CLM Act not required

-29.48223274

149.8463679

MOREE

Sunnyside Road

Sunnyside ROAD

Unclassified

Regulation under CLM Act not required

-29.45652718

149.8226682

MORISSET

Railcorp Station Masters Cottage

24 Dora STREET

Unclassified

Regulation under CLM Act not required

-33.10849681

151.4880317

MORISSET

Morisset High School

Bridge STREET

Unclassified

Regulation under CLM Act not required

-33.10475221

151.4866482

MORISSET

Sanyog Holdings Pty Ltd

57 Dora STREET

Service Station

Under assessment

-33.107318

151.490061

MORPETH

Telstra Cable Installation and RTA Bridge work

Northumberland STREET

Other Petroleum

Regulation under CLM Act not required

-32.72489729

151.6266795

MORPETH

Former Service Station

Swan STREET

Service Station

Regulation under CLM Act not required

-32.72477413

151.6250642

MORTLAKE

Former Petroleum Storage Site

108-116 Tennyson ROAD

Other Petroleum

Regulation under CLM Act not required

-33.83979033

151.1064889

MORTLAKE

Kendall Bay Sediments

Kendall BAY

Gasworks

Contamination currently regulated under CLM Act

-33.83905999

151.1120458

MORTLAKE

Former AGL site

Tennyson ROAD

Gasworks

Contamination formerly regulated under the CLM Act

-33.84287407

151.1109313

MORTLAKE

Majors Bay Redevelopment

14-22 Hilly STREET

Other Industry

Regulation under CLM Act not required

-33.83954617

151.1054674

MORUYA

Former Fuel Depot Moruya

11 to 13 Ford STREET

Other Petroleum

Regulation under CLM Act not required

-35.9112243

150.0826475

MORUYA

Caltex Service Station Moruya

80-84 Campbell STREET

Service Station

Regulation under CLM Act not required

-35.91195596

150.0824213

List current as at 8 March 2022

78 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

MORUYA

Caltex Service Station

26 Campbell STREET

Service Station

Regulation under CLM Act not required

-35.9104985

150.0711419

MOSMAN

7-Eleven Mosman

162A Spit Road Corner Mitchell ROAD

Service Station

Regulation under CLM Act not required

-33.81747016

151.2433633

MOSMAN

BP Service Station

175 Ourimbah ROAD

Service Station

Regulation under CLM Act not required

-33.82106757

151.233291

MOSMAN

BP Express Mosman

175 Ourimbah ROAD

Service Station

Regulation under CLM Act not required

-33.821206

151.232961

MOSMAN

7-Eleven Service Station Mosman

45 Spit ROAD

Service Station

Regulation under CLM Act not required

-33.82302718

151.2435627

MOSMAN

Allan Border Oval

Myahgah ROAD

Landfill

Regulation under CLM Act not required

-33.82681534

151.2417712

MOSS VALE

Woolworths Service Station Moss Vale

609 Argyle STREET

Service Station

Regulation under CLM Act not required

-34.55409411

150.3609797

MOSS VALE

Coles Express Service Station

579 Argyle STREET

Service Station

Regulation under CLM Act not required

-34.55313422

150.364684

MOSS VALE

Moss Vale Refuelling Facility

Lackey ROAD

Other Petroleum

Regulation under CLM Act not required

-34.54662421

150.3721525

MOUNT ANNAN

Woolworths Caltex Mount Annan

157 Narellan (Corner Smeaton Grange Road) ROAD

Service Station

Regulation under CLM Act not required

-34.04685527

150.7610434

MOUNT ANNAN

Great Southern Railways Aqueduct

Off Narellan ROAD

Unclassified

Regulation under CLM Act not required

-34.07308479

150.7707436

MOUNT COLAH

Caltex Service Station Mount Colah

603 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.67034662

151.1151861

MOUNT COLAH

Foxglove Oval

Foxglove ROAD

Landfill

Contamination currently regulated under CLM Act

-33.65829855

151.1229638

MOUNT DRUITT

Caltex (former Mobil) Service Station, 17 Mount Street, Mount Druitt

17 Mount STREET

Service Station

Regulation under CLM Act not required

-33.76567994

150.8244544

MOUNT DRUITT

7-Eleven Mount Druitt

Lot 6 Luxford ROAD

Other Petroleum

Regulation under CLM Act not required

-33.76483839

150.8254157

List current as at 8 March 2022

79 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

MOUNT HUTTON

Woolworths Service Station

46 Wilsons ROAD

Service Station

Regulation under CLM Act not required

-32.9836378

151.67309

MOUNT PRITCHARD

7-Eleven Service Station

352 Elizabeth DRIVE

Service Station

Regulation under CLM Act not required

-33.90260656

150.8963326

MOUNT THORLEY

Bulga Surface Operations

Broke ROAD

Other Industry

Regulation under CLM Act not required

-32.68325751

151.1206158

MOUNT THORLEY

Lowes Petroleum (Former BP) Depot Mount Thorley

74 Mount Thorley ROAD

Other Petroleum

Regulation under CLM Act not required

-32.62443074

151.1025122

MOUNT VICTORIA

Former Mobil Service Station

81 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.5889727

150.2511783

MOUNT VICTORIA

Caltex Service Station

36a Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.58436517

150.2465528

MUDGEE

Caltex Service Station

114-116 Church STREET

Service Station

Regulation under CLM Act not required

-32.59428029

149.5876199

MUDGEE

Shell Coles Express Service Station

47 Church STREET

Service Station

Regulation under CLM Act not required

-32.59347493

149.5884623

MUDGEE

BP Service Station Mudgee

77 Church STREET

Service Station

Regulation under CLM Act not required

-32.59545872

149.588123

MUDGEE

Mobil Depot

47 Douro STREET

Other Petroleum

Contamination currently regulated under CLM Act

-32.60023979

149.5823448

MUDGEE

Mudgee Gasworks

Mortimer Street and Court STREET

Gasworks

Regulation under CLM Act not required

-32.59168859

149.5817705

MUDGEE

Former Essential Energy Depot

27-31 Inglis STREET

Other Industry

Regulation under CLM Act not required

-32.60076552

149.5858905

MUDGEE

Former Caltex Depot Mudgee

cnr Nicholson Street & Atkinson STREET

Other Petroleum

Regulation under CLM Act not required

-32.60125298

149.5851398

MULGRAVE

7-Eleven (former Mobil) Service Station

Corner Windsor Road and Mulgrave ROAD Service Station

Regulation under CLM Act not required

-33.61687781

150.8341809

MULLUMBIMBY

Station Street, Mullumbimby NSW 2482

Station STREET

Regulation being finalised

-28.547627

153.503538

List current as at 8 March 2022

Other Industry

80 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

MULWALA

Mulwala ADI Explosives Factory

Bayly STREET

Other Industry

Regulation under CLM Act not required

-35.97572689

145.9809786

MURWILLUMBAH

Murwillumbah Ambulance Depot

27 Queen STREET

Other Petroleum

Regulation under CLM Act not required

-28.32552576

153.4000182

MURWILLUMBAH SOUTH

Puma Murwillumbah (formerly Matilda)

182 Tweed Valley WAY

Service Station

Contamination currently regulated under CLM Act

-28.3263681

153.4103824

MURWILLUMBAH SOUTH

Former Norco Butter Factory (Eastern Portion)

230 Tweed Valley WAY

Other Petroleum

Regulation under CLM Act not required

-28.32791359

153.4073052

MUSWELLBROOK

Former Caltex Depot

1 Lower William STREET

Other Petroleum

Regulation under CLM Act not required

-32.26614257

150.8865136

MUSWELLBROOK

Vacant Rail Land

27 Brook STREET

Unclassified

Regulation under CLM Act not required

-32.26346086

150.8873181

MUSWELLBROOK

United Branded (Former Mobil) Service Station Muswellbrook

49-51 Maitland STREET

Service Station

Regulation under CLM Act not required

-32.27218162

150.8900206

MUSWELLBROOK

Former Mobil Depot Muswellbrook

43-51 Ford STREET

Other Petroleum

Regulation under CLM Act not required

-32.2599725

150.887573

MUSWELLBROOK

Woolworths Petrol

72 Brook STREET

Service Station

Regulation under CLM Act not required

-32.26325377

150.8905966

MUSWELLBROOK

Caltex Muswellbrook Service Station

84-86 Maitland STREET

Service Station

Regulation under CLM Act not required

-32.27793094

150.8980938

MUSWELLBROOK

Former Gasworks

Corner Carl Street and Foley STREET

Gasworks

Regulation under CLM Act not required

-32.26672337

150.8935982

MUSWELLBROOK

Bayswater Power Station

New England HIGHWAY

Other Industry

Regulation under CLM Act not required

-32.3954046

150.9502683

MUSWELLBROOK

Former Industrial Site

Lot 89 Rathmore STREET

Other Industry

Regulation under CLM Act not required

-32.30544071

150.8823657

MUSWELLBROOK

Caltex Service Station

12-16 Sydney STREET

Service Station

Regulation under CLM Act not required

-32.26785559

150.8879601

MUSWELLBROOK

Former Caltex Depot

47-50 Victoria STREET

Service Station

Regulation under CLM Act not required

-32.26788823

150.8930609

List current as at 8 March 2022

81 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

MUSWELLBROOK

Former Pit Top No. 1 Colliery Muswellbrook Coal

Corner Clendinning Street and Victoria STREET

Other Industry

Regulation under CLM Act not required

-32.27031992

150.9009981

NABIAC

Caltex Service Station Nabiac

3964 Wallanbah (Cnr Wallanbah Rd and Pacific Hwy) ROAD

Service Station

Regulation under CLM Act not required

-32.09864883

152.3754346

NAMBUCCA HEADS

Former Mobil Service Station

6 Bowra STREET

Service Station

Regulation under CLM Act not required

-30.64282127

153.0035884

NARELLAN

Caltex Service Station Narellan

1 George Hunter DRIVE

Service Station

Regulation under CLM Act not required

-34.03963992

150.7432386

NARELLAN

Former Landfill

1 Elyard STREET

Landfill

Regulation under CLM Act not required

-34.043474

150.7393256

NAROOMA

Narooma Service Station

60 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-36.21617955

150.126261

NAROOMA

Former Caltex - Narooma

82 Princes HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-36.21711766

150.1279305

NARRABEEN

Caltex Service Station

1509-1511 Pittwater ROAD

Service Station

Regulation under CLM Act not required

-33.70455756

151.2969352

NARRABEEN

Shell Coles Express Service Station

1418 Pittwater ROAD

Service Station

Regulation under CLM Act not required

-33.70013931

151.3002782

NARRABEEN

Narrabeen Shotgun Range Sydney Academy of Sport

Wakehurst PARKWAY

Unclassified

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.72138423

151.2642798

NARRABEEN

7-Eleven Service Station

1234 Pittwater ROAD

Service Station

Regulation under CLM Act not required

-33.71958892

151.298272

NARRABEEN

7-Eleven Narrabeen North

1497 Pittwater Road, corner Gondola ROAD

Service Station

Regulation being finalised

-33.7078448

151.2966483

NARRABRI

Caltex Service Station

13 Doyle STREET

Service Station

Regulation under CLM Act not required

-30.3239182

149.7843052

NARRABRI

Lowes Petroleum (Former Mobil) Narrabri Depot 3 Old Gunnedah ROAD

Other Petroleum

Regulation under CLM Act not required

-30.33473586

149.789587

NARRABRI

Caltex Service Station

Service Station

Regulation under CLM Act not required

-30.33968576

149.7657241

List current as at 8 March 2022

31-35 Cooma ROAD

82 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

NARRABRI

Caltex Narrabri Service Station

31 Dangar (Cnr Anne and Dangar) STREET Service Station

Regulation under CLM Act not required

-30.32989667

149.7756598

NARRABRI

Caltex Service Station

12 Reid STREET

Other Petroleum

Regulation under CLM Act not required

-30.32282764

149.7901182

NARRABRI

Cargill Soapstock Disposal Site

Westport ROAD

Unclassified

Contamination formerly regulated under the CLM Act

-30.4698458

149.6981931

NARRABRI

Caltex Service Station

7-13 James STREET

Service Station

Regulation under CLM Act not required

-30.33016168

149.7940732

NARRANDERA

Former Mobil Narrandera Depot

24 Whitton STREET

Other Petroleum

Regulation under CLM Act not required

-34.7410523

146.5620667

NARRANDERA

Former Mobil Emoleum Narrandera Depot

5-7 Margaret STREET

Other Petroleum

Regulation under CLM Act not required

-34.74105391

146.5628144

NARROMINE

Narromine Fuel (Former Caltex) Service Station

Cnr Burraway Street and Algalah STREET

Service Station

Regulation under CLM Act not required

-32.23565321

148.2454259

NELLIGEN

Former Clay Target Shooting Range

1398 Kings Highway and adjoining land on Old Bolaro Mountain ROAD Unclassified

Contamination currently regulated under CLM Act

-35.64392469

150.0955224

NELLIGEN

Lot 2 Old Bolaro Road

Old Bolaro ROAD

Unclassified

Contamination formerly regulated under the CLM Act

-35.64485609

150.0937341

NELSON BAY

Shell Coles Express Service Station

25 Stockton STREET

Service Station

Regulation under CLM Act not required

-32.72265762

152.1437317

NELSON BAY

Former Caltex Service Station Nelson Bay 38 Stockton STREET

Service Station

Regulation under CLM Act not required

-32.72335662

152.1429384

NEMINGHA

Caltex Service Station and Depot Nemingha

428 Armidale (previously 16 New England Highway) ROAD Service Station

Regulation under CLM Act not required

-31.12425169

150.9909054

NEUTRAL BAY

Caltex Service Station

16-38 Military ROAD

Service Station

Regulation under CLM Act not required

-33.82907162

151.2163342

NEUTRAL BAY

Shell Coles Express Service Station

200-204 Ben Boyd ROAD

Service Station

Regulation under CLM Act not required

-33.82915781

151.219437

NEW LAMBTON

Caltex Service Station New Lambton

144 Bridges ROAD

Service Station

Regulation under CLM Act not required

-32.93283668

151.7141748

List current as at 8 March 2022

83 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

NEW LAMBTON

BP Service Station

105 St James ROAD

Service Station

Regulation under CLM Act not required

-32.92910325

151.7155801

NEW LAMBTON

7-Eleven (former Mobil) Service Station

291 Turton ROAD

Service Station

Regulation under CLM Act not required

-32.91773864

151.7243096

NEWCASTLE

Reclaimed Land

26-28 Honeysuckle DRIVE

Unclassified

Contamination formerly regulated under the CLM Act

-32.92604705

151.7649508

NEWCASTLE

Wharf Road Newcastle Car Park

313-317 Wharf ROAD

Unclassified

Regulation under CLM Act not required

-32.92570385

151.7744076

NEWCASTLE

Newcastle Foreshore

40 Stevenson Place STREET

Other Industry

Regulation under CLM Act not required

-32.92556503

151.7876742

NEWCASTLE

SRA Land

Scott STREET

Gasworks

Regulation under CLM Act not required

-32.92641425

151.7837817

NEWCASTLE WEST

Former Mobil Service Station

113 Parry STREET

Service Station

Regulation under CLM Act not required

-32.92560628

151.7558542

NEWPORT

7-Eleven (former Mobil) Service Station

307 Barrenjoey ROAD

Service Station

Regulation under CLM Act not required

-33.65632902

151.3182089

NEWPORT

Former Caltex Service Station Newport

316-324 Barrenjoey ROAD

Service Station

Regulation under CLM Act not required

-33.65634516

151.3191571

NEWTOWN

Caltex Service Station Newtown

26 - 36 Enmore ROAD

Service Station

Regulation under CLM Act not required

-33.89851331

151.17714

NEWTOWN

Former Service Station

81 Wilson STREET

Service Station

Contamination formerly regulated under the CLM Act

-33.89626791

151.1827556

NEWTOWN

Aluminium Enterprises

66 Brocks LANE

Metal Industry

Contamination was addressed via the planning process (EP&A Act)

-33.89467126

151.1847528

NEWTOWN

Adjacent to Former Service Station

79 Wilson STREET

Service Station

Contamination formerly regulated under the CLM Act

-33.89630155

151.1826567

NORAVILLE

Former Toukley Landfill

Wilfred Barrett DRIVE

Landfill

Regulation under CLM Act not required

-33.27734185

151.5537784

NORTH ALBURY

Caltex Service Station and Diesel Stop

79 Union ROAD

Service Station

Regulation under CLM Act not required

-36.05496713

146.9487635

List current as at 8 March 2022

84 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

NORTH BOAMBEE VALLEY

Caltex Service Station

Cnr Pacific Hwy & Halls ROAD

Service Station

Regulation under CLM Act not required

-30.30639482

153.1007996

NORTH BONDI

Caltex Service Station North Bondi

321 Old South Head ROAD

Service Station

Regulation under CLM Act not required

-33.88463526

151.268551

NORTH NARRABEEN

7-Eleven Service Station

1501-1503 Pittwater ROAD

Service Station

Regulation under CLM Act not required

-33.70749859

151.296351

NORTH RICHMOND

Caltex Service Station

50 Bells Line Of ROAD

Service Station

Regulation under CLM Act not required

-33.57991338

150.7202346

NORTH ROCKS

7-Eleven Service Station North Rocks

340 North Rocks ROAD

Service Station

Regulation under CLM Act not required

-33.76895144

151.0305952

NORTH ST MARYS

BP Service Station

76 Glossop STREET

Service Station

Regulation under CLM Act not required

-33.76020183

150.7818149

NORTH ST MARYS

Mt Druitt Transmissi9on Substation

69 Kurrajong AVENUE

Other Industry

Under assessment

-33.764111

150.79208

NORTH STRATHFIELD

Budget Service Station

143 Concord ROAD

Service Station

Regulation under CLM Act not required

-33.85945248

151.0927853

NORTH STRATHFIELD

Former Caltex Service Station

92a Concord ROAD

Service Station

Regulation under CLM Act not required

-33.86244297

151.0932434

NORTH SYDNEY

Iora Complex

1 Kiara PLACE

Gasworks

Regulation under CLM Act not required

-33.843145

151.2161142

NORTH SYDNEY

Neutral Bay Sediments

Adjacent to Sub Base Platypus, High STREET

Gasworks

Contamination formerly regulated under the CLM Act

-33.8417682

151.2158756

NORTH SYDNEY

Sub Base Platypus (previously HMAS Platypus)

High STREET

Gasworks

Contamination formerly regulated under the CLM Act

-33.84325935

151.2170347

NORTH WOLLONGONG

Former Mobil Depot

122-126 Montague STREET

Other Petroleum

Regulation under CLM Act not required

-34.40988259

150.8939374

NORTHMEAD

Former Prestige Plastics

1C Redbank ROAD

Other Industry

Regulation under CLM Act not required

-33.79716925

150.989926

NORTHMEAD

Coles Express Service Station Northmead 197 Windsor ROAD

Service Station

Regulation under CLM Act not required

-33.77741733

151.0001719

List current as at 8 March 2022

85 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

NORTHMEAD

Sydney Water Land

51c Hammers ROAD

Landfill

Regulation under CLM Act not required

-33.7887535

150.9858088

NORTHMEAD

Caltex Service Station

98-100 Windsor ROAD

Service Station

Regulation under CLM Act not required

-33.78786563

150.9945909

NORTHMEAD

7-Eleven Service Station Northmead

56 Windsor ROAD

Service Station

Regulation under CLM Act not required

-33.79090731

150.9967332

NOWRA

Former Gasworks Managers Residence

24 Osborne STREET

Gasworks

Regulation under CLM Act not required

-34.8708875

150.5992586

NOWRA

Fire Station

69 Bridge ROAD

Gasworks

Regulation under CLM Act not required

-34.87081582

150.6004881

NOWRA

Historically Filled Land

70 Bridge ROAD

Unclassified

Regulation under CLM Act not required

-34.87081809

150.6013231

NOWRA

Shell Coles Express Service Station

55 Kinghorne STREET

Service Station

Regulation under CLM Act not required

-34.87633757

150.6023481

NOWRA

Former gasworks

Lamonds LANE

Gasworks

Ongoing maintenance required to manage residual contamination (CLM Act)

-34.87111182

150.6000803

NOWRA

Former Hollingworth Scrap Yard

72-74 Jervis and 117 East STREET

Other Industry

Regulation under CLM Act not required

-34.88324216

150.6034361

NOWRA

Woolworths Service Station

60 North Street STREET

Service Station

Regulation under CLM Act not required

-34.87266278

150.6014052

NOWRA

Harry Sawkins Park

Bounded by Princes Hwy, Graham St & McGrath AVENUE

Gasworks

Regulation under CLM Act not required

-34.87093993

150.6037157

NOWRA EAST

Mobil Service Station

Lot 3 Kalandar STREET

Service Station

Contamination formerly regulated under the CLM Act

-34.88850535

150.6093504

NYNGAN

Caltex Service Station

39-41 Pangee STREET

Service Station

Regulation under CLM Act not required

-31.56101006

147.1914997

NYNGAN

Caltex Service Station

126 Pangee STREET

Service Station

Regulation under CLM Act not required

-31.56482841

147.2002892

NYNGAN

Main West Rail Line

Mitchell HIGHWAY

Other Industry

Regulation under CLM Act not required

-31.567428

147.206263

List current as at 8 March 2022

86 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

OAK FLATS

Shellharbour City Works Depot

132 Industrial ROAD

Other Industry

Regulation under CLM Act not required

-34.56546013

150.8087225

OBERON

Caltex Service Station and Depot

Lowes Mount ROAD

Service Station

Regulation under CLM Act not required

-33.69509055

149.8570553

OBERON

Oberon Timber Complex

Lowes Mount ROAD

Other Industry

Regulation under CLM Act not required

-33.69264862

149.8564588

OBERON

Former Shell Depot

32 O'Connell ROAD

Other Petroleum

Regulation under CLM Act not required

-33.6997172

149.8450057

OBERON

CSR Ltd Property and King's Stockyard Creek

Off Endeavour STREET

Other Industry

Contamination formerly regulated under the CLM Act

-33.6922152

149.8686909

OCEAN SHORES

Former Ocean Shores Service Station

Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-28.51270299

153.5301496

OLD GUILDFORD

Caltex Service Station

636-644 Woodville ROAD

Service Station

Regulation under CLM Act not required

-33.86670857

150.9879189

OLD TOONGABBIE

Baulkham Hills Transmission Substation

191z Old Windsor ROAD

Other Industry

Under assessment

-33.782105

150.968634

ORANGE

Former Fuel Depot

24-28 Peisley STREET

Other Petroleum

Contamination currently regulated under CLM Act

-33.29624293

149.1017277

ORANGE

Caltex Orange Depot

184 Byng STREET

Service Station

Regulation under CLM Act not required

-33.28285589

149.1050273

ORANGE

Woolworths Orange Service Station

357-361 Summer Street, corner William STREET

Service Station

Regulation under CLM Act not required

-33.28445811

149.1053604

ORANGE

BP Orange Service Station (Reliance Petroleum)

81 Summer STREET

Service Station

Regulation under CLM Act not required

-33.2825884

149.0951535

ORANGE

BP-Branded Lowes Petroleum Depot

197 - 201 Margaret STREET

Other Petroleum

Regulation under CLM Act not required

-33.27145977

149.1078103

ORANGE

Caltex Summer Street Service Station Orange

70-74 Summer Street, corner Hill STREET

Service Station

Regulation under CLM Act not required

-33.28311722

149.0940712

ORANGE

Lowes Petroleum (BP-branded) Service Station

76 Peisley STREET

Service Station

Regulation under CLM Act not required

-33.29025034

149.1027194

List current as at 8 March 2022

87 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

ORANGE

Former Mobil Service Station

24-28 Bathurst ROAD

Service Station

Regulation under CLM Act not required

-33.2866912

149.1066505

ORANGE

BP (Reliance Petroleum) Service Station Orange

56-60 Bathurst ROAD

Service Station

Regulation under CLM Act not required

-33.28980053

149.1086212

ORANGE

Former Mobil Service Station

168 Peisley STREET

Service Station

Regulation under CLM Act not required

-33.28525478

149.1037259

ORANGE

5-7 Edward St Orange

5-7 Edward STREET

Other Industry

Contamination currently regulated under CLM Act

-33.2991077

149.1034092

OURIMBAH

Palmdale Service Centre Pty Ltd

3130 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.3381336

151.374586

OURIMBAH

United Ourimbah

51 Pacific HIGHWAY

Service Station

Under assessment

-33.36025941

151.3694483

OURIMBAH

Shell Coles Express Service Station

78-80 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.3468202

151.3710098

OXLEY VALE

Hayes Transport Services

10 Manilla ROAD

Other Petroleum

Regulation under CLM Act not required

-31.06991417

150.9101381

OYSTER BAY

Shell Coles Express Service Station

20 Carvers ROAD

Service Station

Contamination currently regulated under CLM Act

-34.00934475

151.0758626

OYSTER COVE

Cove Marine Pty Ltd

60 Frederick STREET

Unclassified

Contamination currently regulated under POEO Act

-32.73549959

151.952446

PADDINGTON

7-Eleven Service Station

59 Oxford STREET

Service Station

Contamination currently regulated under CLM Act

-33.88322921

151.2205024

PADDINGTON

Former Workshop

52 Hopewell STREET

Other Industry

Regulation under CLM Act not required

-33.88195798

151.2220744

PADSTOW

Caltex Padstow

115 Fairford ROAD

Service Station

Regulation under CLM Act not required

-33.9434571

151.0345671

PADSTOW

Selleys / Dulux

1-29 Gow STREET

Chemical Industry

Regulation under CLM Act not required

-33.93904125

151.0381725

PADSTOW

Former Exide Battery Manufacturing & Recycling

55 Bryant STREET

Other Industry

Contamination currently regulated under CLM Act

-33.94265241

151.0378986

List current as at 8 March 2022

88 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

PADSTOW

Galvatech

49 Gow STREET

Metal Industry

Contamination currently regulated under POEO Act

-33.93808679

151.0346862

PADSTOW

Foseco Australia

7 Stuart STREET

Chemical Industry

Regulation under CLM Act not required

-33.94342957

151.0377316

PADSTOW

Sebel Furniture

Parts 64 and 92 Gow STREET

Other Industry

Regulation under CLM Act not required

-33.93606752

151.0322057

PAGEWOOD

Former Email Site

Corner of Page Street and Holloway STREET

Metal Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.94302462

151.2132036

PAMBULA

Offsite area (roadways) adjacent to United Service Station Pambula (former Shell)

Corner Quondola Street and Bullara STREET

Service Station

Regulation under CLM Act not required

-36.93104481

149.8746763

PARKES

Caltex Service Station Parkes

352-360 Clarinda STREET

Service Station

Regulation under CLM Act not required

-33.13317454

148.173643

PARKES

Former Caltex Parkes (Mugincoble) Depot - Eugowra Rd, Mugincoble Eugowra ROAD

Service Station

Regulation under CLM Act not required

-33.19007031

148.224822

PARKES

BP Truckstop

(Newell Highway) 1 Forbes ROAD

Other Petroleum

Regulation under CLM Act not required

-33.14309226

148.1710282

PARKES

Former BP Telescope Service Station

339-341 Clarinda STREET

Service Station

Regulation under CLM Act not required

-33.13216152

148.1743239

PARKES

BP Reliance East End Service Station Parkes

46 Clarinda STREET

Service Station

Regulation under CLM Act not required

-33.14243539

148.1846227

PARKES

Former Parkes Gas Works (including Rail Corridor and offsite land)

129 Woodward Street and land within the Parkes railway CORRIDOR Gasworks

Contamination currently regulated under CLM Act

-33.14480316

148.1844397

PARKLEA

Caltex Parklea Service Station

Old Windsor (north of Miami Street) ROAD

Service Station

Regulation under CLM Act not required

-33.72427108

150.9388531

PARRAMATTA

BP Service Station

435 Church STREET

Service Station

Regulation under CLM Act not required

-33.80498714

151.0056151

PARRAMATTA

Coleman Oval Embankment

Cnr of Pitt STREET and Maquarie STREET

Unclassified

Regulation under CLM Act not required

-33.80441625

150.9954841

PARRAMATTA

7-Eleven (former Mobil) Service Station

81 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.80919769

151.0142894

List current as at 8 March 2022

89 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

PARRAMATTA

Parramatta Park Toilet Block Demolition

The Cresent Toilet Block Parramatta PARK Unclassified

Regulation under CLM Act not required

-33.81054034

150.9961968

PAUPONG

Former Timber Treatment Plant

Off Paupong ROAD

Other Industry

Regulation under CLM Act not required

-36.57657408

148.6624998

PENDLE HILL

7-Eleven Service Station

217 Wentworth AVENUE

Service Station

Regulation under CLM Act not required

-33.8017814

150.9577994

PENNANT HILLS

Shell Coles Express Pennant Hills West

386 Pennant Hills ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.73928611

151.0679704

PENRITH

Mirvac Industrial Site

2101 Castlereagh ROAD

Other Industry

Regulation under CLM Act not required

-33.73497514

150.6954097

PENRITH

7-Eleven (former Mobil) Service Station

212-222 Andrews ROAD

Service Station

Regulation under CLM Act not required

-33.73059678

150.6952571

PENRITH

Lowes Petroleum (Former Mobil) Depot Penrith

174 Coreen AVENUE

Other Petroleum

Regulation under CLM Act not required

-33.74484268

150.6980504

PENRITH

Caltex Service Station

Castlereagh Rd Cnr Lugard STREET

Service Station

Regulation under CLM Act not required

-33.73426843

150.6933382

PENRITH

BP Express Service Station

Corner Coreen Avenue and Castlereagh ROAD

Service Station

Regulation under CLM Act not required

-33.74385498

150.6925743

PENRITH

Crane Enfield Metals

2115-2131 Castlereagh ROAD

Metal Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.73734959

150.696442

PENRITH

7-Eleven Service Station Penrith

30 Henry STREET

Service Station

Regulation under CLM Act not required

-33.75408799

150.7045594

PENRITH

Caltex Penrith Service Station

153 Coreen AVENUE

Service Station

Regulation under CLM Act not required

-33.74287244

150.6927071

PENRITH

Jet 60 Dry Cleaners

Shop 3 134-138 Henry STREET

Unclassified

Regulation under CLM Act not required

-33.75231953

150.6964541

PENRITH

Former Dry Cleaners

Shop 3, 134-138 Henry STREET

Other Industry

Regulation under CLM Act not required

-33.75231953

150.6964541

PENSHURST

7-Eleven Service Station

612 Forest ROAD

Service Station

Regulation under CLM Act not required

-33.96153533

151.0793525

List current as at 8 March 2022

90 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

PENSHURST

Caltex Service Station

641 King Georges ROAD

Service Station

Regulation under CLM Act not required

-33.95985335

151.0891118

PERISHER VALLEY

Perisher Centre Loading Dock

Kosciuszko ROAD

Other Petroleum

Regulation under CLM Act not required

-36.40392862

148.4111593

PERISHER VALLEY

Perisher Ski Resort

Kosciuszko ROAD

Other Petroleum

Regulation under CLM Act not required

-36.41106374

148.4005469

PETERSHAM

Fanny Durack Aquatic Centre

Station STREET

Unclassified

Regulation under CLM Act not required

-33.89194583

151.151824

PETERSHAM

7-Eleven Petersham

8-10 Crystal STREET

Service Station

Under assessment

-33.88862

151.158667

PHEASANTS NEST

7-Eleven Service Station

(Southbound) Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-34.28291571

150.6394606

PHEASANTS NEST

7-Eleven (former Mobil) Service Station

(Northbound) Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-34.28303112

150.6363145

PICTON

Coles Express Picton

93-99 Argyle STREET

Service Station

Regulation under CLM Act not required

-34.16844337

150.6114236

PICTON

McDonalds

69 -71 Argyle STREET

Service Station

Regulation under CLM Act not required

-34.16711877

150.6121524

PITT TOWN

Whites Water Service

1 Canning PLACE

Other Industry

Regulation under CLM Act not required

-33.57418268

150.8811385

PLUMPTON

Woolworths Service Station Plumpton (Plumpton Marketplace Shops)

260 Jersey ROAD

Service Station

Regulation under CLM Act not required

-33.74478874

150.8369408

POINT PIPER

5 Wunulla Road, Point Piper

5 Wunulla ROAD

Other Industry

Under assessment

-33.868382

151.253274

PORT BOTANY

Vopak B

20 Friendship ROAD

Chemical Industry

Regulation under CLM Act not required

-33.97946548

151.2121752

PORT BOTANY

Vopak A

49 Friendship ROAD

Chemical Industry

Regulation under CLM Act not required

-33.97426175

151.2206228

PORT BOTANY

Terminals

45 Friendship ROAD

Chemical Industry

Regulation under CLM Act not required

-33.97609287

151.2174402

List current as at 8 March 2022

91 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

PORT BOTANY

Bunnerong Canal

Between Brotherson Dock and Bumborah Point ROAD Unclassified

Regulation under CLM Act not required

-33.96798227

151.2230052

PORT BOTANY

Bulk Liquids Berth UPSS, Port Botany

Charlotte ROAD

Other Petroleum

Regulation under CLM Act not required

-33.97386329

151.2120157

PORT BOTANY

Port Operations Centre UPSS, Port Botany Penrhyn ROAD

Other Petroleum

Regulation under CLM Act not required

-33.96803686

151.2205968

PORT BOTANY

Port Botany Railway Corridors

Friendship ROAD

Other Industry

Regulation under CLM Act not required

-33.95467008

151.2178012

PORT BOTANY

Smith Bros

4 Bumborah Point ROAD

Other Petroleum

Regulation under CLM Act not required

-33.9681757

151.2239505

PORT BOTANY

Vopak Terminals

21 Fishburn ROAD

Other Industry

Under assessment

-33.97946548

151.2121752

PORT KEMBLA

Coates Hire Facility (Eastern Portion)

1 Flinders STREET

Other Industry

Regulation under CLM Act not required

-34.47104817

150.89162

PORT KEMBLA

Shell Port Kembla CVRO

87-89 Flinders STREET

Other Petroleum

Regulation under CLM Act not required

-34.46964995

150.8953859

PORT KEMBLA

Darcy Road Rail Sidings

Darcy ROAD

Other Industry

Regulation under CLM Act not required

-34.47792834

150.9105503

PORT KEMBLA

No 2 Steelworks

Five Islands ROAD

Metal Industry

Contamination formerly regulated under the CLM Act

-34.45965024

150.8844432

PORT KEMBLA

Port Kembla Orica

Foreshore Road and Darcy ROAD

Other Industry

Contamination currently regulated under CLM Act

-34.47773583

150.9054545

PORT KEMBLA

Port Kembla, Auszinc Metals and Alloys

Lot 2 Shellharbour ROAD

Metal Industry

Regulation under CLM Act not required

-34.49335414

150.8961205

PORT KEMBLA

South Yard Rail Sidings

Lot 3 Old Port ROAD

Unclassified

Regulation under CLM Act not required

-34.47500551

150.8951759

PORT KEMBLA

Manildra Park

Flinders STREET

Other Petroleum

Contamination formerly regulated under the CLM Act

-34.46946878

150.8935731

PORT KEMBLA

Port Kembla Copper Smelter

Military ROAD

Metal Industry

Contamination currently regulated under POEO Act

-34.4810006

150.9063426

List current as at 8 March 2022

92 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

PORT KEMBLA

Caltex Service Station

16 Flinders STREET

Service Station

Regulation under CLM Act not required

-34.47058088

150.8945864

PORT KEMBLA

BHP Area 21

Springhill ROAD

Metal Industry

Contamination formerly regulated under the CLM Act

-34.45243931

150.8676495

PORT KEMBLA

Port Kembla Steelworks Recycling Area

Springhill ROAD

Unclassified

Regulation under CLM Act not required

-34.45271181

150.8677127

PORT KEMBLA

Commonwealth Rolling Mills (CRM)

Old Port ROAD

Metal Industry

Regulation under CLM Act not required

-34.47476117

150.8974746

PORT KEMBLA

Port Kembla, Former Electricity Commission Site

Old Port Road/Christie Drive ROAD

Other Industry

Regulation under CLM Act not required

-34.46899143

150.8982854

PORT KEMBLA

Port Kembla Steelworks - Steelhaven

Five Islands ROAD

Other Industry

Regulation under CLM Act not required

-34.47605247

150.891144

PORT KEMBLA

Port Kembla Steelworks - No.1 Works Site Five Islands ROAD

Metal Industry

Regulation under CLM Act not required

-34.47386606

150.8794912

PORT KEMBLA

Port Kembla Springhill Works

Springhill ROAD

Metal Industry

Regulation under CLM Act not required

-34.45574479

150.875052

PORT MACQUARIE

Former Mobil Depot

211 Lake ROAD

Other Petroleum

Regulation under CLM Act not required

-31.44688513

152.8864499

PORT MACQUARIE

Caltex Service Station

112-114 Gordon STREET

Service Station

Regulation under CLM Act not required

-31.43491709

152.9047618

PORT MACQUARIE

Caltex Port Macquarie Service Station

29 Lord STREET

Service Station

Regulation under CLM Act not required

-31.43326436

152.9169873

PORT MACQUARIE

Coles Myer

43 John Oxley DRIVE

Service Station

Regulation under CLM Act not required

-31.45741442

152.8739626

PORT MACQUARIE

Air BP Avgas Facility

Oliver DRIVE

Other Petroleum

Regulation under CLM Act not required

-31.43227222

152.8681083

PORT MACQUARIE

Former Mobil Service Station

Corner Oxley Highway and Major Innes DRIVE

Service Station

Regulation under CLM Act not required

-31.45738931

152.873956

PORT MACQUARIE

Port Macquarie Council Depot

Koala STREET

Unclassified

Regulation under CLM Act not required

-31.45341586

152.9032764

List current as at 8 March 2022

93 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

PORT MACQUARIE

Shell Coles Express Port Macquarie Service Station

121 Gordon STREET

Service Station

Regulation under CLM Act not required

-31.4343131

152.9046869

PORT MACQUARIE

Caltex Service Station

92 Hastings River DRIVE

Service Station

Regulation under CLM Act not required

-31.42934052

152.8830188

PORT MACQUARIE

Caltex Service Station

12-14 Bolwarra ROAD

Service Station

Regulation under CLM Act not required

-31.45015286

152.8854769

PORT MACQUARIE

Car park

28 Hayward STREET

Other Industry

Regulation under CLM Act not required

-31.43385131

152.9072399

PORTLAND

Ivanhoe Colliery

Pipers Flat ROAD

Other Industry

Regulation under CLM Act not required

-33.36595748

150.0099577

PORTLAND

Mt Piper Power Station

350 Boulder ROAD

Other Petroleum

Regulation under CLM Act not required

-33.35581541

150.0350801

PRAIRIEWOOD

7-Eleven (former Caltex) Service Station

485-487 Smithfield ROAD

Service Station

Regulation under CLM Act not required

-33.87102509

150.9031383

PRESTONS

Jalco Automotive Pty Ltd

238 Hoxton Park ROAD

Unclassified

Under assessment

-33.928012

150.892804

PROSPECT

7-Eleven (former Mobil) Service Station Prospect

354 Flushcombe ROAD

Service Station

Regulation under CLM Act not required

-33.79541624

150.9049417

PROSPECT

Pincott's Cottage, Gate C1

Off Reservoir ROAD

Unclassified

Regulation under CLM Act not required

-33.81589773

150.9144343

PROSPECT

Gatehouse, 544 Reservoir Road

544 Reservoir ROAD

Unclassified

Regulation under CLM Act not required

-33.81026272

150.9160605

PROSPECT

Cottage 3, William Lawson Drive

William Lawson DRIVE

Unclassified

Regulation under CLM Act not required

-33.81490331

150.9149885

PUNCHBOWL

Former BP Service Station

1375 Canterbury Road, corner Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.93170424

151.0537302

PUNCHBOWL

Punchbowl Laundry

42-44 Belmore ROAD

Chemical Industry

Contamination currently regulated under CLM Act

-33.93582701

151.0562638

PUNCHBOWL

Caltex Service Station Punchbowl

1285-1289 Canterbury ROAD

Service Station

Regulation under CLM Act not required

-33.93146308

151.0596348

List current as at 8 March 2022

94 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

PUTNEY

Putney Marina

20 Waterview STREET

Other Industry

Regulation under CLM Act not required

-33.82608091

151.1003966

PYMBLE

Caltex Service Station

1089 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.74102977

151.1385257

PYMBLE

Shell Coles Express Service Station

21 Ryde ROAD

Service Station

Regulation under CLM Act not required

-33.75198512

151.1438115

PYMBLE

Former 3M site

950 Pacific HIGHWAY

Gasworks

Regulation under CLM Act not required

-33.75050288

151.1460578

PYMBLE

Pymble West Dry Cleaners

6 Philip MALL

Other Industry

Under preliminary investigation order

-33.76109009

151.1284329

PYRMONT

Former Council Works Depot (Fig and Wattle Depot)

14-26 Wattle STREET

Other Industry

Regulation under CLM Act not required

-33.8752655

151.1942645

QUAKERS HILL

7-Eleven (former Mobil) Service Station

83 Lalor ROAD

Service Station

Regulation under CLM Act not required

-33.72759077

150.8966764

QUAKERS HILL

BP Branded Parkway (Former Caltex) Service Station Quakers Hill

450 Quakers Hill PARKWAY

Service Station

Regulation under CLM Act not required

-33.72998613

150.9023617

QUEANBEYAN

Former Mobil Service Station

153 Uriarra ROAD

Service Station

Regulation under CLM Act not required

-35.34425514

149.2148687

QUEANBEYAN

Bill Lilley Automotive

169 Crawford STREET

Service Station

Regulation under CLM Act not required

-35.35138121

149.232486

QUEANBEYAN

Woolworths Queanbeyan Service Station 196 Crawford (Cnr Morisset St) STREET

Service Station

Regulation under CLM Act not required

-35.35163055

149.2335759

QUEANBEYAN

Caltex Queanbeyan Service Station

88 Macquoid (also known as Bungendore Rd) STREET Service Station

Regulation under CLM Act not required

-35.34930535

149.2438607

QUEANBEYAN

Former Mobil Emoleum Depot

109-111 High STREET

Other Petroleum

Regulation under CLM Act not required

-35.3396115

149.237556

QUEANBEYAN

Former Caltex Depot

20-30 Railway STREET

Other Petroleum

Regulation under CLM Act not required

-35.34187485

149.2247277

QUEANBEYAN EAST

BP-Branded Service Station Queanbeyan

50 Yass ROAD

Service Station

Regulation under CLM Act not required

-35.34126641

149.2445103

List current as at 8 March 2022

95 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

QUEANBEYAN WEST

Caltex Service Station

Lanyon Dr Cnr Mccrae St (1 Suraci Place) STREET

Service Station

Regulation under CLM Act not required

-35.36372923

149.2067531

QUIRINDI

Former Mobil Depot Quirindi

4-6 Cross STREET

Other Petroleum

Regulation under CLM Act not required

-31.49903355

150.681972

QUIRINDI

Tamarang ServiCentre Quirindi

113-117 Station (also known as 119-121 Nowland) STREET

Service Station

Under assessment

-31.50179204

150.6814611

QUIRINDI

Caltex Service Station, Quirindi

199-201 George STREET

Service Station

Regulation under CLM Act not required

-31.5068778

150.6805874

RAMSGATE

Shell Coles Express Service Station

Grand Parade cnr Ramsgate ROAD

Service Station

Regulation under CLM Act not required

-33.98537988

151.1471234

RANDWICK

7-Eleven Service Station

126-130 Barker STREET

Service Station

Contamination currently regulated under CLM Act

-33.92096152

151.2355927

RANDWICK

Caltex Service Station

2 Alison ROAD

Service Station

Regulation under CLM Act not required

-33.9065752

151.2320697

RANDWICK

Metro Petroleum

345 Avoca STREET

Service Station

Regulation under CLM Act not required

-33.92544832

151.2396799

RANDWICK

Service Station, Randwick

33-37 Carrington ROAD

Service Station

Contamination currently regulated under CLM Act

-33.90655015

151.2525065

RAVENSWORTH

Ravensworth Operations Narama Mine

Lemington ROAD

Other Industry

Regulation under CLM Act not required

-32.47115903

151.0359579

RAVENSWORTH

Cumnock Colliery

Pikes Gully ROAD

Other Industry

Regulation under CLM Act not required

-32.40218281

150.9960082

RAYMOND TERRACE

Shell Coles Express Raymond Terrace

107 Adelaide (formerly Pacific Highway) STREET

Service Station

Regulation under CLM Act not required

-32.76110922

151.7492847

RAYMOND TERRACE

Caltex Service Station Raymond Terrace

136 Adelaide Street, corner Glenelg STREET

Service Station

Regulation under CLM Act not required

-32.76503842

151.7425264

RAYMOND TERRACE

Former Motor Registry

53 William STREET

Other Petroleum

Regulation under CLM Act not required

-32.76286473

151.7445839

RAYMOND TERRACE

Raymond Terrace Wastewater Treatment Works 22 Elizabeth AVENUE

Other Industry

Regulation under CLM Act not required

-32.7745339

151.7498871

List current as at 8 March 2022

96 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

RAZORBACK

Muscat Developments Pty Ltd

115 Mount View CLOSE

Unclassified

Under assessment

REDFERN

BP Service Station

116 Regent STREET

Service Station

REDFERN

Former Printing Works

101a Marriott STREET

REDFERN

BP-branded Jasbe Surry Hills

411 Cleveland STREET

REDFERN

Latitude

Longitude

-34.157069

150.634647

Regulation under CLM Act not required

-33.89367876

151.1995256

Other Industry

Regulation under CLM Act not required

-33.89512556

151.2113422

Service Station

Regulation under CLM Act not required

-33.89183974

151.2132466

Surry Hills Shopping Village

397-399 Cleveland & 2-38 Baptist STREET Other Industry

Regulation under CLM Act not required

-33.89229521

151.2119397

REVESBY

Dorf Clark Industries

184-194 Milperra ROAD

Metal Industry

Regulation under CLM Act not required

-33.93387149

151.000553

REVESBY

Thetis Pty Ltd - Bituminous Products

33-35 Violet STREET

Chemical Industry

Contamination currently regulated under CLM Act

-33.93702092

151.0067896

REVESBY

Mirotone Pty Ltd

21 Marigold STREET

Chemical Industry

Contamination currently regulated under POEO Act

-33.93559608

151.0002207

REVESBY

Caltex Service Station Revesby

181 The River ROAD

Service Station

Regulation under CLM Act not required

-33.95573605

151.0171779

RHODES

Homebush Bay Sediments adjoining the former UCAL and Allied Feeds sites

Homebush BAY

Chemical Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.8263749

151.0839216

RHODES

Former Glad factory site

10-16 Marquet STREET

Chemical Industry

Regulation under CLM Act not required

-33.82884048

151.0848716

RHODES

Former Allied Feeds site

Walker STREET

Other Industry

Contamination formerly regulated under the CLM Act

-33.82465376

151.0870401

RHODES

Former UCAL site

Walker STREET

Chemical Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.82727505

151.0853195

RHODES

Homebush Bay sediments adjoining former Berger Paint factory

Oulton AVENUE

Chemical Industry

Contamination currently regulated under CLM Act

-33.83535308

151.083238

RICHMOND

Caltex Richmond Service Station

98 March (Cnr East Market St) STREET

Service Station

Regulation under CLM Act not required

-33.59937996

150.7514483

List current as at 8 March 2022

97 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

RIVERSTONE

Axalta Coating Systems

15-23 Melbourne ROAD

Other Industry

Regulation under CLM Act not required

-33.6636649

150.8557519

RIVERSTONE

7-Eleven Riverstone

55 Garfield ROAD

Service Station

Regulation under CLM Act not required

-33.67802232

150.8635246

RIVERSTONE

Woolworths Vineyard Service Station, Riverstone

1 Woodland Street, corner of Windsor ROAD

Service Station

Regulation under CLM Act not required

-33.65607641

150.8724067

RIVERSTONE

Vacant Commercial Land

88-94 Junction ROAD

Unclassified

Regulation under CLM Act not required

-33.66226398

150.8789967

RIVERWOOD

7-Eleven Riverwood

30 Bonds ROAD

Service Station

Regulation under CLM Act not required

-33.9523701

151.0583887

ROCKDALE

7-Eleven (former Mobil) Service Station

293 West Botany STREET

Service Station

Regulation under CLM Act not required

-33.94995672

151.1484667

ROCKDALE

7-Eleven Service Station

99 Railway STREET

Service Station

Regulation under CLM Act not required

-33.95247322

151.1356785

ROCKDALE

Lindsay St, Rockdale

7 Lindsay STREET

Other Industry

Under assessment

-33.95900867

151.1436466

ROOTY HILL

7-Eleven (former Mobil) Service Station

106 Rooty Hill Road South ROAD

Service Station

Regulation under CLM Act not required

-33.78036181

150.8501998

ROOTY HILL

7-Eleven (former Mobil) Service Station

1042 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.78214955

150.8287656

ROOTY HILL

Infrabuild NSW Pty Ltd (formerly OneSteel NSW Pty Ltd) 22 Kellogg ROAD

Other Industry

Regulation under CLM Act not required

-33.76664143

150.8493465

ROSE BAY

Caltex Rose Bay Service Station

488 Old South Head ROAD

Service Station

Regulation under CLM Act not required

-33.87475145

151.2723847

ROSE BAY

Rose Bay Budget Service station

638-646 New South Head ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.87062149

151.2677617

ROSEBERY

Autofoil P/L

2 Mentmore AVENUE

Other Industry

Regulation under CLM Act not required

-33.91121318

151.2054882

ROSEBERY

Caltex Rosebery Service Station

321 Gardeners (Cnr Macquarie St) ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.92302898

151.2059541

List current as at 8 March 2022

98 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

ROSEBERY

Former Industrial Site (Former Electroplating Facility)

108 Dunning AVENUE

Other Industry

Regulation under CLM Act not required

-33.91630811

151.201557

ROSEBERY

Rosebery Service Station

395 Gardeners ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.92246784

151.2024589

ROSEHILL

James Hardie Australia and former James 8 and 10 Colquhoun Street and 5 Devon Hardie lands STREET

Landfill

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.82539019

151.0339466

ROSEHILL

2 Ritchie Street, Rosehill

2 Ritchie STREET

Unclassified

Contamination formerly regulated under the CLM Act

-33.82691192

151.0154948

ROSEHILL

James Hardie Factory (former, western portion)

181 James Ruse DRIVE

Other Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.81605834

151.0238145

ROSELANDS

Roselands Shopping Centre

24 Roseland AVENUE

Service Station

Regulation under CLM Act not required

-33.93499281

151.0691284

ROSELANDS

Woolworths Caltex Petrol Service Station Roselands 218 King Georges ROAD

Service Station

Regulation under CLM Act not required

-33.93303118

151.0735036

ROSELANDS

7-Eleven (former Mobil) Service Station

91 Canary's ROAD

Service Station

Regulation under CLM Act not required

-33.93356078

151.0736274

ROSEVILLE

Mobil Service Station

2 Boundary STREET

Service Station

Regulation under CLM Act not required

-33.78769177

151.1796011

ROSEVILLE CHASE

Coles Express Roseville Chase

388 Eastern Valley WAY

Service Station

Regulation under CLM Act not required

-33.78337722

151.1973901

ROZELLE

Caltex Service Station

121 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.86252996

151.168497

ROZELLE

7-Eleven (former Mobil) Service Station

178-180 (176-184) Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.8630268

151.1680857

ROZELLE

Kennards Rozelle

15-39 Wellington STREET

Other Petroleum

Regulation under CLM Act not required

-33.86176757

151.1686519

ROZELLE

White Bay Power Station

Robert STREET

Other Industry

Regulation under CLM Act not required

-33.86674636

151.1772204

ROZELLE

BP Service Station

Corner Darling Street and Thornton STREET

Service Station

Regulation under CLM Act not required

-33.8591647

151.1716591

List current as at 8 March 2022

99 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

RUFUS RIVER

SA Water Depot - Rufus River

Old Wentworth STREET

Other Petroleum

Regulation under CLM Act not required

-34.04191512

141.2679475

RUSHCUTTERS BAY

d'Albora Marinas

1b New Beach ROAD

Other Industry

Contamination currently regulated under POEO Act

-33.87351297

151.2345082

RUTHERFORD

Rutherford Transpacific

11 Kyle STREET

Other Industry

Regulation under CLM Act not required

-32.71105203

151.500311

RUTHERFORD

Shell Coles Express Service Station Rutherford

118 New England HIGHWAY

Service Station

Regulation under CLM Act not required

-32.7208703

151.5394595

RUTHERFORD

Caltex Service Station

134-138 New England HIGHWAY

Service Station

Regulation under CLM Act not required

-32.7202589

151.5381526

RUTHERFORD

Transpacific Industrial Services/Nationwide Oil Pty Ltd

99 Kyle STREET

Chemical Industry

Regulation under CLM Act not required

-32.71262159

151.5013865

RUTHERFORD

former Anambah Landfill

Anambah ROAD

Landfill

Under assessment

-32.698605

151.504263

RYDALMERE

Caltex Service Station

309 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.81196193

151.0371185

RYDALMERE

Mitsubishi Electric

348 Victoria ROAD

Other Industry

Contamination currently regulated under CLM Act

-33.81040138

151.0392812

RYDALMERE

Rheem Australia

1 Alan STREET

Other Industry

Contamination formerly regulated under the CLM Act

-33.81545013

151.0295476

RYDALMERE

BP Service Station

265 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.8109483

151.0328101

RYDALMERE

Hunter Douglas

Victoria ROAD

Chemical Industry

Regulation under CLM Act not required

-33.81009112

151.0384732

RYDALMERE

United Petroleum (former 7-Eleven) Service Station Rydalmere

262-272 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.81006724

151.032377

RYDE

Shell Coles Express Ryde

45 Lane Cove ROAD

Service Station

Regulation under CLM Act not required

-33.80726028

151.109981

RYDE

Caltex Service Station

110 Lane Cove ROAD

Service Station

Regulation under CLM Act not required

-33.80142973

151.1137925

List current as at 8 March 2022

100 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

RYDE

7-Eleven (former Mobil) Service Station

326-328 Blaxland ROAD

Service Station

Regulation under CLM Act not required

-33.80242183

151.1004278

RYDE

Ryde Bus Depot

51 - 75 Buffalo ROAD

Other Petroleum

Regulation under CLM Act not required

-33.81679771

151.1225255

SANCTUARY POINT

United Service Station, Sanctuary Point

147 Larmer AVENUE

Service Station

Regulation under CLM Act not required

-35.09918861

150.6329537

SANDGATE

Caltex Service Station Sandgate

162 Maitland ROAD

Service Station

Regulation under CLM Act not required

-32.86501596

151.706161

SANDGATE

North Limited Storage Handling facility

Maitland ROAD

Other Industry

Contamination formerly regulated under the CLM Act

-32.86598453

151.7012866

SANS SOUCI

7-Eleven (Former Mobil) Service Station

474 Rocky Point ROAD

Service Station

Regulation under CLM Act not required

-33.99088939

151.1333779

SANS SOUCI

BP Sans Souci

520 Rocky Point ROAD

Service Station

Contamination currently regulated under CLM Act

-33.99245122

151.1323571

SANS SOUCI

Kendall Street Reserve

Lawson Street and Kendall STREET

Landfill

Under preliminary investigation order

-33.99966431

151.13005

SANS SOUCI

Former Service Station

542-544 Rocky Point ROAD

Service Station

Contamination was addressed via the planning process (EP&A Act)

-33.99376148

151.1316131

SANS SOUCI

Former 7-Eleven Ramsgate

368 Rocky Point ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.98615125

151.1359961

SCHOFIELDS

Reserve 478, Grange Avenue, Schofields

Reserve 478, Grange AVENUE

Landfill

Regulation under CLM Act not required

-33.701489

150.852739

SCONE

Shell Coles Express Service Station

91- 93 Kelly STREET

Service Station

Contamination currently regulated under CLM Act

-32.04715941

150.8676346

SCONE

Scone Works Depot

220 Susan STREET

Other Petroleum

Regulation under CLM Act not required

-32.04444892

150.879152

SCONE

Mobil Scone Airport Elt

8 Walter Pye AVENUE

Other Petroleum

Regulation under CLM Act not required

-32.03596733

150.8323698

SCONE

BP - Former Depot

Scone St, Guernsey St & Susan STREET

Service Station

Contamination formerly regulated under the CLM Act

-32.04599284

150.8662046

List current as at 8 March 2022

101 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

SCONE

BP Scone

26 Kelly STREET

Service Station

Regulation under CLM Act not required

SCONE

BP Scone Service Station

58 Kelly STREET

Service Station

Contamination currently regulated under CLM Act

SEVEN HILLS

7-Eleven (Former Mobil) Service Station Seven Hills

151 Prospect HIGHWAY

Service Station

SEVEN HILLS

Australia Post

3 Powers ROAD

SEVEN HILLS

Car Park (Former Brickworks / Warehouse)

SEVEN HILLS

Latitude

Longitude

-32.04033034

150.86549

-32.043752

150.866301

Regulation under CLM Act not required

-33.76894646

150.9427004

Unclassified

Regulation under CLM Act not required

-33.77434009

150.9395495

1 Powers ROAD

Other Industry

Regulation under CLM Act not required

-33.77387442

150.9379787

BP-branded Jasbe Petroleum Service Station

156 Prospect HIGHWAY

Service Station

Regulation under CLM Act not required

-33.76906502

150.9414821

SEVEN HILLS

Caltex Service Station

38 Abbott ROAD

Service Station

Regulation under CLM Act not required

-33.76692649

150.9548271

SEVEN HILLS

Caltex Service Station Seven Hills

105 Station ROAD

Service Station

Regulation under CLM Act not required

-33.77435881

150.9448733

SEVEN HILLS

Former Australian Waste Oil Refineries Site

27 Powers ROAD

Other Industry

Contamination formerly regulated under the CLM Act

-33.77536127

150.9511122

SHELLY BEACH

Former Shelly Beach Landfill

Oaks AVENUE

Landfill

Regulation under CLM Act not required

-33.36700551

151.4913631

SHORTLAND

Former Astra Street Landfill

2 (part) & 28 (part) Astra STREET

Landfill

Contamination currently regulated under CLM Act

-32.8689426

151.6974685

SHORTLAND

Tuxford Park landfill

10 King STREET

Landfill

Regulation under CLM Act not required

-32.87721139

151.6936837

SHORTLAND

Former Lorna St landfill

8/475 Sandgate ROAD

Landfill

Regulation under CLM Act not required

-32.87888726

151.7023245

SHORTLAND

7-Eleven (Former BP) Service Station

298-302 Sandgate ROAD

Service Station

Regulation under CLM Act not required

-32.8861645

151.6953912

SHORTLAND

Shortland Wastewater Treatment Works

Aden STREET

Other Industry

Under assessment

-32.882996

151.684745

List current as at 8 March 2022

102 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

SILVERWATER

Former Silverwater Landfill

Carnarvon ROAD

Landfill

Contamination currently regulated under CLM Act

-33.83506394

151.033214

SILVERWATER

Vacant property

103-105 Silverwater ROAD

Other Industry

Regulation under CLM Act not required

-33.83831374

151.0472576

SILVERWATER

Storage Facility

54-58 Derby STREET

Unclassified

Under assessment

-33.83855869

151.0478649

SILVERWATER

Former Printing Facility

46-58 Derby STREET

Other Industry

Under assessment

-33.83866058

151.0482675

SILVERWATER

Silverwater Correctional Complex

Holker STREET

Landfill

Regulation under CLM Act not required

-33.83123611

151.0585298

SINGLETON

BP Service Station Singleton

53 George (Cnr Macquarie St) STREET

Other Petroleum

Regulation under CLM Act not required

-32.56182325

151.1748054

SINGLETON

Singleton Gasworks

55-57 John STREET

Gasworks

Contamination formerly regulated under the CLM Act

-32.56774715

151.1658188

SINGLETON

Shell Coles Express Service Station

69-73 George STREET

Service Station

Regulation under CLM Act not required

-32.56297156

151.1755215

SINGLETON

Mobil Singleton Airport Elt

74B Range ROAD

Other Petroleum

Regulation under CLM Act not required

-32.60270846

151.1944828

SINGLETON

Putty Saw Mill

(via Singleton) Putty ROAD

Other Industry

Contamination currently regulated under CLM Act

-32.99958725

150.7111684

SINGLETON

NSW Mines Rescue Services - Singleton

6 Lachlan AVENUE

Other Industry

Regulation under CLM Act not required

-32.54537821

151.156584

SMITHFIELD

Caltex Smithfield

16-18 Tait STREET

Service Station

Regulation under CLM Act not required

-33.84596441

150.9435497

SMITHFIELD

Freestones

1 Hume ROAD

Other Petroleum

Regulation under CLM Act not required

-33.83577694

150.9310112

SMITHFIELD

Liquip International

13 Hume ROAD

Other Industry

Regulation under CLM Act not required

-33.83802635

150.9319034

SMITHFIELD

Coles Express (former Mobil) Service Station

678 The Horsley Drive, corner Smithfield ROAD

Service Station

Regulation under CLM Act not required

-33.85376154

150.9400104

List current as at 8 March 2022

103 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

Contamination being managed via the planning process (EP&A Act)

-33.85025253

150.9411561

Corner Ebden Street and Wodonga PLACE Service Station

Contamination formerly regulated under the CLM Act

-36.08875942

146.9093882

Shell Coles Express Service Station

Lot 1 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.50589001

150.1238487

SOUTH COOGEE

Caltex South Coogee Service Station

169-173 Malabar ROAD

Service Station

Regulation under CLM Act not required

-33.93233184

151.2574377

SOUTH GRAFTON

Shell Coles Express Service Station

91 Bent STREET

Service Station

Regulation under CLM Act not required

-29.70605829

152.9400329

SOUTH GRAFTON

Former United (former Mobil) Service Station

Corner Pacific Highway and Charles STREET

Service Station

Regulation under CLM Act not required

-29.70814828

152.9412928

SOUTH GRAFTON

Former Caltex Service Station

46-58 Schwinghammer STREET

Service Station

Regulation under CLM Act not required

-29.71149672

152.9453337

SOUTH GRAFTON

Former Caltex Depot South Grafton

72-82 Swallow ROAD

Other Petroleum

Regulation under CLM Act not required

-29.73168549

152.944024

SOUTH GRAFTON

Caltex Service Station

Pacific Hwy Cnr Gwyder HIGHWAY

Service Station

Regulation under CLM Act not required

-29.70739015

152.9425508

SOUTH GRANVILLE

Enhance Service Station South Granville

2 Rawson ROAD

Service Station

Regulation under CLM Act not required

-33.86366193

151.0088768

SOUTH KEMPSEY

Caltex Service Station

52 Lachlan STREET

Service Station

Regulation under CLM Act not required

-31.09361084

152.8370796

SOUTH LISMORE

North Coast Petroleum (Former Mobil) Depot Lismore

19-21 Elliot ROAD

Other Petroleum

Regulation under CLM Act not required

-28.81212046

153.2661935

SOUTH LISMORE

Former Mobil Service Station

126 - 128 Union STREET

Service Station

Regulation under CLM Act not required

-28.81242175

153.267541

SOUTH LISMORE

Caltex Service Station

237 Union STREET

Service Station

Regulation under CLM Act not required

-28.82052708

153.2648111

SOUTH LISMORE

Former Mobil Depot

26-32 Phyllis STREET

Other Petroleum

Regulation under CLM Act not required

-28.81005206

153.2660073

SMITHFIELD

Former Landfill

Little STREET

SOUTH ALBURY

BP Border Service Station

SOUTH BOWENFELS

List current as at 8 March 2022

Landfill

104 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

SOUTH MURWILLUMBAH

Former Caltex Depot

39 Lundberg DRIVE

Service Station

Regulation under CLM Act not required

-28.332622

153.4212884

SOUTH MURWILLUMBAH

Caltex Service Station

1-7 Buchanan (Cnr Tweed Valley Way) STREET

Service Station

Regulation under CLM Act not required

-28.32687988

153.4093274

SOUTH MURWILLUMBAH

Former Mobil Depot

45 Wardrop STREET

Other Petroleum

Regulation under CLM Act not required

-28.33421395

153.3993772

SOUTH NOWRA

Caltex South Nowra

100 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.90516081

150.6029621

SOUTH PENRITH

7-Eleven Service Station

45 Aspen STREET

Service Station

Regulation under CLM Act not required

-33.77727694

150.7107228

SOUTH TAMWORTH

Coles Express Tamworth

251 - 253 Goonoo Goonoo ROAD

Service Station

Contamination currently regulated under CLM Act

-31.1118945

150.9228523

SOUTH TAMWORTH

Caltex Service Station

2 Kathleen Street, corner Kent STREET

Service Station

Regulation under CLM Act not required

-31.10361712

150.9186343

SOUTH WENTWORTHVILLE

Aldi Stores Development

331-339 Great Western HIGHWAY

Metal Industry

Regulation under CLM Act not required

-33.81605854

150.9697429

SOUTH WENTWORTHVILLE

Caltex Service Station

313 Great Western HIGHWAY

Service Station

Regulation under CLM Act not required

-33.81643692

150.9718802

SOUTH WEST ROCKS

Former Trial Bay Caltex Depot

Phillip DRIVE

Other Petroleum

Under assessment

-30.89190078

153.0573056

SOUTH WEST ROCKS

Former Shell Trial Bay Depot

Phillip DRIVE

Other Petroleum

Regulation under CLM Act not required

-30.89273836

153.0612772

SOUTH WEST ROCKS

Residential area and Reserve opposite Former Caltex terminal

Phillip DRIVE

Other Petroleum

Regulation under CLM Act not required

-30.89172594

153.0573164

SPRINGVALE

Springvale Colliery

Castlereagh HIGHWAY

Other Industry

Regulation under CLM Act not required

-33.40334736

150.1070462

ST CLAIR

7-Eleven (former Mobil) Service Station

4 Endeavour AVENUE

Service Station

Regulation under CLM Act not required

-33.79430926

150.7885793

ST IVES

7-Eleven (former Mobil) St Ives Service Station

157-159 Mona Vale Road, corner Putarri AVENUE

Service Station

Regulation under CLM Act not required

-33.73265301

151.1563899

List current as at 8 March 2022

105 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

ST IVES

Caltex Service Station

452 Mona Vale ROAD

Service Station

Regulation under CLM Act not required

-33.70752272

151.187545

ST IVES

Caltex Service Station

164 Mona Vale ROAD

Service Station

Regulation under CLM Act not required

-33.7307595

151.1570462

ST IVES

Caltex Service Station St Ives

363 Mona Vale ROAD

Service Station

Regulation under CLM Act not required

-33.7168971

151.1735263

ST IVES

Shell Service Station

179-181 Mona Vale ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.73124859

151.1575827

ST LEONARDS

Telstra Data Centre

4A Herbert STREET

Other Petroleum

Regulation under CLM Act not required

-33.81873741

151.1914222

ST MARYS

Former Woolworths Service Station

120-128 Forrester ROAD

Service Station

Regulation under CLM Act not required

-33.75525115

150.7752897

ST MARYS

7-Eleven (former Mobil) Service Station

2 Christie STREET

Service Station

Regulation under CLM Act not required

-33.74790843

150.7767667

ST MARYS

7-Eleven (former Mobil) Service Station

2 Wilson STREET

Service Station

Regulation under CLM Act not required

-33.77790415

150.771689

ST MARYS

Solveco

38 LINKS ROAD

Other Industry

Contamination currently regulated under CLM Act

-33.73875413

150.7716457

ST MARYS

Integral Energy Mt Druitt Transmission Substation

69 Kurrajong North ROAD

Other Industry

Regulation under CLM Act not required

-33.76376093

150.7921691

ST MARYS

Caltex St Marys Service Station

Wordoo St Cnr Forrester ROAD

Service Station

Regulation under CLM Act not required

-33.75334263

150.7755489

ST MARYS

Chemcolour Industries

19-25 Anne STREET

Chemical Industry

Regulation under CLM Act not required

-33.75027071

150.7725397

ST MARYS

Old Drycleaning location

1-7 Queen STREET

Other Industry

Under assessment

-33.76223376

150.774412

ST MARYS

St Mary's Shopping Village

10 Charles Hackett DRIVE

Other Industry

Regulation under CLM Act not required

-33.76647672

150.7710143

ST PETERS

Cooks River Rail Terminal

20 Canal ROAD

Unclassified

Regulation under CLM Act not required

-33.91943986

151.1726689

List current as at 8 March 2022

106 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

ST PETERS

Camdenville Park

May STREET

Other Industry

Regulation under CLM Act not required

ST PETERS

Former Tidyburn Facility

53 Barwon Park ROAD

Chemical Industry

Contamination formerly regulated under the CLM Act

ST PETERS

BP Express Service Station

2 Princes HIGHWAY

Service Station

ST PETERS

Former Industrial Manufacturing Facility (Taubman's Paints)

75 Mary STREET

ST PETERS

Burrows Industrial Estate

STANMORE

Latitude

Longitude

-33.90911815

151.176951

-33.9130091

151.1809912

Regulation under CLM Act not required

-33.90982281

151.1809936

Other Industry

Regulation under CLM Act not required

-33.91307297

151.1731383

1-3 Burrows ROAD

Landfill

Regulation under CLM Act not required

-33.91725

151.180616

125 Corunna Road

125 Corunna ROAD

Unclassified

Regulation under CLM Act not required

-33.88937382

151.1644589

STOCKTON

Former Coroba Landfill

310 Fullerton STREET

Landfill

Regulation under CLM Act not required

-32.89578751

151.7898857

STRATHFIELD

7-Eleven (former Mobil) Service Station

577 Liverpool ROAD

Service Station

Regulation under CLM Act not required

-33.88736091

151.0743474

STRATHFIELD SOUTH

Former Landfill Site

7-9 Dunlop STREET

Landfill

Regulation under CLM Act not required

-33.89509698

151.0796751

STROUD

Stroud Fuel Supplies (Former Caltex) Service Station

1 Cowper STREET

Service Station

Regulation under CLM Act not required

-32.39092749

151.9563089

SUFFOLK PARK

BP Service Station

207-209 Broken Head ROAD

Service Station

Regulation under CLM Act not required

-28.68800088

153.6083821

SUFFOLK PARK

Suffolk Park dip site

Cnr Broken Head Road & Beech DRIVE

Cattle Dip

Regulation under CLM Act not required

-28.6874242

153.6072824

SUMMER HILL

Maurice Dry Cleaners

150 Smith STREET

Other Industry

Under assessment

-33.891935

151.137331

SURRY HILLS

Woolworths Petrol Surry Hills

475 Cleveland STREET

Service Station

Regulation under CLM Act not required

-33.89223271

151.2161434

SURRY HILLS

81 & 81A (Formerly 69 - 81) Foveaux Former Legion Cabs (Trading) Cooperative STREET

Service Station

Regulation under CLM Act not required

-33.88470082

151.2107944

List current as at 8 March 2022

107 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

SURRY HILLS

Ausgrid Road Reserve

Mary STREET

Other Industry

Regulation under CLM Act not required

SUTHERLAND

United Service Station and Sutherland Reservoir

1 to 3 Oxford STREET

Service Station

Contamination currently regulated under CLM Act

SUTHERLAND

7-Eleven Service Station

693 Old Princes HIGHWAY

Service Station

SUTTON FOREST

Coles Express Sutton Forest West

Hume HIGHWAY

SWANSEA

Caltex Service Station

126 Pacific HIGHWAY

SWANSEA

Latitude

Longitude

-33.88292195

151.2095176

-34.029532

151.0579906

Regulation under CLM Act not required

-34.02976735

151.0588789

Service Station

Regulation under CLM Act not required

-34.60808989

150.2250592

Service Station

Regulation under CLM Act not required

-33.08811841

151.6381764

Swansea 1 - Wastewater Pumping Station 137 and 137a Northcote AVENUE

Other Industry

Regulation under CLM Act not required

-33.09733813

151.6473669

SYDENHAM

SRA Land

117 Railway PARADE

Other Industry

Regulation under CLM Act not required

-33.91560723

151.1656846

SYDENHAM

Sydenham XPT Maintenance Facility

Way STREET

Other Industry

Regulation under CLM Act not required

-33.91698468

151.1614089

SYDNEY

Interpro House (OSP 46581)

447 Kent STREET

Other Petroleum

Regulation under CLM Act not required

-33.87225413

151.204761

SYDNEY

Eurostar Dry Cleaners

100 Oxford STREET

Chemical Industry

Regulation under CLM Act not required

-33.8792987

151.2156647

SYDNEY

Chifley Tower (basement fuel storage area)

2 Chifley SQUARE

Other Petroleum

Under assessment

-33.865992

151.211838

SYDNEY OLYMPIC PARK

RMS Western Precinct

14A-14E and 16 Hill ROAD

Other Petroleum

Regulation under CLM Act not required

-33.82239777

151.0758664

SYDNEY OLYMPIC PARK

Haslams Creek South Area 3

At Kronos Hill, Kevin Coombes AVENUE

Landfill

Contamination formerly regulated under the CLM Act

-33.84113059

151.0602966

SYDNEY OLYMPIC PARK

Bicentennial Park

Bicentennial DRIVE

Landfill

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.84456248

151.0788116

SYDNEY OLYMPIC PARK

Former Golf Driving Range Landfill

Sarah Durack AVENUE

Landfill

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.85358517

151.0713987

List current as at 8 March 2022

108 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

SYDNEY OLYMPIC PARK

Kronos Hill Landfill

Kevin Coombes AVENUE

Landfill

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.84014442

151.0649521

SYDNEY OLYMPIC PARK

Wilson Park (Former oil gas plant site)

Newington ROAD

Gasworks

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.82623982

151.0536833

SYDNEY OLYMPIC PARK

Woo-la-ra Landfill

Hill ROAD

Landfill

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.82695807

151.07282

SYDNEY OLYMPIC PARK

Aquatic Centre Carpark Landfill

Shane Gould AVENUE

Landfill

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.85153457

151.0678127

SYDNEY OLYMPIC PARK

Blaxland Common Landfill

Jamieson STREET

Landfill

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.82638382

151.05972

SYLVANIA

Caltex Service Station

61 Port Hacking ROAD

Service Station

Regulation under CLM Act not required

-34.0140089

151.104212

SYLVANIA HEIGHTS

Ampol Service Station (former Caltex) Sylvania Heights

414-416 Princes HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-34.02361051

151.0895394

TALBINGO

Old Town Landfill

Bridle STREET

Landfill

Regulation under CLM Act not required

-35.59018237

148.3041771

TALBINGO

T3 Spoil dump and adjoining river sediments

Off Snowy Mountains HIGHWAY

Landfill

Contamination formerly regulated under the CLM Act

-35.6177268

148.2926158

TALBINGO

Former grit blasting site

Old Damsite ROAD

Other Industry

Regulation under CLM Act not required

-35.60894551

148.3030165

TALLAWANG

Rail Corridor at Tallawang

Whistons LANE

Other Industry

Under assessment

-32.201009

149.45324

TAMINDA

Taminda Depots and Adjacent Areas

27-29 Gunnedah ROAD

Other Petroleum

Under assessment

-31.09642128

150.9058193

TAMINDA

Mobil Depot

9 Hinkler ROAD

Other Petroleum

Regulation under CLM Act not required

-31.09584286

150.9040493

TAMINDA

Cleanaway Operations Pty Ltd

31 Gunnedah ROAD

Other Industry

Under assessment

-31.09621029

150.9051567

TAMINDA

Cummins South Pacific Pty Ltd

141 Gunnedah ROAD

Other Petroleum

Under assessment

-31.096677

150.891745

List current as at 8 March 2022

109 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

TAMWORTH

Caltex Tamworth Service Station

109 Gunnedah ROAD

Service Station

Regulation under CLM Act not required

-31.09723226

150.8955299

TAMWORTH

Curlew Crescent

19-29 Curlew CRESCENT

Metal Industry

Regulation under CLM Act not required

-31.06963607

150.9069306

TAMWORTH

Former Service Station, Fitzpatrick Super Fund, Tamworth

210 Goonoo Goonoo ROAD

Service Station

Regulation under CLM Act not required

-31.10613594

150.9234143

TAMWORTH

Gunnedah Road Site

49 GUNNEDAH ROAD

Other Industry

Contamination formerly regulated under the CLM Act

-31.09574904

150.9021583

TAMWORTH

Elovera Former Sheep Dip

730 Ascot Calala ROAD

Cattle Dip

Regulation under CLM Act not required

-31.1801846

150.962897

TAMWORTH

Housing NSW

29 -33 White STREET

Other Petroleum

Regulation under CLM Act not required

-31.0915651

150.9357811

TAMWORTH

Former Mobil Service Station

373-375 Armidale ROAD

Service Station

Regulation under CLM Act not required

-31.10122679

150.9441341

TAMWORTH

Kensell's Mitsubishi

11-14 Kable AVENUE

Other Petroleum

Regulation under CLM Act not required

-31.08921565

150.9273063

TAMWORTH

Caltex Star Tamworth

21 White STREET

Service Station

Regulation under CLM Act not required

-31.09255137

150.9341709

TAMWORTH

Former Service Station Tamworth

(Cnr Scott Rd) 254-256 Goonoo Goonoo ROAD

Service Station

Regulation under CLM Act not required

-31.1118945

150.9228523

TAMWORTH

Elgas Depot (former gasworks)

115 Marius STREET

Gasworks

Under preliminary investigation order

-31.08546191

150.926437

TAMWORTH

Proposed ALDI Store Tamworth

194-196 Peel STREET

Other Industry

Under assessment

-31.08522053

150.9260054

TARAGO

Tarago Railway Siding

Goulburn STREET

Other Industry

Contamination currently regulated under CLM Act

-35.0695949

149.6516166

TARAGO

Tarago former Station Masters Cottage

106 Goulburn STREET

Landfill

Under assessment

-35.069381

149.652123

TARCUTTA

Mobil Service Station

(Hume Highway) 32 Sydney STREET

Service Station

Contamination formerly regulated under the CLM Act

-35.2772942

147.73574

List current as at 8 March 2022

110 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

TAREE

Caltex Taree

12 Pitt STREET

Service Station

Regulation under CLM Act not required

-31.90551738

152.4783334

TAREE

Former Caltex Depot

44 Stevenson STREET

Other Petroleum

Regulation under CLM Act not required

-31.90563595

152.4640848

TAREE

Former BP Service Station (Reliance Petroleum)

150 Manning River DRIVE

Service Station

Regulation under CLM Act not required

-31.93842026

152.4682056

TAREE

Former Shell Depot

53-55 Stevenson STREET

Other Petroleum

Regulation under CLM Act not required

-31.90514622

152.4649706

TAREE

United Service Station and Former Mobil Depot

85 Muldoon Street, corner Grey Gum ROAD

Service Station

Regulation under CLM Act not required

-31.89744109

152.4508569

TAREE

Caltex Service Station

104-106 Commerce STREET

Service Station

Regulation under CLM Act not required

-31.90720519

152.4500926

TAREE

Footpath in front of the former BP service station 53-55 Victoria STREET

Service Station

Regulation under CLM Act not required

-31.91015653

152.4659073

TAREN POINT

Former Oyster Farm

Part 2R Alexander Avenue and part 98 Woodlands ROAD

Other Industry

Contamination was addressed via the planning process (EP&A Act)

-34.01714802

151.1252694

TAREN POINT

Former Oyster Farmer

1A Atkinson ROAD

Other Industry

Regulation under CLM Act not required

-34.02081803

151.1283282

TAREN POINT

Former manufacturing site

46-50 Bay ROAD

Other Industry

Regulation under CLM Act not required

-34.0236184

151.1231649

TAREN POINT

Mangrove Lane Cycle pathway

Mangrove LANE

Unclassified

Regulation under CLM Act not required

-34.02404025

151.1324783

TAREN POINT

Caltex Service Station

114 Taren Point ROAD

Service Station

Regulation under CLM Act not required

-34.02065958

151.1218938

TAREN POINT

Shell Coles Express Service Station

99-103 Parraweena ROAD

Service Station

Regulation under CLM Act not required

-34.02630233

151.1200897

TAREN POINT

Redevelopment Site

25 Bay ROAD

Landfill

Regulation under CLM Act not required

-34.02119591

151.1274727

TELARAH

Former Ausgrid Depot

Green STREET

Other Industry

Regulation under CLM Act not required

-32.7276446

151.5269745

List current as at 8 March 2022

111 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

TELARAH

ACIRL

5 Junction STREET

Other Industry

Regulation under CLM Act not required

-32.73457183

151.5400128

TEMORA

Woolworths Caltex Temora

98-100 Hoskins STREET

Service Station

Regulation under CLM Act not required

-34.44324584

147.5318667

TEMORA

Former Temora Roundhouse

Corner Victoria and Camp STREET

Unclassified

Regulation under CLM Act not required

-34.450492

147.528955

TEMPE

Tempe Depot

1a Gannon STREET

Other Petroleum

Regulation under CLM Act not required

-33.92408255

151.1596469

TEMPE

Caltex Service Station

775 Princes HIGHWAY

Service Station

Contamination currently regulated under CLM Act

-33.9253681

151.1596532

TEMPE

Former Tempe Tip

South STREET

Landfill

Contamination currently regulated under CLM Act

-33.92558642

151.1667178

TEMPE

Railcorp Site Renwick Street

Renwick STREET

Other Industry

Regulation under CLM Act not required

-33.91997709

151.1576058

TENTERFIELD

United Tenterfield Service Station

94 Rouse STREET

Service Station

Under assessment

-29.06260969

152.0168305

TERALBA

Lake Macquarie Teralba Sanitary Depot

Griffen ROAD

Landfill

Regulation under CLM Act not required

-32.9372059

151.6214528

TERALBA

Lucky's Scrap Metal Yard

21 Racecourse ROAD

Metal Industry

Contamination currently regulated under CLM Act

-32.946854

151.617083

TERANIA CREEK

Former Izzards Cattle Tick Dip

Wallace ROAD

Cattle Dip

Contamination formerly regulated under the CLM Act

-28.64999469

153.2788615

THE ENTRANCE NORTH

The Entrance North Beach (Crown Reserve)

25CR Hargraves STREET

Landfill

Under assessment

-33.337535

151.504779

THE ROCKS

Dawes Point Park

Hickson ROAD

Other Industry

Regulation under CLM Act not required

-33.855334

151.209726

THIRLMERE

Thirlmere Rail Heritage Museum

10 Barbour ROAD

Other Industry

Regulation under CLM Act not required

-34.20689245

150.5693902

THORNLEIGH

Caltex Thornleigh Service Station

192-198 Pennant Hills (Cnr Duffy Ave) ROAD

Service Station

Regulation under CLM Act not required

-33.72660793

151.08364

List current as at 8 March 2022

112 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

THORNLEIGH

Coles Express Service Station Thornleigh

188 - 190 Pennant Hills ROAD

Service Station

Regulation under CLM Act not required

-33.72502184

151.0850569

THORNTON

Energy Australia Thornton Pole Yard

55 Weakleys DRIVE

Other Industry

Regulation under CLM Act not required

-32.79973875

151.6374998

TIGHES HILL

Holcim Australia Cement Batching Plant

340 Industrial DRIVE

Other Industry

Regulation under CLM Act not required

-32.90532418

151.7574857

TIGHES HILL

SRA Land

73 Elizabeth STREET

Unclassified

Regulation under CLM Act not required

-32.90795794

151.754631

TIGHES HILL

Former Ampol Depot

94 Elizabeth STREET

Other Petroleum

Regulation under CLM Act not required

-32.90658137

151.757239

TIGHES HILL

Former Mobil Terminal

110 Elizabeth STREET

Other Petroleum

Contamination formerly regulated under the CLM Act

-32.90600406

151.7586907

TOCUMWAL

Former Mobil Depot

250 Murray STREET

Other Petroleum

Regulation under CLM Act not required

-35.79180653

145.5648214

TOCUMWAL

Former Mobil Depot

79-83 Deniliquin ROAD

Other Petroleum

Regulation under CLM Act not required

-35.80914914

145.5585528

TOMAGO

Balcombe Sweat Furnace

26 Laverick AVENUE

Metal Industry

Regulation under CLM Act not required

-32.82557395

151.7056416

TOMAGO

Former Hydromet Site

25 School DRIVE

Metal Industry

Under assessment

-32.8301553

151.7300603

TOMAGO

RZM Site - Tomago

1877 Pacific HIGHWAY

Other Industry

Regulation under CLM Act not required

-32.81419433

151.6985159

TOMERONG

Log Cabin Service Station (United Petroleum)

D1300 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-35.01820959

150.5779687

TOONGABBIE

7-Eleven (Former Mobil) Service Station Toongabbie

3 Metella ROAD

Service Station

Regulation under CLM Act not required

-33.78692357

150.9462837

TOORMINA

Caltex Service Station

2 Minorca PLACE

Service Station

Regulation under CLM Act not required

-30.35229568

153.0906606

TORONTO

Coles XP (Former Mobil) Toronto Service Station

133 - 137 Cary (Cnr Thorne St) STREET

Service Station

Regulation under CLM Act not required

-33.01187681

151.5930879

List current as at 8 March 2022

113 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

TORONTO

BP Toronto Service Station

132 Cary (Cnr Donnelly Ave) STREET

Service Station

Regulation under CLM Act not required

-33.01144673

151.5937863

TORONTO

Toronto Hotel

74 Victory PARADE

Unclassified

Regulation under CLM Act not required

-33.01214835

151.5958127

TORONTO

Caltex Service Station

147 Cary STREET

Service Station

Regulation under CLM Act not required

-33.01288007

151.5928388

TORONTO

155B Brighton Avenue, Toronto NSW 2283

155B Brighton AVENUE

Other Industry

Under assessment

-33.014912

151.59974

TOUKLEY

Former Shell Toukley Autoport

211 Main ROAD

Service Station

Regulation under CLM Act not required

-33.26383791

151.5386268

TOUKLEY

7-Eleven Australia

287 Main ROAD

Service Station

Regulation under CLM Act not required

-33.26469166

151.5462414

TRANGIE

Caltex Service Station

(Mitchell Hwy) 76 Narromine STREET

Service Station

Regulation under CLM Act not required

-32.03234676

147.985164

TUGGERAH

BP Tuggerah

100 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.30578167

151.4198083

TUMBARUMBA

Former Caltex Depot

150 Albury STREET

Other Petroleum

Regulation under CLM Act not required

-35.77024081

147.9927182

TUMBI UMBI

Former Tumbi Landfill

140 Bellevue ROAD

Landfill

Regulation under CLM Act not required

-33.3993472

151.456471

TUMUT

CSR Blue Dam

Jepsen AVENUE

Other Industry

Regulation under CLM Act not required

-35.30098337

148.1958308

TUMUT

CSR Railway cutting

Jepsen AVENUE

Unclassified

Regulation under CLM Act not required

-35.30422002

148.1942579

TUMUT

Former Telstra Depot

22-26 Carey STREET

Other Industry

Regulation under CLM Act not required

-35.29873079

148.2191122

TUNCESTER

Asbestos Waste Burial Site

13 Rifle Range ROAD

Other Industry

Contamination currently regulated under CLM Act

-28.79939255

153.2193708

TUROSS HEAD

Tern Inn Restaurant (abandoned UPSS)

2 Trafalgar ROAD

Service Station

Regulation under CLM Act not required

-36.05871059

150.1308443

List current as at 8 March 2022

114 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

TURRAMURRA

7-Eleven (former Mobil) Service Station Turramurra

1408 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.73326389

151.1264194

TURRAMURRA

Woolworths Service Station

1233 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.73317594

151.1313195

TURRELLA

Tulloch Australia Pty Ltd

61 Turrella STREET

Chemical Industry

Contamination currently regulated under CLM Act

-33.92857213

151.1475387

TWEED HEADS

Former Mobil Quix Service Station

60 MINJUNGBAL DRIVE

Service Station

Contamination formerly regulated under the CLM Act

-28.20143775

153.5445381

TWEED HEADS

Francis Street Road Reserve adjacent to 79-81 Wharf Street, Tweed Heads

79-81 Wharf STREET

Other Petroleum

Regulation under CLM Act not required

-28.17351959

153.542262

TWEED HEADS

Tweed Heads Slipway

8 Terranora TERRACE

Landfill

Under assessment

-28.180667

153.541125

TWEED HEADS SOUTH

Former BP Depot

142 Minjungbal DRIVE

Other Petroleum

Regulation under CLM Act not required

-28.20860702

153.5455932

TWEED HEADS SOUTH

Coles Express Service Station

Corner Minjungbal Drive and Heffron STREET

Service Station

Regulation under CLM Act not required

-28.19459987

153.5419978

TWEED HEADS SOUTH

Woolworths Plus Petrol

98-102 Pacific (100 Minjungbal Drive) HIGHWAY

Service Station

Regulation under CLM Act not required

-28.20488521

153.5448675

TWEED HEADS WEST

Caltex Service Station

96 to 98 Kennedy DRIVE

Service Station

Regulation under CLM Act not required

-28.1871486

153.5229866

TYAGARAH

Tyagarah Airstrip

25 Staceys WAY

Other Petroleum

Regulation under CLM Act not required

-28.59511995

153.546834

ULAN

Ulan Coal Mine

4505 Ulan ROAD

Other Industry

Regulation under CLM Act not required

-32.25620603

149.7558075

ULLADULLA

Coles Express Ulladulla

153 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-35.36288274

150.47272

ULLADULLA

Woolworths Petrol Station

155-157 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-35.36316263

150.4725668

ULLADULLA

Caltex Service Station

62A Deering Street, corner Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-35.36276828

150.473578

List current as at 8 March 2022

115 of 129


Suburb

SiteName

ULTIMO

Shell Coles Express Service Station

UNANDERRA

Address

ManagementClass

Latitude

Longitude

Service Station

Regulation under CLM Act not required

-33.88138825

151.1966791

Endeavour Energy Springhill Field Service Centre 195 Five Island ROAD

Other Industry

Regulation under CLM Act not required

-34.45837706

150.8598825

UNANDERRA

BlueScope Stainless Steel

13 Marley PLACE

Metal Industry

Contamination currently regulated under CLM Act

-34.44959798

150.8571632

UNANDERRA

Unanderra Weekend Detention Centre

34-40 Lady Penryhn DRIVE

Landfill

Regulation under CLM Act not required

-34.4620226

150.8473821

UNANDERRA

Veolia Environmental Services

9 Waynote PLACE

Other Industry

Regulation under CLM Act not required

-34.46042393

150.863232

UNANDERRA

Caltex Service Station

86-98 Princes HIGHWAY

Service Station

Regulation under CLM Act not required

-34.45414951

150.845165

UNANDERRA

Former Prime Service Station and adjoining lands

41-49 Princes HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-34.45056105

150.8490833

UNANDERRA

DGL Environmental Pty Ltd

201 Five Islands ROAD

Metal Industry

Under assessment

-34.453808

150.855247

URALLA

Caltex Service Station

103 Bridge STREET

Service Station

Regulation under CLM Act not required

-30.64524911

151.4934484

URALLA

Phoenix Foundry

44 Duke STREET

Metal Industry

Regulation under CLM Act not required

-30.65093272

151.5004479

URANQUINTY

Former Caltex Depot Kapooka (Wagga Wagga)

6876 Olympic (Uranquinty Rd) HIGHWAY

Service Station

Regulation under CLM Act not required

-35.15319793

147.3085469

URUNGA

Former Antimony Process plant

Hillside DRIVE

Chemical Industry

Contamination currently regulated under CLM Act

-30.50422942

153.0132011

VALENTINE

BP Express Service Station

855 Macquarie DRIVE

Service Station

Regulation under CLM Act not required

-33.00801109

151.6425806

VALENTINE

Valentine Public School

Tallawalla ROAD

Unclassified

Regulation under CLM Act not required

-33.0091613

151.6423231

VALLA

BP Nambucca Heads (Travel Centre and Truckstop)

2 Corkwood ROAD

Other Industry

Regulation under CLM Act not required

-30.628134

152.972702

List current as at 8 March 2022

387-429 Wattle STREET

ContaminationActivityType

116 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

VILLAWOOD

Nepotian (Former Toll) Site

110A Christina ROAD

Other Industry

Under preliminary investigation order

-33.87919117

150.9812193

VILLAWOOD

Former Defence Site

29 Biloela STREET

Landfill

Regulation under CLM Act not required

-33.88782978

150.9886275

VILLAWOOD

Former Siemens/Westinghouse

49 Miowera ROAD

Other Industry

Contamination formerly regulated under the CLM Act

-33.87641909

150.9836746

VILLAWOOD

Former Orica Crop Care

2 Christina ROAD

Chemical Industry

Contamination formerly regulated under the CLM Act

-33.880329

150.9896329

VILLAWOOD

PPG Industries

9 Birmingham AVENUE

Chemical Industry

Regulation under CLM Act not required

-33.87800757

150.9887929

VILLAWOOD

Former Electrical Component Manufacturer

66 Christina ROAD

Other Industry

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.88018315

150.9838773

VILLAWOOD

Ettason Villawood Site

2A Birmingham AVENUE

Chemical Industry

Regulation under CLM Act not required

-33.87877335

150.9827722

VINEYARD

Shell Coles Express Service Station

731 Windsor ROAD

Service Station

Regulation under CLM Act not required

-33.65780463

150.8753245

WAGGA WAGGA

Caltex Service Station

170 Fitzmaurice STREET

Service Station

Regulation under CLM Act not required

-35.10289587

147.3679002

WAGGA WAGGA

Former BP Service Station

31 Bourke STREET

Service Station

Regulation under CLM Act not required

-35.12626628

147.3547199

WAGGA WAGGA

Caltex (former Mobil) Service Station

106 Edward STREET

Service Station

Regulation under CLM Act not required

-35.11910909

147.3682364

WAGGA WAGGA

Former Caltex Depot

60 Lake Albert DRIVE

Service Station

Regulation under CLM Act not required

-35.12316794

147.37724

WAGGA WAGGA

Former Mobil Depot Wagga Wagga

97-99 Coleman STREET

Other Petroleum

Regulation under CLM Act not required

-35.12173871

147.3576651

WAGGA WAGGA

Ashmont Autoport

Cnr Tobruk Street and Bardia STREET

Service Station

Regulation under CLM Act not required

-35.12517373

147.329919

WAGGA WAGGA

Former Caltex Service Station

343 Hammond AVENUE

Service Station

Regulation under CLM Act not required

-35.12420793

147.4157959

List current as at 8 March 2022

117 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

WAGGA WAGGA

Caltex Service Station

56 - 60 Docker St STREET

Service Station

Regulation under CLM Act not required

-35.11737947

147.3558145

WAGGA WAGGA

Former Iron Foundry

212-230 Hammond STREET

Metal Industry

Regulation under CLM Act not required

-35.12605478

147.4045461

WAGGA WAGGA

Coles Express Wagga Wagga

353-355 Edward STREET

Service Station

Regulation under CLM Act not required

-35.11606625

147.3509339

WAGGA WAGGA

Former Wiradjuri landfill

Narrung STREET

Landfill

Under assessment

-35.09628532

147.3619535

WAGGA WAGGA

Former Gasworks

54 Chaston STREET

Gasworks

Ongoing maintenance required to manage residual contamination (CLM Act)

-35.12262069

147.3482778

WAGGA WAGGA

Former Gasworks

Cnr Tarcutta Street and Cross STREET

Gasworks

Ongoing maintenance required to manage residual contamination (CLM Act)

-35.10871183

147.3737933

WAGGA WAGGA

BP Wagga Wagga

180 Edward STREET

Service Station

Regulation under CLM Act not required

-35.11850802

147.3639619

WAGGA WAGGA

Former Dry Cleaning Facility

183 Fitzmaurice STREET

Other Industry

Contamination currently regulated under CLM Act

-35.10209987

147.3683852

WAHROONGA

Coles Express Wahroonga

1601 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.71945571

151.1163002

WAHROONGA

7-Eleven Service Station

1579 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.71974617

151.1168106

WAITARA

Caltex Service Station

59-61 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.71064349

151.1024644

WALGETT

Former Shell Depot

Castlereagh HIGHWAY

Other Petroleum

Regulation under CLM Act not required

-30.00861179

148.1239938

WALLERAWANG

Wallerawang Power Station

1 Main STREET

Other Petroleum

Regulation under CLM Act not required

-33.40339296

150.0855101

WALLERAWANG

Lidsdale Coal Loading Facility

Main STREET

Other Industry

Regulation under CLM Act not required

-33.39996523

150.0737717

WALLSEND

Caltex Maryland Service Station Wallsend 41 Minmi ROAD

Service Station

Regulation under CLM Act not required

-32.88967866

151.6619253

List current as at 8 March 2022

118 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

WALLSEND

Coles Express Wallsend East

15 Thomas STREET

Service Station

Regulation under CLM Act not required

-32.90719444

151.6693426

WALLSEND

OneSteel Recycling

64-80 Sandgate ROAD

Metal Industry

Regulation under CLM Act not required

-32.89425477

151.6799648

WALLSEND

Ausgrid Wallsend Depot

Abbott STREET

Other Industry

Regulation under CLM Act not required

-32.90162796

151.6857267

WALLSEND

Cnr of Douglas Street and 111 Newcastle Road Wallsend

111 Newcastle ROAD

Metal Industry

Regulation under CLM Act not required

-32.90416617

151.6832227

WAMBERAL

Caltex Service Station

654 The Entrance ROAD

Service Station

Regulation under CLM Act not required

-33.42338668

151.4375685

WANGI WANGI

Myuna Colliery

Wangi Point ROAD

Other Industry

Regulation under CLM Act not required

-33.06139532

151.5697186

WARATAH

Waratah Area Health

Turton ROAD

Unclassified

Regulation under CLM Act not required

-32.90961233

151.7260867

WARATAH

Waratah former Gasworks

Turton and Georgetown ROADS

Gasworks

Contamination currently regulated under CLM Act

-32.90591166

151.7272715

WARDELL

Nancy's Cattle Dip, Thurgates Lane, Wardell

Thurgates LANE

Cattle Dip

Regulation under CLM Act not required

-28.9540212

153.4274874

WARILLA

Woolworths Petrol Warilla

43 -57 Shellharbour ROAD

Service Station

Regulation under CLM Act not required

-34.5470966

150.863748

WARKWORTH

Emulsion Plant, Dyno Nobel Asia Pacific Pty Ltd

186 Long Point ROAD

Chemical Industry

Regulation under CLM Act not required

-32.5781708

151.0834387

WARKWORTH

United Colliery

Jerrys Plains ROAD

Other Industry

Regulation under CLM Act not required

-32.5654356

150.9916698

WARNERS BAY

Caltex Service Station

55 King STREET

Service Station

Regulation under CLM Act not required

-32.97418806

151.6476184

WARNERS BAY

7-Eleven (former Mobil) Service Station

393 Hillsborough ROAD

Service Station

Regulation under CLM Act not required

-32.9659363

151.6543264

WARNERS BAY

Historically Filled Land

41-43 Charles STREET

Unclassified

Regulation under CLM Act not required

-32.97340461

151.6464383

List current as at 8 March 2022

119 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

WARNERVALE

Former Timber Treatment Plant

Aldenham and Railway ROADS

Other Industry

Contamination formerly regulated under the CLM Act

-33.24732018

151.4469037

WARRAGAMBA

Warragamba Dam Viewing Platform

Eighteenth STREET

Unclassified

Regulation under CLM Act not required

-33.88545624

150.6016219

WARRAGAMBA

Megarrity's Creek Site

Weir ROAD

Unclassified

Regulation under CLM Act not required

-33.8873146

150.5967305

WARRAWONG

Caltex Service Station

75-77 King STREET

Service Station

Regulation under CLM Act not required

-34.49037817

150.888802

WARREN

Former Shell Depot

8 Dubbo STREET

Other Petroleum

Regulation under CLM Act not required

-31.69379262

147.8308088

WARREN

Caltex Warren Service Station

1 Coonamble ROAD

Service Station

Regulation under CLM Act not required

-31.69508383

147.8405578

WARREN

Former Mobil Warren Depot

16 Dubbo STREET

Other Petroleum

Contamination currently regulated under CLM Act

-31.6943058

147.8314606

WARWICK FARM

Warwick Farm Public School

95 Lawrence Hargrave ROAD

Unclassified

Regulation under CLM Act not required

-33.90978695

150.9291852

WATERLOO

Proposed Construction Site

2 John STREET

Other Industry

Regulation under CLM Act not required

-33.89989686

151.2010324

WATERLOO

Waverley Woollahra Process Plant

355 Botany ROAD

Other Industry

Regulation under CLM Act not required

-33.9063092

151.2042672

WATERLOO

Shell Coles Express Service Station

867-877 South Dowling STREET

Service Station

Regulation under CLM Act not required

-33.90179774

151.2143789

WATERLOO

Lawrence Dry Cleaners

887-893 Bourke STREET

Unclassified

Contamination currently regulated under CLM Act

-33.89897433

151.2101436

WATERLOO

Divercity Waterloo Blocks C & D and adjacent plaza / park

1, 9, 13, 13A, 13B and 23 Archibald Avenue, 20 Dunkerley Place and 850 Bourke STREET

Other Industry

Regulation under CLM Act not required

-33.90200158

151.2098496

WATERLOO

Iconic (Former Chubb Factory) Waterloo

830-838 Elizabeth STREET

Other Industry

Regulation under CLM Act not required

-33.90227718

151.2060305

WATERLOO

22-24 Archibald Avenue

22-24 Archibald AVENUE

Other Petroleum

Regulation under CLM Act not required

-33.90206938

151.2139293

List current as at 8 March 2022

120 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

WAUCHOPE

Expressway Spares UST

3 Sancrox ROAD

Other Petroleum

Regulation under CLM Act not required

-31.44163879

152.8231104

WAUCHOPE

Former Shell Depot

56-64 High STREET

Other Petroleum

Regulation under CLM Act not required

-31.45804845

152.7314151

WAUCHOPE

Wauchope Service Station

57 High STREET

Service Station

Regulation under CLM Act not required

-31.45737022

152.7305018

WAUCHOPE

Former Timber Treatment Site

Blackbutt DRIVE

Other Industry

Regulation under CLM Act not required

-31.46575645

152.7228555

WAUCHOPE

Shell Coles Express Service Station

64 High STREET

Service Station

Regulation under CLM Act not required

-31.45764495

152.7315975

WAUCHOPE

Wauchope Public Primary School

2 Waugh STREET

Unclassified

Regulation under CLM Act not required

-31.45602953

152.7295059

WAVERTON

SRA Land

95 Bay ROAD

Unclassified

Contamination formerly regulated under the CLM Act

-33.83716728

151.1969497

WAVERTON

Berry's Bay Woodley's Marina

1 Balls Head DRIVE

Other Industry

Contamination formerly regulated under the POEO Act

-33.84441851

151.1947433

WAVERTON

Oyster Cove AGL

2 King STREET

Gasworks

Ongoing maintenance required to manage residual contamination (CLM Act)

-33.83637995

151.193541

WEE JASPER

Wee Jasper Tavern

6499 Wee Jasper ROAD

Other Industry

Regulation under CLM Act not required

-35.10992483

148.679428

WELLINGTON

Former Caltex Service Station

124-128 Lee STREET

Service Station

Regulation under CLM Act not required

-32.55082729

148.9411537

WELLINGTON

BP Wellington Service Station

35A Maxwell STREET

Service Station

Under assessment

-32.55835121

148.9447284

WELLINGTON

Woolworths Petrol Wellington

79 Lee STREET

Service Station

Regulation under CLM Act not required

-32.54874227

148.9408531

WELLINGTON

The Wash Shed (Laundromat)

67 Gobolion STREET

Gasworks

Under assessment

-32.545494

-32.545494

WELLINGTON

Police Citizens Youth Club (PCYC)

69 Gobolion STREET

Gasworks

Under assessment

-32.5456

148.944004

List current as at 8 March 2022

121 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

WELLINGTON

J&J Mechanical

1 Warrawee STREET

Gasworks

Under assessment

WENTWORTH

Caltex - Wentworth

110 Adams STREET

Service Station

Regulation under CLM Act not required

WENTWORTH FALLS

Bodington Hospital

Bodington DRIVE

Unclassified

Contamination formerly regulated under the CLM Act

WENTWORTH POINT

RMS Eastern Precinct

3-7 Burroway ROAD

Other Petroleum

WENTWORTH POINT

Former TNT Express

23 Bennelong PARKWAY

WENTWORTHVILLE

Former Workshop

WERRINGTON

Latitude

Longitude

-32.545802

148.943318

-34.1024927

141.9160539

-33.73204611

150.3874554

Regulation under CLM Act not required

-33.8233882

151.0815668

Other Petroleum

Regulation under CLM Act not required

-33.83115118

151.0726636

2 Rawson Rd and 8 Barfil CRESCENT

Unclassified

Regulation under CLM Act not required

-33.81568808

150.9671853

Caltex Service Station

Cnr Dunheved Rd and Henry Lawson DRIVE

Service Station

Regulation under CLM Act not required

-33.74577725

150.7409877

WERRINGTON

Claremont Meadows Former landfill

Gipps STREET

Landfill

Regulation under CLM Act not required

-33.77341076

150.7557628

WERRINGTON COUNTY

7-Eleven Werrington

Lot 122 Dunheved ROAD

Service Station

Regulation under CLM Act not required

-33.74699408

150.7428609

WEST BALLINA

Caltex Big Prawn Service Station

Pacific HIGHWAY

Service Station

Contamination formerly regulated under the CLM Act

-28.86374913

153.5321482

WEST GOSFORD

Caltex Service Station

283 Manns ROAD

Service Station

Regulation under CLM Act not required

-33.41659727

151.325219

WEST GOSFORD

Caltex Service Station

69-71 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.42729985

151.3214621

WEST GOSFORD

Caltex Service Station

30a Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.42778813

151.3190581

WEST GOSFORD

Adcock Memorial Park

Central Coast HIGHWAY

Landfill

Contamination currently regulated under CLM Act

-33.42963075

151.3273331

WEST NOWRA

Endeavour Energy Nowra Field Service Centre

20 Depot ROAD

Other Industry

Regulation under CLM Act not required

-34.88993085

150.5878854

List current as at 8 March 2022

122 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

WEST PENNANT HILLS

7-Eleven (former Mobil) Service Station

552 Pennant Hills ROAD

Service Station

Regulation under CLM Act not required

-33.74686545

151.0508067

WEST RYDE

7-Eleven (former Mobil) Service Station

917 Victoria ROAD

Service Station

Regulation under CLM Act not required

-33.80921103

151.0932917

WEST RYDE

Pfizer Australia Pty Ltd

38-42 Wharf ROAD

Chemical Industry

Regulation under CLM Act not required

-33.81021085

151.0693631

WEST RYDE

Reckitt Benckiser

44 Wharf ROAD

Chemical Industry

Regulation under CLM Act not required

-33.81172205

151.0692752

WEST RYDE

JHM Property Development

2A Mellor STREET

Other Industry

Regulation under CLM Act not required

-33.81207534

151.094598

WEST TAMWORTH

Woolworths Petrol

119 Bridge STREET

Service Station

Regulation under CLM Act not required

-31.09358262

150.9167693

WEST WALLSEND

West Wallsend Cemetery

6 Cemetery ROAD

Unclassified

Regulation under CLM Act not required

-32.902828

151.570636

WEST WYALONG

Lowes Petroleum (Former BP) Depot West Wyalong

Compton (formerly known as Town Bypass/Railway Road) ROAD

Other Petroleum

Regulation under CLM Act not required

-33.93440247

147.2154596

WEST WYALONG

Caltex Depot

(Wyalong By-pass Rd) Lot 1-3 Showground ROAD

Service Station

Regulation under CLM Act not required

-33.92580863

147.1978504

WEST WYALONG

Former Mobil Depot

104 Compton ROAD

Other Petroleum

Regulation under CLM Act not required

-33.93449194

147.2147948

WESTON

Illegal Dumping Site

Corner Kline Street & First STREET

Unclassified

Regulation under CLM Act not required

-32.81367986

151.4551507

WETHERILL PARK

Former Fuel Storage Depot

200-212 Cowpasture ROAD

Other Petroleum

Regulation under CLM Act not required

-33.84568871

150.8764012

WETHERILL PARK

Sims Wetherill Park

35-37 Frank STREET

Metal Industry

Regulation under CLM Act not required

-33.84056122

150.9086265

WETHERILL PARK

Shell Coles Express Service Station

565 Polding STREET

Service Station

Regulation under CLM Act not required

-33.8569731

150.8992804

WETHERILL PARK

Cleanaway (Formerly Nationwide Oil) Wetherill Park

6 Davis ROAD

Other Industry

Regulation under CLM Act not required

-33.83770038

150.9045197

List current as at 8 March 2022

123 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

WETHERILL PARK

BOC Sydney Operations Centre

428-440 Victoria STREET

Chemical Industry

Regulation being finalised

-33.84375988

150.8960027

WETHERILL PARK

Camide Former Landfill

Newton ROAD

Landfill

Regulation under CLM Act not required

-33.83898879

150.8963813

WETHERILL PARK

Fairfield Sustainable Resource Centre

Corner Hassall Street and Widemere ROAD

Other Industry

Under assessment

-33.838947

150.914593

WICKHAM

Caltex Terminal and "Building 33" on offsite adjacent land

156 Hannell Street and 33 Annie STREET

Other Petroleum

Contamination currently regulated under CLM Act

-32.9153413

151.7560062

WICKHAM

Former Warehouse

10 Dangar STREET

Unclassified

Regulation under CLM Act not required

-32.92383206

151.759761

WICKHAM

Former Factory

57 Annie STREET

Other Industry

Regulation under CLM Act not required

-32.91524827

151.7539893

WICKHAM

Railcorp Wickham

50 Railway STREET

Other Industry

Regulation under CLM Act not required

-32.9210433

151.7544687

WICKHAM

Fuchs Lubricants Wickham

2 Holland STREET

Other Industry

Contamination currently regulated under CLM Act

-32.9214709

151.7556928

WILBERFORCE

Former Drum Reconditioners

12-14 Box AVENUE

Other Industry

Contamination formerly regulated under the CLM Act

-33.5453884

150.8587934

WILBERFORCE

Former Solvent Recycling Site

13 Box AVENUE

Chemical Industry

Regulation under CLM Act not required

-33.54557427

150.8577006

WILEY PARK

Sydney Water Property

1B Hillcrest STREET

Other Industry

Regulation under CLM Act not required

-33.92391634

151.0676256

WILLIAMTOWN

Hunter Land Effluent Pond

38 Cabbage Tree ROAD

Other Industry

Regulation under CLM Act not required

-32.80750069

151.8310107

WILLOUGHBY

Shell Coles Express Service Station

616-626 Willoughby ROAD

Service Station

Regulation under CLM Act not required

-33.80593769

151.1988559

WILLOUGHBY

Caltex Service Station

157 Penhur STREET

Service Station

Regulation under CLM Act not required

-33.79793513

151.1981926

WILLOUGHBY

BP Willoughby Express Tower

498 Willoughby STREET

Service Station

Contamination currently regulated under POEO Act

-33.81022918

151.199315

List current as at 8 March 2022

124 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

WILLOUGHBY

Bicentennial Reserve, Flat Rock Gully, Willoughby Leisure Centre

Small STREET

Other Industry

Under assessment

WILLOUGHBY EAST

Willoughby Bus Depot

Corner Ann Street and Stan STREET

Other Industry

WILTON

Condell Park Homestead

(Part Lot 17 DP 270536) Condell Park ROAD

WINDANG

Caltex Service Station

WINDSOR

Former Caltex Service Station

WINDSOR

Latitude

Longitude

-33.811902

151.202797

Regulation under CLM Act not required

-33.7982569

151.2038993

Unclassified

Regulation under CLM Act not required

-34.21910141

150.6837962

244-248 Windang ROAD

Service Station

Regulation under CLM Act not required

-34.5274434

150.8691161

46-52 Macquarie STREET

Service Station

Regulation under CLM Act not required

-33.60783315

150.8213428

Former Caltex Windsor Depot and Service 48-50 Mileham STREET Station

Service Station

Regulation under CLM Act not required

-33.61538627

150.8157517

WINDSOR

Woolworths (former Caltex) Service Station

Cnr Macquarie Street & Baker STREET

Service Station

Regulation under CLM Act not required

-33.60569346

150.8232803

WINDSOR

Former Fire Station Windsor

19 Fitzgerald STREET

Other Industry

Under assessment

-33.6064873

150.8199089

WINDSOR

Windsor Zone Substation

56-60 Macquarie STREET

Other Industry

Under assessment

-33.608114

150.820854

WINGHAM

Former Caltex Service Station

1036-1038 Wingham ROAD

Service Station

Regulation under CLM Act not required

-31.86236594

152.3805752

WINGHAM

Bogas Service Station

Cnr Primrose Street and Isabella STREET

Service Station

Regulation under CLM Act not required

-31.86833656

152.3716346

WINMALEE

Prime Winmalee Service Station

281 Hawkesbury ROAD

Service Station

Regulation under CLM Act not required

-33.68223276

150.5997203

WIRLINGA

Former Liquid Waste Disposal Facility

704 Riverina ROAD

Unclassified

Regulation under CLM Act not required

-36.07103958

147.0193522

WOLLI CREEK

Former Ausgrid Substation 10061

13 Gertrude STREET

Other Industry

Regulation under CLM Act not required

-33.93364031

151.1543818

WOLLONGONG

Redevelopment site

33 - 39 Beatson STREET

Other Petroleum

Regulation under CLM Act not required

-34.43196083

150.8976661

List current as at 8 March 2022

125 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

WOLLONGONG

Caltex Service Station

9 Flinders STREET

Service Station

Regulation under CLM Act not required

-34.41505616

150.8932515

WOLLONGONG

Greenhouse Park

Springhill ROAD

Landfill

Contamination currently regulated under CLM Act

-34.44119949

150.8931764

WOLLONGONG

Former Wollongong Gasworks

120 and 122 Smith STREET

Gasworks

Regulation under CLM Act not required

-34.42030173

150.8906745

WOLLONGONG

Woolworths Service Station

425 Crown STREET

Service Station

Contamination currently regulated under CLM Act

-34.42637378

150.8799288

WOLLONGONG

Wollongong Harbour Central Spur

Off Endeavour DRIVE

Other Petroleum

Regulation under CLM Act not required

-34.42066879

150.906821

WOODBURN

Caltex Service Station

129 River STREET

Service Station

Regulation under CLM Act not required

-29.07206887

153.3409769

WOODBURN

Crown Reserve 88037 Woodburn

Pacific HIGHWAY

Landfill

Regulation under CLM Act not required

-29.06580577

153.3541886

WOOLGOOLGA

Caltex Woolgoolga Service Station

16 Bosworth ROAD

Service Station

Regulation under CLM Act not required

-30.12569561

153.1946006

WOOLGOOLGA

United Petroleum Service Station(1868 Solitary Islands Way)

56 Clarence STREET

Service Station

Contamination currently regulated under CLM Act

-30.11045544

153.1904609

WOOLLAHRA

Former Service Station

20 Wallis STREET

Service Station

Regulation under CLM Act not required

-33.8901965

151.2372752

WOOLLAHRA

Proposed Jewish Care Centre

7-21 Saber STREET

Unclassified

Regulation under CLM Act not required

-33.8904055

151.2480062

WOOLLAHRA

Caltex Woollahra Service Station

116 Old South Head ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.88959697

151.2553736

WOOLLOOMOOLOO

Former BP Service Station

2 Dowley STREET

Service Station

Contamination being managed via the planning process (EP&A Act)

-33.86940191

151.2218741

WOOLOMIN

Woolomin Gold Rush Store

65 Nundle ROAD

Other Petroleum

Contamination formerly regulated under the CLM Act

-31.30415134

151.149729

WOOLOOWARE

Caltex Service Station

100 Woolooware ROAD

Service Station

Regulation under CLM Act not required

-34.05274635

151.1408413

List current as at 8 March 2022

126 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

WOOLOOWARE

Oyster Farm

Captain Cook DRIVE

Other Industry

Regulation under CLM Act not required

-34.03807914

151.1476055

WOONGARRAH

Former Warnervale Landfill

236-264 Hakone ROAD

Landfill

Regulation under CLM Act not required

-33.2376313

151.464362

WOOTTON

Former Chemical Spill Site

11859 Pacific HIGHWAY

Chemical Industry

Regulation under CLM Act not required

-32.28168548

152.3117819

WOY WOY

Mobil Former Woy Woy Service Station and adjacent land

177-181 Blackwall ROAD

Service Station

Contamination formerly regulated under the CLM Act

-33.49257884

151.3273559

WOY WOY

Barry Robertson Holden

231 Blackwall ROAD

Service Station

Regulation under CLM Act not required

-33.49621068

151.3285128

WOY WOY

Bogas Service Station

66 Memorial AVENUE

Service Station

Contamination currently regulated under CLM Act

-33.5069738

151.3315579

WOY WOY

Rogers Park

Dunban ROAD

Landfill

Regulation under CLM Act not required

-33.50009693

151.3181347

WOY WOY

Austin Butler Memorial Oval

Blackwall ROAD

Landfill

Regulation under CLM Act not required

-33.48672201

151.3283032

WOY WOY

James Browne Oval

Welcome STREET

Landfill

Regulation under CLM Act not required

-33.49720596

151.3242986

WOY WOY

7-Eleven Service Station

Corner Rawson and Ocean Beach ROADS

Service Station

Under assessment

-33.493563

151.320598

WYALONG

Caltex Service Station

50 Neeld (Newell Highway) STREET

Service Station

Regulation under CLM Act not required

-33.92665025

147.2446546

WYOMING

Caltex Service Station Wyoming

465 Pacific HIGHWAY

Service Station

Regulation under CLM Act not required

-33.40945391

151.3499812

WYONG

Wyong Bayer/Kemcon

16 Lucca ROAD

Chemical Industry

Contamination formerly regulated under the CLM Act

-33.26192339

151.4429446

WYONG

Caltex Service Station

M1 Pacific (Northbound) MOTORWAY

Service Station

Regulation under CLM Act not required

-33.25641477

151.4024821

WYONG

Caltex Service Station

M1 Pacific (Southbound) MOTORWAY

Service Station

Regulation under CLM Act not required

-33.25330747

151.4053862

List current as at 8 March 2022

127 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

WYONG

IXOM Facility

8 Pavitt CRESCENT

Other Industry

Regulation under CLM Act not required

-33.26379108

151.4485113

YAGOONA

Galserv Galvanising Services

117-153 Rookwood ROAD

Metal Industry

Contamination currently regulated under POEO Act

-33.89493085

151.0388013

YAGOONA

BP Service Station Potts Hill (Yagoona)

155 Rookwood ROAD

Service Station

Regulation under CLM Act not required

-33.89330525

151.0390969

YAGOONA

7-Eleven (former Mobil) Service Station

519 Hume HIGHWAY

Service Station

Regulation under CLM Act not required

-33.90760623

151.0207783

YAGOONA

Shell Coles Express Service Station

112 Rookwood ROAD

Service Station

Regulation under CLM Act not required

-33.89856213

151.0370458

YAGOONA

Sydney Water Corporation Potts Hill Complex

91 Brunker ROAD

Other Industry

Regulation under CLM Act not required

-33.89887589

151.0289165

YALLAH

Tallawarra Power Station site

Princes HIGHWAY

Unclassified

Ongoing maintenance required to manage residual contamination (CLM Act)

-34.52412143

150.8062159

YAMBA

Caltex Service Station

22 Treelands DRIVE

Service Station

Regulation under CLM Act not required

-29.42701701

153.3279204

YANCO

Former Service Station

14 Main AVENUE

Service Station

Contamination formerly regulated under the CLM Act

-34.60356494

146.4105016

YASS

Caltex Service Station

228 Comur STREET

Service Station

Regulation under CLM Act not required

-34.84440036

148.9140179

YASS

Caltex Service Station

1715 Yass Valley WAY

Service Station

Regulation under CLM Act not required

-34.80708856

148.8824228

YASS

Former Mobil Depot Yass and adjacent land

54-58 Laidlaw STREET

Service Station

Ongoing maintenance required to manage residual contamination (CLM Act)

-34.83252976

148.9068888

YASS

Former Gasworks

Dutton STREET

Gasworks

Contamination currently regulated under CLM Act

-34.83982614

148.9060029

YASS

Transgrid Depot Yass

Perry STREET

Unclassified

Under assessment

-34.86238341

148.9052809

YENNORA

Former Alcoa Australia Rolled Products Facility - Area 3

1 Kiora CRESCENT

Metal Industry

Regulation under CLM Act not required

-33.86568158

150.9649297

List current as at 8 March 2022

128 of 129


Suburb

SiteName

Address

ContaminationActivityType

ManagementClass

Latitude

Longitude

YENNORA

Spicer Axle Australia Manufacturing Facility

205-231 Fairfield ROAD

Other Industry

Regulation under CLM Act not required

-33.85655114

150.9579167

YENNORA

Former Caltex Service Station

137-141 Fairfield STREET

Service Station

Regulation under CLM Act not required

-33.86824768

150.9706137

YENNORA

Former Metal Plant

44 Larra STREET

Metal Industry

Contamination formerly regulated under the CLM Act

-33.86340576

150.9764349

YENNORA

TetraPak Site

6 Foray STREET

Other Industry

Contamination formerly regulated under the CLM Act

-33.8557183

150.9561605

YENNORA

19 Pine Road, Yennora

Pine ROAD

Metal Industry

Contamination currently regulated under CLM Act

-33.86713232

150.9621172

YETHOLME

Yetholme CCA Timber Treatment Plant

351 Eusdale ROAD

Other Industry

Contamination formerly regulated under the CLM Act

-33.45386256

149.8537787

YOUNG

Former Mobil Depot and Service Station Young

149 Lovell STREET

Service Station

Regulation under CLM Act not required

-34.31024587

148.290424

YOUNG

Former Shell Depot

166 Nasmyth STREET

Other Petroleum

Regulation under CLM Act not required

-34.31025192

148.2931008

YOUNG

Former battery recycler

45 Nasmyth STREET

Metal Industry

Contamination currently regulated under CLM Act

-34.31201571

148.306772

YOUNG

Adjacent to former battery recycler

47 Nasmyth STREET

Metal Industry

Contamination formerly regulated under the CLM Act

-34.31176273

148.3064765

YOUNG

Mobil Depot

186 Nasmyth STREET

Other Petroleum

Contamination currently regulated under CLM Act

-34.30954389

148.2908476

YOUNG

Former Caltex Depot

95 Lovell STREET

Service Station

Regulation under CLM Act not required

-34.31127119

148.2955092

ZETLAND

Energy Australia/ Ausgrid Zetland Depot

122 - 138 Joynton AVENUE

Other Industry

Regulation under CLM Act not required

-33.90883116

151.2101184

ZETLAND

Former Goodrich Control Systems, Zetland

84 - 92 Epsom ROAD

Other Industry

Regulation under CLM Act not required

-33.91025707

151.2078048

List current as at 8 March 2022

129 of 129


APPENDIX E

SAFEWORK NSW RECORDS


Frances Kuipers Licensing <licensing@safework.nsw.gov.au> Thursday, 31 March 2022 2:25 PM Frances Kuipers SafeWork NSW: 00677002 –Site Search application – Result found [ ref:_00D281hl6J._5004a7h6FM:ref ] THIS FILE Concord, 160 Burwood Rd - site plan_pdf.html; THIS FILE 160 Burwood Road Concord- Results_pdf.html

From: Sent: To: Subject: Attachments:

Security Classification: Sensitive Personal Please do not amend the subject line of this email Dear Frances Re: Site Search for Schedule 11 Hazardous Chemicals on premises Application – Result found I refer to your application for a Site Search for Schedule 11 Hazardous Chemicals on premises for the following site: 160 Burwood Road Concord NSW 2750 Please find attached copies of the documents that SafeWork NSW holds on record number 35/005234 relating to the storage of Hazardous Chemicals at the above-mentioned premises. If you have any further information or if you have any questions, please use one of the following options, quoting the SafeWork NSW enquiry reference number: 00677002  

Email: licensing@safework.nsw.gov.au Phone: 13 10 50

Kind regards Gabriela Draper Licensing Representative SafeWork NSW | Better Regulation Division Department of Customer Service p- 13 10 50 e- licensing@safework.nsw.gov.au | www.customerservice.nsw.gov.au Level 3, 32 Mann Street, Gosford, NSW 2250 To help protect y our priv acy , Micro so ft Office prev ented auto matic downlo ad o f this picture from the Internet.

1


We are always looking for ways that we can improve our services. You may be contacted by email in the next few weeks to complete a short survey and provide us with your feedback on what we did well and where we can improve. If you do not wish to participate in our surveys, please email us at: licensingQA@customerservice.nsw.gov.au and we will ensure that you are not contacted.

To help protect y Micro so ft Office p auto matic downlo picture from the I

ref:_00D281hl6J._5004a7h6FM:ref

2












































































































































































































































































































































































































APPENDIX F

2014 Report 13188/2-AA


G

EOTECHNIQUE

®

Member of Australian Contaminated Land Consultants Association Inc

PTY LTD ABN 64 002 841 063

Job No: 13188/2 Our Ref: 13188/2-AA 12 September 2014 Nix Anderson Pty Ltd 17 Chuter Street McMahons Point NSW 2060 Attention: Mr R McGuinness Dear Sir re:

Proposed Development Robert Timms Factory Site (Bushell’s) 160 Burwood Road, Concord Contamination Assessment of Soil

This letter report presents the results of a contamination assessment of soils recovered from 10 geotechnical boreholes at 160 Burwood Road, Concord in the local government area of Canada Bay, hereafter referred to as the site. It is understood that the site is proposed for an integrated Residential Community. This contamination assessment was to provide some indications on the contamination status of the sub-surface soil within the site for planning purposes. The site is irregular in shape and covers an area of approximately 4 hectares (ha). OBJECTIVE OF THE ASSESSMENT

The objective of the assessment was to ascertain whether the soils being assessed are likely to present a risk of harm to human health and the environment under the conditions for the proposed high density residential development. SCOPE OF WORK

In order to achieve the objective, the following scope of work was conducted in accordance with our proposal dated 2 May 2014 (Reference Q6616);

Recovery of soil samples from ten (10) boreholes locations in conjunction with a geotechnical investigation also undertaken by Geotechnique Pty Ltd (Geotechnique).

Chemical analysis by National Association of Testing Authorities (NATA) accredited testing laboratories, in accordance with Chains of Custody (COC) prepared by Geotechnique.

Implementation of industry standard quality assurance (QA) and quality control (QC) measures. QA/QC samples were also prepared and forwarded to the laboratories.

Assessment of the laboratory analytical results against current applicable guidelines.

Assessment of field and laboratory QA and QC.

Assessment of the contamination status of the soils. Lemko Place, Penrith NSW 2750 PO Box 880, Penrith NSW 2751 Telephone (02) 422 2700 Facsimile (02) 4722 2777 e-mail: info@geotech.com.au www.geotech.com.au


G EOTECHNIQUE PTY LTD

2 13188/2-AA 160 Burwood Road, Concord

SITE CONDITION th

th

During fieldwork from 7 to 14 August 2014, the site operated as a coffee factory. It consisted of a number of site features including:    

A multi storey factory building An administration building A gas storage area A guardhouse fronting Burwood Road

Open area of the site consisted of bitumen car parks, bitumen or concrete driveways and landscaped areas. There were no obvious ash materials, asbestos sheets / pieces, odour, discolouration of the soils or petroleum hydrocarbon staining on the bare ground surface of the site that would indicate the potential for contamination. The site generally slopes to the east. The adjoining properties: To the north: To the east: To the south: To the west:

Golf course, slopes similarly to the east. Residential land, slopes away from the site. Burwood Road, slopes similarly to the east. Residential land, slopes gently toward the site.

REVIEW OF AVAILABLE INFORMATION AND POTENTIAL FOR CONTAMINATION

SLR Consulting Australia Pty Ltd provided relevant information regarding their environmental investigation of the site (Appendix A). From 11 areas of environmental concern (AEC1 to AEC11), there was a potential for the site to be contaminated with Hydrocarbons, metals, pesticide, asbestos and PCBs. Borehole locations were appropriately located corresponding to the suggested AECs. From interviewing the site supervisor, Ms Kayte Nguyen, Engineering Support Officer from Fresh Food Corporation Pty Ltd, the factory produced coffee from raw coffee bean. There were two main waste products from the process; coffee grounds and caustic solution. While coffee ground removal off site by contractor, the caustic solution which was used to clean the interior of the factory’s machineries was neutralised with acid on site and discharge into the sewer system. Therefore, if the neutralization was not done appropriately or if there was spillage of either the caustic waste or the acid that was used to neutralized it, soil pH within the site could be altered. Bushell’s website provides an article about Bushell’s history (Appendix B). According to the article, Bushell’s purchased the site in 1956. Prior to that, the site was believed to have been occupied by a timber yard. Wood preservatives such as combination of copper, chromium and arsenic could have been used and potentially contaminated the soil. Available aerial photographs (from 1970 to 2014) indicate that the factory appears in all aerial photos. Geotechnical borehole logs of the 10 boreholes that were drilled indicated that fill was encountered at all boreholes up to depth of 5m. The fills could possibly have been imported from unknown sources for levelling and could have been contaminated with a wide range of contaminants. Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

3 13188/2-AA 160 Burwood Road, Concord

FIELD SAMPLING AND LABORATORY TESTING th

th

Field work for the contamination assessment of soils was carried out on 7 to 14 August 2014 in conjunction with a geotechnical investigation. Reference may be made to Report 13188/1 dated 10 September 2014 for details of the geotechnical investigation results. Environmental Scientist and Engineer from Geotechnique were responsible for sampling and logging the sub-surface profile encountered at the ten borehole locations (BH1 to BH10). The boreholes were bored using a truck mounted drilling rig to depth of about 10m. The borehole locations are shown on the attached Drawing No 13188/1-AA1. Reference should be made to the engineering logs (Report 13188/1) for detailed descriptions of the soil profile encountered during field work. Sub-surface materials encountered in the boreholes are summarised below. In particular, asphalt or concrete underlain by road base gravel were encountered BH1, BH6, BH7, BH8 and BH10. Topsoil

The following 6 types of fill were encountered; Type 1: Silty Sand, fine grained, grey, with root fibres, was encountered to depths of 100 millimetres (mm) to 200mm below existing ground level (EGL) at BH2, BH3 and BH4, underlain by type 1 or type 4 fill. Type 2: Silty Clay, medium plasticity, grey, inclusion of sandstone fragments, was encountered to depths of 100 mm below EGL at BH5, underlain by type 3 fill.

Fill

The following 6 types of fill were encountered; Type 1: 200mm to 800mm thick silty Sand, fine grained, brown with clay and gravel, was encountered at BH1, BH3, BH4, BH7, BH8 and BH9. Type 2: 250mm to 1500mm thick silty Clay, medium to high plasticity, grey, trace of ironstone, was encountered at BH1, BH6, BH7, BH9 and BH10. Type 3: 300mm to 2300mm thick sandy Clay, low plasticity, dark brown trace of gravel, was encountered at BH1, BH2, BH3, BH5, BH7 and BH9. Type 4: 1350mm thick silty Sand, fine grained, grey, inclusion of gravel, was encountered at BH2. Type 5: 1200mm thick silty Clay, medium plasticity, grey, inclusion of gravel, was encountered at BH2 and BH7. Type 6: 1300mm thick sand Clay, high plasticity, dark grey, was encountered at BH3. Type 7: 200mm to 300mm thick Sandstone floater, was encountered at BH3 and BH4.

Residual Soil

The following 3 types of natural soil were encountered; Type 1: Silty SAND, fine grained, dark grey was, encountered at BH, BH3, BH4 and BH8. Type 2: Sandy CLAY, medium to high plasticity, brown and grey, was encountered at BH2, BH6 and BH7. Type 3: Silty CLAY, high plasticity, grey, was encountered at BH5, BH9 and BH10.

Bedrock

SANDSTONE, fine to medium grained, grey brown, extremely weathered, low strength.

Based on the contents of the fill materials and the natural soil profiles, it appears that Types 2, 3, 6 and 7 might have originated from construction of the factory; whilst Type 1, 4 and 5 fill materials could have been imported to the site for site levelling purposes. Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

4 13188/2-AA 160 Burwood Road, Concord

The recovered soil samples did not have obvious asbestos sheets / pieces, odour, staining or discolouration that would indicate the potential for contamination. Samples were recovered from the excavated material using a stainless steel trowel, which was decontaminated prior to use to prevent cross contamination. The sampling procedures adopted were as follows; 

Bulk soil samples from boreholes were surfaced using a truck mounted drilling rig, with auger attachment, over the depth interval nominated by the Environmental Scientist/ Engineer. A representative soil sample was recovered directly from the auger, using a decontaminated stainless steel trowel.

To minimise the potential loss of volatiles the soil sample was immediately transferred to a labelled, laboratory supplied, 250ml glass jar and sealed with an airtight, Teflon screw top lid. The fully filled jar was then placed in a chilled container.

Distilled water used for rinsing the trowel during sampling was collected at the completion of field work and placed in a glass bottle supplied by the laboratory. The rinsate water sample was labelled and placed in the chilled container. In order to ensure the analytical performance of the primary laboratory, duplicate and split samples were prepared and kept in labelled laboratory supplied glass jars (acid-washed and solvent-rinsed) sealed with airtight screw Teflon top lids. The fully filled jars were placed in a chilled container. At completion of field sampling the chilled containers were transported to our Penrith office. All the jars and bottles were then transferred to a refrigerator where the temperature is maintained below 4°C. The day after field work, the chilled containers with the trip spike sample were forwarded under COC conditions to the primary laboratory of SGS Environmental Services (SGS) and the secondary laboratory, Envirolab Services Pty Ltd (Envirolab), both NATA accredited. On receipt of the samples the laboratories returned the Sample Receipt Advice verifying the integrity of all the samples received. Within the holding times detailed in Schedule B(3) of The National Environment Protection (Assessment of Site Contamination) Measure 1999 (NEPM) by the National Environment Protection Council (NEPC), the recovered soil samples were analysed, except for some pH analysis where holding time has been over by few days. As mentioned, the soil profile encountered did not reveal any visual (staining, dying) or olfactory indicators of potential contaminants. Based on site observation, review of available information and the potential for contamination due to past and present site activities, the soil profile, the presence of fill, a suitable testing strategy is adopted below:

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

5 13188/2-AA 160 Burwood Road, Concord

Environmental Concern In the vicinity of above ground tanks (ASTs), potential underground fuel tanks (USTs) For screening in related to timber yard and possible pH issue Screening for imported fill

Borehole BH2, BH5, BH9 and BH10

All boreholes All boreholes

Testing Strategy Full range including metals, TPH, BTEX, PAH, OCP, PCB, total Phenols, total Cyanides, pH and Asbestos for top layer of fill or top soil, lower layer of fill and natural soil layer immediately below fill. Metals, OCP, PAH and pH for all top layer top soil or fill and some lower fill layer. Full range for each fill type.

FIELD QUALITY ASSURANCE & QUALITY CONTROL (QA & QC)

The following QA / QC procedures were implemented for the sampling and analytical program. Rinsate Sample

Five (5) rinsate water samples (R1 to R5) were recovered over the course of the field work in order to identify possible cross contamination between the sampling locations. The rinsate water samples were analysed for Metals (arsenic (As), cadmium (Cd), chromium (Cr), copper (Cu), lead (Pb), mercury (Hg), nickel (Ni) and zinc (Zn)). The test results for the rinsate water samples are summarised in Table A. Copies of the actual laboratory test results certificates are kept in the offices of Geotechnique and will be provided upon request. As indicated in Table A, all other concentrations in the rinsate samples were less than LOR or much lower than the assessing criteria, which indicates that adequate decontamination had been carried out in the field. Trip Spike Sample

Trip spike samples are obtained from the laboratory on a regular basis prior to conducting field sampling where volatile substances are suspected. The samples are retained in our Penrith office at less than 4°C for a period of not more than seven days. During field work trip spike samples are kept in a chilled container with soil samples recovered from the site. The trip spike samples are then forwarded to the laboratory together with the soil samples. The trip spike is prepared by adding a known amount of pure petrol standard to a clean sand sample. The sample is mixed thoroughly to ensure a relatively homogenous distribution of the spike throughout the sample. When the sample is submitted for analysis the same procedure is adopted as for the soil samples being analysed. The purpose of the trip spike is to detect any loss or potential loss of volatiles from the soil samples during field work or transportation. Two (2) trip spike samples were tested for BTEX. The test results for the trip spike sample, reported as a percentage recovery of the applied spike concentration, are shown in the attached Table B. The results indicate that it is unlikely that BTEX, if present within the soil samples recovered from the site, volatilised significantly during field work or transportation. Applying the losses experienced in the spike sample (worst case scenario) the actual concentrations of BTEX in each soil sample analysed might be at worst 0.121mg/kg (Benzene), 0.121mg/kg (Toluene), 0.119mg/kg (Ethyl benzene) and 0.357mg/kg (Xylenes). The concentrations in this case would still be considerably less than the relevant assessment criteria adopted (refer to Table F). Furthermore, all BTEX results were less than laboratory detection limits and there were no visible or olfactory indication of hydrocarbon contamination. Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

6 13188/2-AA 160 Burwood Road, Concord

Based on the above it is considered that any loss of volatiles from the recovered samples that might have occurred would not affect the outcome / conclusions of this report. Duplicate Sample

In order to ensure reliable analytical results from the laboratory, duplicate soil samples were prepared from original samples and submitted blind to the primary laboratory of SGS for analysis. Duplicate samples were prepared on the basis of sample numbers recovered during the field work. The duplicate sample frequency was computed using the total number of samples analysed as part of this assessment. The duplicate frequency adopted (5% for metals, PAH, OCP and pH, 9% for TPH, BTEX, PCB, Phenols and Cyanides) complies with the NEPM, which recommends a duplicate frequency of at least 5%. The duplicate samples test results are presented with the attached laboratory analytical reports and summarised in the attached Table C. A comparison was made of the laboratory test results for the duplicate samples with the original samples and the Relative Percentage Differences (RPD) were computed to assess the difference between the original and duplicate. RPD within 30% are generally considered acceptable. However, this variation can be higher for organic analysis than for inorganics and for low concentrations of analytes. As shown in Table C, the comparisons between the duplicate and corresponding original samples indicated generally acceptable RPD, with the exception of higher RPD of As due to inhomogeneity of the fill, Total PAH and Phenols due to low concentrations detected. Based on the above, the variation is not considered to be critical and overall the duplicate sample comparisons indicate that the laboratory test data provided by SGS are of adequate accuracy and reliability for this assessment. Split Sample

Split samples provide a check on the analytical performance of the primary laboratory. Split samples were submitted for analysis to the laboratory of Envirolab. Split samples were prepared on the basis of sample numbers recovered during the field work. The split sample frequency was computed using the total number of samples analysed as part of this assessment. The split sample frequency adopted (5% for metals, PAH, OCP and pH, 9% for TPH, BTEX, PCB, Phenols and Cyanides) complies with the NEPM, which recommends a frequency of 5%. The results are summarised in the attached Table D. Based on Schedule B (3) of the NEPM the difference in the results between the split samples should in general be within 30% of the mean concentration determined by both laboratories, i.e., RPD should be within 30%. However, this variation can be higher for organic analysis than for inorganics and for low concentrations of analytes. As shown in Table D the comparisons between the split and corresponding original samples indicated acceptable RPD, with the exception of higher RPD for Benzo (a) Pyrene (BaP) due to inhomogeneity of the fill, As, Hg, Zn, and Total PAH due to low concentrations detected. In particular, BaP concentration of the split sample was marginally higher than Ecological Screening Level for Urban residential. Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

7 13188/2-AA 160 Burwood Road, Concord

Based on the above, it is concluded that the test results provided by the primary laboratory may be relied upon for this assessment. LABORATORY QA & QC

Geotechnique uses only NATA accredited laboratories for chemical analyses. The laboratory must also incorporate quality laboratory management systems to ensure that trained analysts using validated methods and suitably calibrated equipment produce reliable results. In addition to the quality control samples, the laboratory must also ensure that all analysts receive certification as to their competence in carrying out the analysis and participate in national and international proficiency studies. SGS and Envirolab are both accredited by NATA and operate Quality Systems designed to comply with ISO / IEC 17025. The samples analysed for TPH (C6–C9) and BTEX were extracted by the purge and trap method recommended by the NSW EPA. All reported laboratory limits of reporting (LOR) / practical quantitation limits (PQL) were less than the assessment criteria. As part of the analytical run for the project the laboratories included laboratory blanks, duplicate samples, laboratory control samples, matrix spikes and surrogate spikes. We have checked the QA / QC procedures and results adopted by the laboratories against the appropriate guidelines. The quality control sample numbers adopted by SGS and Envirolab are considered adequate for the analyses undertaken and generally conform to recommendations provided in the National Environment Protection Measure (NEPM) 1999 “Guideline on Laboratory Analysis of Potentially Contaminated Soils”. Overall, the quality control elements adopted by SGS and Envirolab indicate the analytical data to fall within acceptable levels of accuracy and precision for the analysis of soils. The analytical data provided is therefore considered to be reliable and useable for this assessment. ASSESSMENT CRITERIA

Investigation levels and screening levels developed in the NEPM 2013 were used in this assessment, as follows; 

Risk-based Health Investigation Levels (HIL) for a broad range of metals and organic substances. The HIL are applicable for assessing human health risk via all relevant pathways of exposure. The HIL as listed in Table 1A (1) of Schedule B1 “Guideline on Investigation Levels for Soil and Groundwater” are provided for different land uses. The site is located within a parcel of industrial land, which will be developed into high density residential community. As such, with regard to human health, analytical results will be assessed against risk based HIL for residential with minimal opportunities for soil access; including dwellings with fully and permanently paved yard space such as high-rise buildings and apartments (HIL B).

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

8 13188/2-AA 160 Burwood Road, Concord

Health Screening Levels (HSL) for selected petroleum compounds, fractions and Naphthalene are applicable for assessing human health risk via inhalation and direct contact pathways. The HSL depend on specific soil physicochemical properties, land use scenarios and the characteristics of building structures. The HSL listed in Table 1A(3) of Schedule B1 “Guideline on Investigation Levels for Soil and Groundwater” apply to different soil types and depths below surface to >4 m. For this assessment, the analytical result was assessed against the available HSL for with minimal opportunities for soil access; including dwellings with fully and permanently paved yard space such as high-rise buildings and apartments (HSL B) for clay to depth of 0m to <1m and for sand to depth of 0m to <1m.

Ecological Screening Levels (ESL) for selected petroleum hydrocarbon compounds, TPH fractions and Benzo(a)Pyrene are applicable for assessing the risk to terrestrial ecosystems. ESL listed in Table 1B(6) of Schedule B1 “Guideline on Investigation Levels for Soil and Groundwater” broadly apply to coarse and fine-grained soils and various land uses and are generally applicable to the top 2m of soil. The analytical results were assessed against the available ESL for urban residential for coarse and fine-grained soils.

Ecological Investigation Levels (EIL), a specific type of Soil Quality Guidelines (SQG) for selected metals are applicable for assessing the risk to terrestrial ecosystems. EIL listed in Table 1B(1-5) of Schedule B1 “Guideline on Investigation Levels for Soil and Groundwater” depend on specific soil physicochemical properties and land use scenarios and generally apply to the top 2m of soil. The EIL are calculated using 30% effect concentration (EC30) or lowest observed effect concentrations (LOEC) toxicity data. For arsenic and lead generic EIL for urban residential land use for aged contamination are adopted. For other metals, where available, EIL are calculated directly by using EIL calculator developed by CSIRO for NEPC. For this assessment the analytical results were assessed against the available SQG / EIL for urban residential land use for aged contamination in soil for low traffic volume.

With regard to protection of the environment and impact on plant growth the available Provisional Phytotoxicity Based Investigation Levels (PIL) published in the Guidelines for the NSW Site Auditor Scheme (NSW EPA / DEC, 2006) and EIL published in the NEPM 1999 for cadmium and mercury are used.

For discrete soil samples, the individual concentrations of analytes, except Cd and Hg, were assessed against the HIL B / HSL B / ESL / EIL. The individual concentrations of Cd and Hg were assessed against the PIL and HIL B. The soil will be deemed contaminated or containing contamination “hot spots” if the above criteria are unfulfilled. Further investigation, remediation and/or management will be recommended if the area of concern is found to be contaminated or contain contamination “hot spots”. LABORATORY TEST RESULTS, ASSESSMENT & DISCUSSION

Copies of the actual laboratory test results certificates from SGS are kept in the offices of Geotechnique and will be provided upon request. The test results are also presented in Tables E1, E2 and F to I together with the assessment criteria adopted. A discussion of the test data is presented in the following sub-sections. Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

9 13188/2-AA 160 Burwood Road, Concord

Metals

The Metals test results for discrete selected soil samples are presented in Tables E1 and E2 and as shown, all concentrations of Metals were below the available relevant EIL, HIL B, except for elevated concentration of As from sample BH5 (0.1-0.4) which is marginally exceed HIL B. All Cd and Hg concentrations were also below the relevant PIL. pH

The pH test results for discrete selected soil samples are presented in Tables E1 and E2 and as shown, soil pHs are ranging from extremely acidic (4) to strongly alkaline (9), however, majority of the pHs are within normal range of 6 to 8. TPH and BTEX

The TPH and BTEX test results for the discrete selected soil samples are presented in Table F. As shown in Table F the concentrations of F1 (TPH C6-C10 less BTEX), F2 (TPH >C10-C16 less Naphthalene), F3 (TPH >C16-C34), F4 (TPH >C34-C40) and BTEX were below the relevant HSL B and / or ESL adopted. Moreover, all the test results were below the LOR. PAH

The PAH test results for the selected discrete soil samples are presented in Table G and as shown, all BaP, BaP TEQ, Naphthalene and Total PAH were below the relevant HIL B or ESL or HSL B or EIL adopted, except for elevated BaP concentrations from samples BH2 (4.5-4.8) and split sample S1 (original sample BH9 (2.0-2.3)) which are higher than ESL but much lower than HIL B. OCP

The OCP test results for selected discrete soil samples are presented in Table H and as indicated OCP were well below the relevant HIL B and all OCP were less than the laboratory LOR. The concentrations of DDT were also below the EIL. PCB

The PCB test results for the selected discrete soil samples are presented in Table H and as shown the PCB concentrations were below the relevant HIL B adopted and less than the laboratory LOR. Phenols

The Phenols test results for the selected discrete soil samples are presented in Table H and as shown the Phenols concentrations were well below the relevant HIL B adopted and less than the laboratory LOR. Cyanides

The Cyanides test results for the selected discrete soil samples are presented in Table H and as shown the Cyanides concentrations were well below the relevant HIL B adopted and some less than the laboratory LOR. Asbestos

The asbestos results for the selected discrete soil samples are presented in Table I and as shown no asbestos was detected in any of the samples. CONCLUSION AND RECOMMENDATIONS

Based on this assessment it is considered that soils collected geotechnical borehole within the site are generally unlikely to pose a risk of harm to human health and the environment and are environmentally suitable to retain on site for the proposed development subjected to: Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

10 13188/2-AA 160 Burwood Road, Concord

Elevated As concentration found in sample BH5 (0.1-0.4), which is marginally higher than relevant HIL B, deems the soil within the vicinity of this sample to be contaminated or containing contamination “hot spots”. Further investigation, remediation and/or management are required to make the contaminated soil suitable for the proposed development.

Elevated BaP concentrations from samples BH2 (4.5-4.8) and split sample S1 (original sample BH9 (2.0-2.3)) do not pose a risk of harm to human health and the environment due to the fact that these concentrations appear deeper than 2.0m which are unlikely to significantly upset any terrestrial ecosystem. However, if the soils were to be excavated and used as topsoil, then they may have an impact on the immediate ecosystems where they landed. A horticulturist may be consulted to determine the suitability of the soils before being use as topsoil.

Soil pHs were detected ranging from extremely acidic (4) to strongly alkaline (9). Extremely acidic condition could have an impact on footing of future structures; therefore appropriate consideration should be taken into account during the designing process.

If suspect materials (identified by unusual staining, odour, discolouration or inclusions such as building rubble, asbestos sheets / pieces, ash material, etc) are encountered during the construction stage, we recommend that this office is contacted for assessment and necessary action. LIMITATIONS

Within the stated scope of work the services performed by Geotechnique in preparation of this report were conducted in a manner consistent with the level of quality and skill generally exercised by members of the profession and consulting practice. This report has been prepared for Nix Anderson Pty Ltd for the purpose stated within. Any reliance on this report by other parties shall be at such parties' sole risk as the report might not contain sufficient information for other purposes. This report shall only be presented in full and may not be used to support any other objective than those set out in the report, except where written approval is provided by Geotechnique. The information in this report is considered accurate at completion of field sampling (14 August 2014) and in accordance with current site conditions. Any variations to the site form or use beyond this date might nullify the conclusions stated. No contamination assessment can eliminate all risk; even a rigorous professional assessment might not detect all contamination within the investigated locations. Reference should be made to the attached "Environmental Notes" for details of the limitations of this assessment.

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

11 13188/2-AA 160 Burwood Road, Concord

If you have any questions, please do not hesitate to contact the undersigned. Yours faithfully GEOTECHNIQUE PTY LTD

pp AN NGUYEN Environmental Scientist Attached Drawing No 13188/1-AA1 Borehole Locations Lab Summary Tables A to I 13188/1-AA Borehole Logs Nos 1 to 10 Appendix A Areas of Environmental Concern from SLR Consulting Australia Pty Ltd Appendix B Bushell’s History Appendix C Envirolab Services Certificates of Analysis and SGS Environmental Services Analytical Report Appendix D Environmental Notes

Nix Anderson Pty Ltd AN.sf/11.09.2014


BH2

BH3 BH5 BH1 BH4 BH9

BH7

DUK E

BH8

U AVEN E

BH6

BH10

BUR

LEGEND

WOO

D RO

AD

0

Imagery ©2014 NearMap.com

Borehole

20

40

60

80

100m

Scale 1:2000 NOTES

G

EOTECHNIQUE

®

PTY LTD

PO Box 880 Penrith NSW 2750 Tel: 02 4722 2700 Fax: 02 4722 2777 e-mail:info@geotech.com.au www.geotech.com.au

1. Site features are indicative and are not to scale. 2. This drawing has been produced using a base plan provided by others to which additional information e.g test pits, borehole locations or notes have been added. Some or all of the plan may not be relevant at the time of producing this drawing

Nix Management Pty Ltd Proposed Development Robert Timms Factory Site (Bushell’s) 160 Burwood Road, Concord Borehole Locations

Drawing No: 13188/1-AA1 Job No: 13188/1 Drawn By: MH Date: 20 August 2014 Checked By: ER File No: 13188-1 Layers: 0, AA1


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

R.L. surface : 5.5

deg.

datum :

AHD

classification symbol

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

Asphaltic concrete Road base Sandy GRAVEL, fine to medium grained, grey FILL; Sandstone Gravel, medium to coarse grained, red grey, with sand FILL; Silty Sand, fine grained, brown, with clay and gravel

0.5

hand penetrometer kPa

deg.

consistency density index

slope :

bearing :

0

DS

Logged/Checked by: AN/MT

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 1 Date : 07/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations

Well compacted

M M M

N=R 6,15,7/50 Ref

1

FILL; Silty Clay, medium to high plasticity, grey, M<PL trace of ironstone

1.5

Auger

DS

N=8 4,4,4

2

FILL; Sandy Clay, low plasticity, dark brown, trace of gravel

M<PL

2.5

DS

3 N=R 3,25/150

SM

Silty SAND, fine grained, dark grey

DS

Commenced Coring at 3.3m

form no. 002 version 04 - 05/11

3.5

4

4.5

W

MD

Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

0

DS

Logged/Checked by: LY/MT

deg.

R.L. surface : 5.4

deg.

datum :

AHD

classification symbol

bearing : MATERIAL DESCRIPTION

soil type, plasticity or particle characteristic, colour, secondary and minor components.

hand penetrometer kPa

slope :

consistency density index

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 2 Date : 11/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations

TOPSOIL; Silty Sand, fine grained, grey, with inclusion of root fibre FILL; Silty Sand, fine grained, grey, with inclusion of gravel

Well compacted

FILL: Gravelly Sandy Clay, low plasticity, brown

Well compacted

FILL; Silty Clay, medium plasticity, dark grey, with inclusion of timber

Well compacted

0.5

DS

N=4 4,2,2

1

1.5

DS

N=11 5,6,5

2

2.5

3

DS

N=4 2,2,2

form no. 002 version 04 - 05/11

3.5

4

4.5

DS

N=3 2,1,2


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

deg.

R.L. surface : 5.4

deg.

datum :

AHD

classification symbol

bearing :

CH

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

Sandy CLAY, high plasticity, brown and grey

M>PL

St-H

hand penetrometer kPa

slope :

consistency density index

5

Logged/Checked by: LY/MT

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 2 Date : 11/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations

Residual

Auger

DS

5.5

6

N=11 4,5,6

6.5

7

7.5

8

form no. 002 version 04 - 05/11

8.5

9

9.5

SANDSTONE; extremely weathered, extremely low strength, brown and grey

Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

Logged/Checked by: LY/MT

Dry

11

11.5

12

12.5

13

form no. 002 version 04 - 05/11

13.5

14

14.5

R.L. surface : 5.4

deg.

datum :

AHD

classification symbol

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

Borehole 2 terminated at 10.5m

hand penetrometer kPa

deg.

bearing :

10

10.5

slope :

consistency density index

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 2 Date : 11/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

deg.

datum :

AHD

classification symbol

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

0.5

hand penetrometer kPa

R.L. surface : 5.4

consistency density index

deg.

TOPSOIL; Silty Sand, fine grained, grey, with root fibre FILL; Clayey Sand, medium grained, brown, with gravel

DS

DS

slope :

bearing :

0

N=R 11/50 Ref

Logged/Checked by: LY/MT

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 3 Date : 12/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations

Well compacted

Sandstone floater

FILL; Sandy Clay, medium plasticity, brown

Well compacted

FILL; Sandy Clay, high plasticity, dark grey

Well compacted

1

1.5

DS

N=5 2,2,3

Auger

2

2.5

3 N=R 10,10/50

SM

Silty SAND, fine to medium grained, grey

SANDSTONE; extremely weathered, grey

Dry

form no. 002 version 04 - 05/11

3.5

4

Coring commenced at 4.1m

4.5

M

L-VD

Alluvial

Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

Logged/Checked by: LY/MT

deg.

R.L. surface : 5.8

deg.

datum :

AHD

classification symbol

bearing :

0

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

hand penetrometer kPa

slope :

consistency density index

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 4 Date : 12/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations

TOPSOIL; Silty Sand, medium grained, grey, with root fibre Well compacted

FILL; Gravelly Sand, medium grained, brown DS N=R 15/150 Ref

0.5

SANDSTONE; floater SM

1

Silty SAND, fine to medium grained, brown grey

SANDSTONE; extremely weathered. extremely low strength, brown and grey

1.5

2

Dry

2.5

3

form no. 002 version 04 - 05/11

3.5

4

4.5

Commenced Coring at 2.5m

M

VD

Alluvial

Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

R.L. surface : 6.7

deg.

datum :

AHD

classification symbol

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

TOPSOIL; Silty Clay, medium plasticity, grey, with root fibre FILL; Sandy Gravelly Clay, medium plasticity, grey, with inclusion of sandstone fragments

DS CH

Silty CLAY, high plasticity, grey

hand penetrometer kPa

deg.

consistency density index

slope :

bearing :

0

0.5

Logged/Checked by: LY/MT

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 5 Date : 13/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations

Well compacted

M>PL

S

Residual

N=4 4,2,2

Auger 1

SANDSTONE; extremely weathered, extremely low strength, brown

Dry

1.5

Commenced Coring at 1.6m

2

2.5

3

form no. 002 version 04 - 05/11

3.5

4

4.5

Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

deg.

datum :

AHD

classification symbol

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

ROADBASE, gravel FILL; Gravelly Clay, medium plasticity, grey 0.5 N=R 7,20/100, Ref

1

CI

Sandy CLAY, medium plasticity, brown, with inclusion of ironstone

Dry

SANDSTONE; extremely weathered, extremely low strength, brown, with some ironstone Commenced Coring at 1.2m

1.5

2

2.5

3

3.5

4

4.5

hand penetrometer kPa

R.L. surface : 6.3

consistency density index

deg.

Remarks and additional observations

CONCRETE

DS

form no. 002 version 04 - 05/11

slope :

bearing :

0

DS

Logged/Checked by: LY/MT

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 6 Date : 13/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Well compacted

M>PL

H

Residual

Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

Logged/Checked by: LY/MT

deg.

R.L. surface : 5.6

deg.

datum :

AHD

classification symbol

bearing :

0

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

ASPHALTIC CONCRETE ROADBASE; sandy gravel, fine to medium grained, grey FILL; Silty Sand, fine grained, brown, with inclusion of gravel

hand penetrometer kPa

slope :

consistency density index

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 7 Date : 11/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations

Well compacted

0.5

DS

N=14 9,10,4

1

1.5

DS

FILL; Sandy Clay, high plasticity, dark grey

Well compacted

FILL; Sandy Clay, medium plasticity, brown, with inclusion of gravel

Well compacted

FILL; Silty Clay, high plasticity, grey

Well compacted

N=5 5,3,2

Auger

2

DS 2.5

3 N=R 2,2,10/ 100

SM

Silty SAND, fine to medium grained, grey brown

SANDSTONE; fine to medium grained, grey brown

3.5

Dry

form no. 002 version 04 - 05/11

Commenced Coring at 3.8m 4

4.5

M

D-VD

Alluvial

Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

Logged/Checked by: LY/MT

deg.

R.L. surface : 5.7

deg.

datum :

AHD

classification symbol

bearing :

0

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

M

MD

hand penetrometer kPa

slope :

consistency density index

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 8 Date : 14/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations

Concrete Pavement 200mm FILL; Silty Sand, fine to medium grained, brown, with some gravel

DS SM

Silty SAND, fine to medium grained, brown, with some ironstone

SM

SANDSTONE; fine to medium grained, brown, extremely weathered

0.5

N=19 5,10,9

1

Dry 1.5

2

2.5

3

form no. 002 version 04 - 05/11

3.5

4

4.5

Commenced Coring at 1.4m

Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

Logged/Checked by: LY/MT

deg.

R.L. surface : 7.16

deg.

datum :

AHD

classification symbol

bearing :

0

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

hand penetrometer kPa

slope :

consistency density index

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 9 Date : 14/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations

Bitumen Pavement FILL; Silty Gravelly Clay, medium plasticity, grey, with some gravel

DS 0.5

M<PL

M<PL FILL; Silty Gravelly Clay, medium to high plasticity, grey brown to dark brown, with gravel

N=13 5,3,10

1

DS

FILL; Silty Gravelly Clay, medium to high plasticity, grey brown to dark brown with ironstone

M<PL

FILL; Silty Clay, medium to high plasticity, dark brown

M<PL

F

Silty CLAY, medium to high plasticity, orange to M>PL grey, with some ironstone

St

1.5

N=5 2,2,3

2

DS

2.5

CI-CH

Residual

3

N=8 2,3,5

3.5

4

Dry

form no. 002 version 04 - 05/11

SANDSTONE; fine to medium grained, grey red

4.5

Commenced Coring at 4.5m

Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

Logged/Checked by: LY/MT

deg.

R.L. surface : 5.9

deg.

datum :

AHD

classification symbol

bearing :

0

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

DS 0.5

Remarks and additional observations

Concrete Road base/gravel FILL; Gravelly Clay, medium plasticity, grey with inclusion of sand

DS

hand penetrometer kPa

slope :

consistency density index

Edson Truck Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/1 Borehole No. : 10 Date : 14/08/2014

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

CH

Shaley CLAY, high plasticity, grey and red brown

Well compacted

M>PL

VSt-H

Residual

N=16 7,7,8

1

Auger N=R 30/150, Ref

1.5

SANDSTONE; extremely weathered, extremely low strength, brown with ironstone bands

2

Dry 2.5

3

form no. 002 version 04 - 05/11

3.5

4

4.5

Commenced coring at 2.4m

Bedrock


G EOTECHNIQUE PTY LTD

EXPLANATORY NOTES Introduction These notes have been provided to simplify the geotechnical report with regard to investigation procedures, classification methods and certain matters relating to the Discussion and Comments section. Not all notes are necessarily relevant to all reports. Geotechnical reports are based on information gained from finite subsurface probing, excavation, boring, sampling or other means of investigation, supplemented by experience and knowledge of local geology. For this reason they must be regarded as interpretative rather than factual documents, limited to some extent by the scope of information on which they rely. Description and Classification Methods The methods of description and classification of soils and rocks used in this report are based on AS1726 - 1993 "Geotechnical Site Investigations". In general, descriptions cover the following properties; strength or density, colour, structure, soil or rock type, and inclusions. Identification and classification of soil and rock involves, to a large extent, judgement within the acceptable level commonly adopted by current geotechnical practices. Soil types are described according to the predominating particle size, qualified by the grading or other particles present (e.g. sandy clay) on the following basis: Soil Classification Clay Silt Sand Gravel

Particle Size Less than 0.002mm 0.002 to 0.06mm 0.06 to 2.00mm 2.00mm to 60.00mm

Cohesive soils are classified on the basis of strength, either by laboratory testing or engineering examination. The strength terms are defined as follows: Classification Very Soft Soft Firm Stiff Very Stiff Hard

Undrained Shear Strength kPa Less than 12 12 – 25 25 – 50 50 – 100 100 – 200 Greater than 200

Non-cohesive soils are classified on the basis of relative density, generally from the results of standard penetration tests (SPT) or Dutch cone penetrometer tests (CPT), as below: Relative Density Very Loose Loose Medium Dense Dense Very Dense

SPT ‘N’ Value (blows/300mm)

CPT Cone Value (qc-MPQ)

Less than 5 5 – 10 10 – 30 30 – 50 >50

Less than 2 2–5 5 – 15 15 – 25 >25

Rock types are classified by their geological names, together with descriptive terms on degrees of weathering, strength, defects and other minor components. Where relevant, further information regarding rock classification is given on the following sheet. Sampling Sampling is carried out during drilling to allow engineering examination (and laboratory testing where required) of the soil or rock. Disturbed samples taken during drilling provide information on plasticity, grain size, colour, type, moisture content, inclusions and depending upon the degree of disturbance, some information on strength and structure.

Undisturbed samples are taken by pushing a thin walled sample tube (normally known as U50) into the soil and withdrawing a sample of the soil in a relatively undisturbed state. Such samples yield information on structure and strength and are necessary for laboratory determination of shear strength and compressibility. Undisturbed sampling is generally effective only in cohesive soils. Details of the type and method of sampling are given in the report. Field Investigation Methods The following is a brief summary of investigation methods currently carried out by this Company and comments on their use and application. Hand Auger Drilling The borehole is advanced by manually operated equipment. The diameter of the borehole ranges from 50mm to 100mm. Penetration depth of hand augered boreholes may be limited by premature refusal on a variety of materials, such as hard clay, gravels or ironstone. Test Pits These are excavated with a tractor-mounted backhoe or a tracked excavator, allowing close examination of the insitu soils if it is safe to descend into the pit. The depth of penetration is limited to about 3.0m for a backhoe and up to 6.0m for an excavator. A potential disadvantage is the disturbance caused by the excavation. Care must be taken if construction is to be carried out near, or within the test pit locations, to either adequately recompact the backfill during construction, or to design the structure to accommodate the poorly compacted backfill. Large Diameter Auger (e.g. Pengo) The hole is advanced by a rotating plate or short spiral auger, generally 300mm or larger in diameter. The cuttings are returned to the surface at intervals (generally of not more than 0.5m) and are disturbed, but usually unchanged in moisture content. Identification of soil strata is generally much more reliable than with continuous spiral flight augers and is usually supplemented by occasional undisturbed tube sampling. Continuous Spiral Flight Augers The hole is advanced by using 90mm-115mm diameter continuous spiral flight augers, which are withdrawn at intervals to allow sampling or insitu testing. This is a relatively economical means of drilling in clays and in sands above the water table. Samples are returned to the surface, or may be collected after withdrawal of the auger flights, but they are very disturbed and may be highly mixed with soil of other stratum. Information from the drilling (as distinct from specific sampling by SPT or undisturbed samples) is of relatively lower reliability due to remoulding, mixing or softening of samples by groundwater, resulting in uncertainties of the original sample depth. The spiral augers are usually advanced by using a V-bit through the soil profile to refusal, followed by Tungsten Carbide (TC) bit, to penetrate into bedrock. The quality and continuity of the bedrock may be assessed by examination of recovered rock fragments and through observation of the drilling penetration resistance. Non-core Rotary Drilling (Wash Boring) The hole is advanced by a rotary bit, with water being pumped down the drill rod and returned up the annulus carrying the drill cuttings. Only major changes in stratification can be determined from the cuttings, together with some information from the feel and rate of penetration. Rotary Mud Stabilised Drilling This is similar to rotary drilling, but uses drilling mud as a circulating fluid, which may consist of a range of products from bentonite to polymers such as Revert or Biogel. The mud tends to mask the cuttings and reliable identification is again only possible from separate intact sampling (e.g. SPT and U50) samples).

i


G EOTECHNIQUE PTY LTD

Continuous Core Drilling A continuous core sample is obtained using a diamond tipped core barrel. Providing full core recovery is achieved (which is not always possible in very low strength rocks and granular soils), this technique provides a very reliable (but relatively expensive) method of investigation. In rocks, an NMLC triple tube core barrel, which gives a core of about 50mm diameter, is usually used with water flush. Portable Proline Drilling This is manually operated equipment and is only used in sites which require bedrock core sampling and there is restricted site access to truck mounted drill rigs. The boreholes are usually advanced initially using a tricone roller bit and water circulation to penetrate the upper soil profile. In some instances, a hand auger may be used to penetrate the soil profile. Subsequent drilling into bedrock involves the use of NMLC triple tube equipment, using water as a lubricant. Standard Penetration Tests Standard penetration tests are used mainly in non-cohesive soils, but occasionally also in cohesive soils, as a means of determining density or strength and of obtaining a relatively undisturbed sample. The test procedure is described in AS1289 6.3.1. The test is carried out in a borehole by driving a 50mm diameter split sample tube under the impact of a 63kg hammer with a free fall of 769mm. It is normal for the tube to be driven in three successive 150mm increments and the 'N’ value is taken as the number of blows for the last 300mm. In dense sands, very hard clays or weak rock, the full 450mm penetration may not be practicable and the test is discontinued. The test results are reported in the following form: In a case where full penetration is obtained with successive blow counts for each 150mm of, say 4, 6 and 7 blows as; N = 13 4,6,7 In a case where the test is discontinued short of full penetration, say after 15 blows for the first 150mm and 30 blows for the next 40mm as; 15, 30/40mm The results of the tests can be related empirically to the engineering properties of the soil. Occasionally the test method is used to obtain samples in 50mm diameter thin walled sample tubes in clays. In these circumstances, the test results are shown on the bore logs in brackets. Cone Penetrometer Testing and Interpretation Cone penetrometer testing (sometimes referred to as Dutch ConeCPT) described in this report, has been carried out using an electrical friction cone penetrometer and the test is described in AS1289 6.5.1. In the test, a 35mm diameter rod with cone tipped end is pushed continuously into the soil, the reaction being provided by a specially designed truck or rig, which is fitted with a hydraulic ram system. Measurements are made of the end bearing resistance on the cone and the friction resistance on a separate 130mm long sleeve, immediately behind the cone. Transducers in the tip of the assembly are connected by electrical wires passing through the centre of the push rods to an amplifier and recorder unit mounted on the control truck. As penetration occurs (at a rate of approximately 20mm per second) the information is output on continuous chart recorders. The plotted results given in this report have been traced from the original records. The information provided on the charts comprises:

The ratios of the sleeve resistance to cone resistance will vary with the type of soil encountered, with higher relative friction in clays than in sands. Friction ratios of 1% to 2% are commonly encountered in sands and very soft clays, rising to 4% to 10% in stiff clays. In sands, the relationship between cone resistance and SPT value is commonly in the range: qc (MPa) = (0.4 to 0.6) N (blows per 300mm) In clays, the relationship between undrained shear strength and cone resistance is commonly in the range: qc=(12 to 18)Cu Interpretation of CPT values can also be made to allow estimate of modulus or compressibility values, to allow calculation of foundation settlements. Inferred stratification, as shown on the attached report, is assessed from the cone and friction traces, from experience and information from nearby boreholes etc. This information is presented for general guidance, but must be regarded as being to some extent interpretive. The test method provides a continuous profile of engineering properties and where precise information or soil classification is required, direct drilling and sampling may be preferable. Portable Dynamic Cone Penetrometer (DCP) Portable Dynamic Cone Penetrometer tests are carried out by driving a rod into the ground with a falling weight hammer and measuring the blows per successive 100mm increment of penetration. There are two similar tests, Cone Penetrometer (commonly known as Scala Penetrometer) AS1289 6.3.2 and the Perth Sand Penetrometer AS1289 6.3.3. Scala Penetrometer is commonly adopted by this company and consists of a 16mm rod with a 20mm diameter cone end, driven with a 9kg hammer, dropping 510mm (AS1289 Test P3.2). Laboratory Testing Laboratory testing is carried out in accordance with Australian Standard 1289 "Methods of Testing Soil for Engineering Purposes". Details of the test procedures are given on the individual report forms. Engineering Logs The engineering logs presented herein are an engineering and/or geological interpretation of the sub-surface conditions and their reliability will depend to some extent on frequency of sampling and the method of drilling. Ideally, continuous undisturbed sampling or core drilling will provide the most reliable assessment, however, this is not always practicable or possible to justify economically. As it is, the boreholes represent only a small sample of the total sub-surface profile. Interpretation of the information and its application to design and construction should take into account the spacing of boreholes, frequency of sampling and the possibility of other than ‘straight line’ variations between the boreholes. Groundwater Where groundwater levels are measured in boreholes, there are several potential problems: •

in low permeability soils groundwater, although present, may enter the hole slowly or perhaps not at all during the investigation period

a localised perched water table may lead to an erroneous indication of the true water table

water table levels will vary from time to time due to the seasons or recent weather changes. They may not be the same at the time of construction as indicated in the report

the use of water or mud as a drilling fluid will mask any groundwater inflow. Water has to be blown out of the hole and drilling mud must be washed out of the hole if water observations are to be made

Cone resistance - the actual end bearing force divided by the cross sectional area of the cone, expressed in MPa * Sleeve friction - the frictional force on the sleeve divided by the surface area, expressed in kPa

ii


G EOTECHNIQUE PTY LTD

More reliable measurements can be achieved by installing standpipes that are read at intervals over several days, or weeks for low permeability soils. Piezometers sealed in a particular stratum may be advisable in low permeability soils, or where there may be interference from a perched water table or surface water. Engineering Reports Engineering reports are prepared by qualified personnel and are based on the information obtained and on current engineering standards of interpretation and analysis. Where the report has been prepared for a specific design proposal, perhaps a three-storey building, the information and interpretation may not be relevant if the design proposal is changed, say to a twenty-storey building. If this occurs, the Company will be pleased to review the report and sufficiency of the investigation work. Every care is taken with the report as it relates to interpretation of sub-surface conditions, discussions of geotechnical aspects and recommendations or suggestions for design and construction. However, the Company cannot always anticipate or assume responsibility for: •

Unexpected variations in ground conditions. The potential for this will depend partly on bore spacing and sampling frequency.

Changes in policy or interpretation of policy by statutory authorities.

The actions of contractors responding to commercial pressures.

If these occur, the Company will be pleased to assist with investigation or advice to resolve the matter. Site Anomalies In the event that conditions encountered on-site during construction appear to vary from those that were expected from the information contained in the report, the Company requests immediate notification. Most problems are much more easily resolved when conditions are exposed rather than at some later stage, well after the event. Reproduction of Information for Contractual Purposes Attention is drawn to the document "Guidelines for the Provision of Geotechnical Information in Tender Documents", published by the Institute of Engineers Australia. Where information obtained from this Investigation is provided for tendering purposes; it is recommended that all information, including the written report and discussion, be made available. In circumstances where the discussion or comments section is not relevant to the contractual situation, it may be appropriate to prepare a specially edited document. The Company would be pleased to assist in this regard and/or make additional copies of the report available for contract purposes, at a nominal charge. Site Inspection The Company will always be pleased to provide engineering inspection services for geotechnical aspects of work to which this report is related. This could range from a site visit to confirm that the conditions exposed are as expected, to full time engineering presence on site. Review of Design Where major civil or structural developments are proposed, or where only a limited investigation has been completed, or where the geotechnical conditions are complex, it is prudent to have the design reviewed by a Senior Geotechnical Engineer.

iii


G EOTECHNIQUE PTY LTD

TABLE A RINSATE SAMPLES (Ref No: 13188/2-AA) Rinsate R1

Rinsate R2

Rinsate R3

Rinsate R4

Rinsate R5

7/08/2014

11/08/2014

12/08/2014

13/08/2014

14/08/2014

METALS

(m g/L)

(m g/L)

(m g/L)

(m g/L)

(m g/L)

Arsenic

<0.02

<0.02

<0.02

<0.02

<0.02

Cadmium

<0.001

<0.001

<0.001

<0.001

<0.001

Chromium

<0.005

<0.005

<0.005

<0.005

<0.005

Copper

<0.005

<0.005

<0.005

<0.005

<0.005

Lead

<0.02

<0.02

<0.02

<0.02

<0.02

Mercury

0.0002

<0.0001

<0.0001

<0.0001

<0.0001

Nickel Zinc

<0.005 <0.01

<0.005 <0.01

<0.005 <0.01

<0.005 <0.01

<0.005 <0.01

ANALYTES

TABLE B TRIP SPIKE SAMPLES (Ref No: 13188/2-AA) ANALYTES

Trip Spike TS1

Trip Spike TS2

Benzene

85%

79%

Toluene

79%

91%

Ethyl Benzene

81%

95%

Xylenes

81%

97%

BTEX

Note : results are reported as percentage recovery of know n spike concentrations

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

TABLE C DUPLICATE SAMPLE (Ref No: 13188/2-AA) .

BH5

Duplicate

RELATIVE PERCENTAGE

0.1-0.4 m

D2

DIFFERENCES (RPD)

m g/kg

m g/kg

%

Arsenic

520

260

67

Cadmium

0.6

0.7

15

Chromium

37

36

3

Copper

41

43

5

Lead

120

110

9

Mercury

0.06

0.08

29

Nickel

10

9.5

5

Zinc

150

150

0

F1 (C6-C10 less BTEX)

<25

<25

-

F2 (>C10-C16)

<25

<25

-

F3 (>C16-C34)

<90

<90

-

F4 (>C34-C40)

<120

<120

-

Benzene

<0.1

<0.1

-

Toluene

<0.1

<0.1

-

Ethyl Benzene

<0.1

<0.1

-

Xylenes

<0.3

<0.3

-

Benzo(a)Pyrene TEQ

0.3

<0.3

-

Total PAH

2.4

1.5

46

Naphthalene

<0.1

<0.1

Benzo(a)Pyrene

0.2

<0.1

-

Hexachlorobenzene (HCB)

<0.1

<0.1

-

Heptachlor

<0.1

<0.1

-

Aldrin+Dieldrin

<0.15

<0.15

-

Endrin

<0.2

<0.2

-

Methoxychlor

<0.1

<0.1

-

Mirex

<0.1

<0.1

-

Endosulfan (alpha, beta & sulphate)

<0.5

<0.5

-

DDD+DDE+DDT

<0.6

<0.6

-

Chlordane (alpha & gamma)

<0.2

<0.2

-

<1

<1

-

0.2

0.2

0

0.3

0.1

100

ANALYTES METALS

TOTAL PETROLEUM HYDROCARBONS (TPH)

BTEX

POLYCYCLIC AROMATIC HYDROCARBONS

ORGANOCHLORINE PESTICIDES (OCP)

POLYCHLORINATED BIPHENYLS (PCB) Total PCB CYANIDES & PHENOLS Cyanides Phenols

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

TABLE D SPLIT SAMPLE (Ref No: 13188/2-AA) BH9

Split Sam ple

RELATIVE PERCENTAGE

2.0-2.3 m

S1

DIFFERENCES (RPD)

m g/kg

m g/kg

(SGS)

(ENVIROLAB)

%

Arsenic

12

20

50

Cadmium

0.4

<0.4

-

Chromium

20

25

22

Copper

20

32

46

Lead

42

50

17

Mercury

0.16

0.3

61

Nickel

2.3

3

26

Zinc

67

100

40

F1 (C6-C10 less BTEX)

<25

<25

-

F2 (>C10-C16)

<25

<50

-

F3 (>C16-C34)

<90

<50

-

F4 (>C34-C40)

<120

<100

-

Benzene

<0.1

<0.2

-

Toluene

<0.1

<0.5

-

Ethyl Benzene

<0.1

<1

-

Xylenes

<0.3

<3

-

ANALYTES

METALS

TOTAL PETROLEUM HYDROCARBONS (TPH)

BTEX

POLYCYCLIC AROMATIC HYDROCARBONS (PAH) Benzo(a)Pyrene TEQ

0.8

1

22

Total PAH

4.8

10.63

76

Naphthalene

<0.1

<0.1

-

Benzo(a)Pyrene

0.5

0.93

60

Hexachlorobenzene (HCB)

<0.1

<0.1

-

Heptachlor

<0.1

<0.1

-

Aldrin+Dieldrin

<0.15

<0.2

-

Endrin

<0.2

<0.1

-

Methoxychlor

<0.1

<0.1

-

Mirex

<0.1

-

-

Endosulfan (alpha (I), beta (II) & sulphate)

<0.5

<0.3

-

DDD+DDE+DDT

<0.6

<0.3

-

Chlordane (alpha & gamma)

<0.2

<0.2

-

<1

<0.7

-

0.1

<0.5

-

0.4

<5

-

ORGANOCHLORINE PESTICIDES (OCP)

POLYCHLORINATED BIPHENYLS (PCB) Total PCB CYANIDES & PHENOLS Cyanides Phenols

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

TABLE E1 METALS, CATION EXCHANGE CAPACITY (CEC), pH & TOTAL ORGANIC CARBON (TOC) TEST RESULTS DISCRETE SAMPLE(S) (Ref No: 13188/2-AA)

Depth (m)

ARSENIC

CADMIUM

CHROMIUM (Total)

COPPER

LEAD

MERCURY

NICKEL

ZINC

CEC (cmolc /kg)

pH

TOC (%)

METALS (mg/kg)

BH1

1.5-1.8

7

0.4

16

6.7

18

0.02

1.5

7.7

7

4

0

BH1

3.15-3.25

9

<0.3

14

4.1

18

0.02

3.1

11

8

6

2

BH2 BH2

0-0.15 0.5-0.8

<3 4

<0.3 0.3

9.1 12

17 15

28 20

0.02 0.01

5.3 4.5

54 38

10 10

5.3 6

4 2

BH2

4.5-4.8

30

0.8

52

130

120

0.4

8.3

260

25

8

3

BH2

5.1-5.25

10

0.3

18

8.5

22

0.02

1.9

19

13

8

0

BH3

0-0.1

<3

<0.3

8.4

8

13

0.01

5.5

26

7

6

2

BH3

1.5-1.8

7

<0.3

12

9

35

0.04

2.6

54

12

7

2

BH4

0-0.15

12

0.4

18

16

38

0.04

4.9

62

18

8

2

BH5

0.1-0.4

520

0.6

37

41

120

0.06

10

150

11

6

1

BH5

0.6-0.7

62

0.4

28

12

43

0.06

2.1

31

7

6

1

BH6

0.6-0.7

7

0.6

27

14

14

0.01

15

17

6

5

0

BH7

0.15-0.45

<3

<0.3

11

8.6

9

0.01

8.6

20

9

9

0

BH7

1.4-1.7

4

<0.3

11

9.3

13

0.01

5.9

17

8

6

0

BH8

0.2-0.4

4

0.5

97

15

10

0.02

50

35

-

8

-

BH9

0.2-0.5

6

0.4

23

18

23

0.02

15

43

34

8

0

BH9

2.0-2.3

12

0.4

20

20

42

0.16

2.3

67

15

7

1

BH9

2.55-2.65

5

0.3

9.3

12

24

0.05

0.7

13

6

5

0

BH10

0.23-0.5

6

0.4

16

22

15

0.01

19

16

15

7

0

BH10

0.55-0.65

4

<0.3

7.2

23

13

<0.01 19

15

6

5

0

1

0.3

0.5

0.5

1

0.05

2

0.02

-

0.05

500

150

500

30000

1200

30

Sample Location

Limits of Reporting (LOR)

0.5

NATIONAL ENVIRONMENT PROTECTION AMENDMENT MEASURE (2013) a

Health-based Investigation Levels (HIL) B - Residential B

e b

Ecological Investigation Levels (EIL) - Urban residential

100

c

400

1200 60000

g

f

-

d

55

1100

-

55

160

GUIDELINES FOR THE NSW SITE AUDITOR SCHEME (2006) Provisional Phytotoxity-Based Investigation Levels (PIL) Notes:

3

1

a: Residential w ith minimal opportunities for soil access; includes dw ellings w ith fully and permanently paved yard space such as high-rise buildings and apartments. b: EIL of aged copper, nickel & zinc w ere derived from calculation spreadsheet developed by CSIRO for NEPC; old NSW suburb w ith low traffic volume; the low est CEC=6 cmolc/kg; pH=4 and TOC=1 % w ere selected for derivation of EIL. c: Chromium (VI) d: Methyl Mercury e: Generic EIL for aged arsenic f: Chromium (III), clay content w as assumed =10%, a conservative assumption g: Generic EIL for aged lead

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

TABLE E2 METALS, CATION EXCHANGE CAPACITY (CEC), pH & TOTAL ORGANIC CARBON (TOC) TEST RESULTS DISCRETE SAMPLE (Ref No: 13188/2-AA)

Sample Location

Depth (m)

ARSENIC

CADMIUM

CHROMIUM (Total)

COPPER

LEAD

MERCURY

NICKEL

ZINC

CEC (cmolc /kg)

pH

TOC (%)

METALS (mg/kg)

BH2

4.5-4.8

30

0.8

52

130

120

0.4

8.3

260

25

8

3

1

0.3

0.5

0.5

1

0.05

0.5

2

0.02

-

0.05

150

500 c

30000

1200

Limits of Reporting (LOR) NATIONAL ENVIRONMENT PROTECTION AMENDMENT MEASURE (2013) Health-based Investigation Levels (HIL)aB - Residential B

500 e

b

Ecological Investigation Levels (EIL) - Urban residential

100

-

400

30d 1200 60000

g

f

240

1100

-

390

1100

GUIDELINES FOR THE NSW SITE AUDITOR SCHEME (2006) Provisional Phytotoxity-Based Investigation Levels (PIL)

Notes:

3

1

a: Residential w ith minimal opportunities for soil access; includes dw ellings w ith fully and permanently paved yard space such as high-rise buildings and apartments. b: EIL of aged copper, nickel & zinc w ere derived from calculation spreadsheet developed by CSIRO for NEPC; old NSW suburb w ith low traffic volume; the low est CEC=25 cmolc/kg; pH=8 and TOC=3 % w ere selected for derivation of EIL. c: Chromium (VI) d: Methyl Mercury e: Generic EIL for aged arsenic f: Chromium (III), clay content w as assumed =10%, a conservative assumption g: Generic EIL for aged lead

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

TABLE F TOTAL PETROLEUM HYDROCARBONS (TPH) AND BTEX TEST RESULTS DISCRETE SAMPLE(S) (Ref No: 13188/2-AA) NATIONAL ENVIRONMENT PROTECTION AMENDMENT MEASURE (2013) Health Screening Levels (HSL) B High density residential

TOLUENE

ETHYLBENZENE

XYLENES

-

-

-

-

45

-

-

-

-

-

-

-

-

BH2

5.1-5.25

CLAY

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3 290

NL

3

NL

NL

NL

180 120 1300 5600 65 105 125

45

-

-

-

-

-

-

-

-

BH3

1.5-1.8

CLAY

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

90

NL

1

NL

NL

310

180 120 1300 5600 65 105 125

45

-

-

-

-

-

-

-

-

BH5

0.1-0.4

CLAY

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

50

280 0.7 480 NL

110

180 120 1300 5600 65 105 125

45

-

-

-

-

-

-

-

-

BH5

0.6-0.7

CLAY

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

50

280 0.7 480 NL

110

180 120 1300 5600 65 105 125

45

-

-

-

-

-

-

-

-

BH9

0.2-0.5

SAND

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

45

110 0.5 160

55

40

70

105

BH9

2.0-2.3

CLAY

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3 150

NL

2

NL

NL

NL

180 120 1300 5600 65 105 125

45

-

-

-

-

-

-

-

-

BH9

2.55-2.65

CLAY

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3 150

NL

2

NL

NL

NL

180 120 1300 5600 65 105 125

45

-

-

-

-

-

-

-

-

BH10

0.23-0.5

CLAY

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

50

280 0.7 480 NL

110

180 120 1300 5600 65 105 125

45

-

-

-

-

-

-

-

-

BH10

0.55-0.65

CLAY

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

50

280 0.7 480 NL

110

180 120 1300 5600 65 105 125

45

-

-

-

-

-

-

-

-

-

-

-

-

-

-

-

-

-

BENZENE

-

F4

-

F3

-

F2**

ETHYLBENZENE

180 120 1300 5600 65 105 125

F1

TOLUENE

105

NL

XYLENES

BENZENE

70

NL

0.1

F4

180 120 300 2800 50 85

NL

0.1

F3

40

3

0.1

F2**

55

NL

120

F1

110 0.5 160

XYLENES

45

160 <120 <0.1 <0.1 <0.1 <0.3 290

90

ETHYLBENZENE

<90 <120 <0.1 <0.1 <0.1 <0.3

<25

TOLUENE

F2*

<25

<25

BENZENE

F1

<25

<25

XYLENES

<25

CLAY

Limits of Reporting (LOR) 25 25 Notes: F1: C6-C10 less BTEX F2*: >C10-C16 less Naphthalene F2**: >C10-C16 F3: >C16-C34 F4: >C34-C40

ETHYLBENZENE

SAND

4.5-4.8

TOLUENE

F3

0.5-0.8

BH2

Soil type

BENZENE

F2**

BH2

Sample Location Depth (m)

F4

F2*

BTEX (mg/kg)

Ecological Screening Levels for coarsegrained soil Urban residential

F1

TPH (mg/kg)

Ecological Screening Levels for finegrained soil Urban residential

180 120 300 2800 50 85

0.3

NL: Not Limiting

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

TABLE G POLYCYCLIC AROMATIC HYDROCARBONS (PAH) TEST RESULTS DISCRETE SAMPLE(S) (Ref No: 13188/2-AA) NATIONAL ENVIRONMENT PROTECTION AMENDMENT MEASURE (2013)

TOTAL PAHs

NAPHTHALENE

NAPHTHALENE

400

NL

170

0.7

3.7 <0.1 0.4

4

400

NL

170

0.7

0-0.15

SAND <0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH2

0.5-0.8

SAND <0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH2

4.5-4.8

CLAY

0.3 1.6

4

400

NL

170

0.7

BH2

5.1-5.25

CLAY <0.3 <0.8 <0.1 <0.1

4

400

0

170

0.7

BH3

0-0.1

SAND <0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH3

1.5-1.8

CLAY

1

6.8 <0.1 0.7

4

400

NL

170

0.7

BH4

0-0.15

SAND

0.8

6.1 <0.1 0.6

4

400

3

170

0.7

BH5

0.1-0.4

CLAY

0.3

2.4 <0.1 0.2

4

400

5

170

0.7

BH5

0.6-0.7

CLAY <0.3 <0.8 <0.1 <0.1

4

400

5

170

0.7

BH6

0.6-0.7

CLAY <0.3 <0.8 <0.1 <0.1

4

400

5

170

0.7

BH7

0.15-0.45

SAND <0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH7

1.4-1.7

CLAY <0.3 <0.8 <0.1 <0.1

4

400

NL

170

0.7

BH8

0.2-0.4

SAND <0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH9

0.2-0.5

SAND <0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH9

2.0-2.3

CLAY

4.8 <0.1 0.5

4

400

NL

170

0.7

BH9

2.55-2.65

CLAY <0.3 <0.8 <0.1 <0.1

4

400

NL

170

0.7

BH10

0.23-0.5

CLAY <0.3 <0.8 <0.1 <0.1

4

400

5

170

0.7

BH10

0.55-0.65

CLAY <0.3 <0.8 <0.1 <0.1

4

400

5

170

0.7

S1

2.0-2.3

CLAY

4

400

NL

170

0.7

BH1

1.5-1.8

BH1

3.15-3.25

BH2

0.7

2.3

0.8

1

TOTAL PAHs

4

SAND

Depth (m) Soil type

BaP TEQ

BaP TEQ

BENZO(a)PYRENE (BaP)

Generic Ecological Ecological Screening Investigation Level (EIL) - Level (ESL) - Urban Urban residential residential

CLAY <0.3 <0.8 <0.1 <0.1

Sample Location

16

NAPHTHALENE

PAH (mg/kg)

BENZO(a)PYRENE (BaP)

Health-based Investigation Health Screening Level Levels (HIL) B a(HSL) B - High density Residential B residential

10.6 <0.1 0.9

Limits of Reporting (LOR) 0.2 0.8 0.1 0.1 Notes: a: Residential w ith minimal opportunities for soil access; includes dw ellings w ith fully and permanently paved yard space such as highrise buildings and apartments. NL: Not Limimting

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

(mg/kg)

(mg/kg)

(mg/kg)

PCB

Cyanides

Phenols

TABLE H ORGANOCHLORINE PESTICIDES (OCP), POLYCHLORINATED BIPHENYLS (PCB), CYANIDES & PHENOLS TEST DISCRETE SAMPLE(S) (Ref No: 13188/2-AA)

BH1

1.5-1.8

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

-

-

-

BH1

3.15-3.25

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

-

-

-

BH2

0-0.15

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

-

-

-

BH2

0.5-0.8

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

0.2

0.6

BH2

4.5-4.8

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.1

0.4

BH2

5.1-5.25

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.1

<0.1

BH3

0-0.1

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

-

-

-

BH3

1.5-1.8

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

0.1

0.4

BH4

0-0.15

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

-

-

-

BH5

0.1-0.4

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

0.2

0.3

BH5

0.6-0.7

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

0.1

0.2

BH6

0.6-0.7

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

-

-

-

BH7

0.15-0.45

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

-

-

-

BH7

1.4-1.7

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

-

-

-

BH8

0.2-0.4

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

-

-

-

BH9

0.2-0.5

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.1

0.2

BH9

2.0-2.3

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

0.1

0.4

BH9

2.55-2.65

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.1

0.1

BH10

0.23-0.5

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.1

<0.1

BH10

0.55-0.65

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.1

<0.1

0.1

0.1

0.15

0.2

0.1

0.1

0.5

0.6

0.2

1

0.1

0.1

15

10

10

20

500

20

400

600

90

1

300

45000

Limits of Reporting (LOR)

CHLORDANE (alpha & gamma)

DDT

DDD+DDE+DDT

ENDOSULFAN (alpha, beta & sulphate)

MIREX

METHOXYCHLOR

ENDRIN

ALDRIN+DIELDRIN

Depth (m)

HEPTACHLOR

Sample Location

HEXACHLOROBENZENE (HCB)

OCP (mg/kg)

0.2

NATIONAL ENVIRONMENT PROTECTION AMENDMENT MEASURE (2013) a

Health-based Investigation Levels (HIL) B - Residential B Ecological Investigation Levels (EIL) - Urban residential Notes:

180

b

a: Residential w ith minimal opportunities for soil access; includes dw ellings w ith fully and permanently paved yard space such as high-rise buildings and apartments. b: Generic EIL for DDT

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

TABLE I ASBESTOS TEST RESULTS DISCRETE SAMPLE(S) (Ref No: 13188/2-AA) Sample Location

Depth (m)

ASBESTOS

BH1

1.5-1.8

No Asbestos Found

BH2

0-0.15

No Asbestos Found

BH2

0.5-0.8

No Asbestos Found

BH2

4.5-4.8

No Asbestos Found

BH3

0-0.1

No Asbestos Found

BH3

1.5-1.8

No Asbestos Found

BH4

0-0.15

No Asbestos Found

BH5

0.1-0.4

No Asbestos Found

BH5

0.6-0.7

No Asbestos Found

BH7

0.15-0.45

No Asbestos Found

BH7

1.4-1.7

No Asbestos Found

BH9

0.2-0.5

No Asbestos Found

BH9

2.0-2.3

No Asbestos Found

BH10

0.23-0.5

No Asbestos Found

Nix Anderson Pty Ltd AN.sf/11.09.2014


G EOTECHNIQUE PTY LTD

APPENDIX A

AREAS OF ENVIRONMENTAL CONCERN FROM SLR CONSULTING AUSTRALIA PTY LTD

Nix Anderson Pty Ltd AN.sf/11.09.2014


AEC 2

AEC 3

AEC 1

AEC 10

AEC 11 AEC 9

AEC 6

AEC 8

AEC 7

AEC 5

AEC 4

Geotechnique Borehole

Recommended direction for the existing boreholes to be moved


Table

Areas of Environmental Concern and Contaminants of Potential Concern

ID

AEC

Contaminants of Potential Concern

AEC 1

Former above ground tanks (ASTs)

Hydrocarbons, metals, asbestos

AEC 2

Former building at the site

Metals, asbestos, pesticides

AEC 3

Reclaimed land

Metals, hydrocarbons, pesticides, asbestos

AEC 4

Potential underground fuel tanks and the transformer area

Hydrocarbons, metals, asbestos, PCBs

AEC 5

Potential underground fuel tanks

Hydrocarbons, metals, aesthetics

AEC 6

Filled area within the vicinity of the administration building

Hydrocarbons, metals, asbestos

AEC 7

Storage of liquid nitrogen, phosphorous acid and hydrochloric acid

AEC 8

Caustic soda room, ejector’s room and separator’s room

AEC 9

Grout area and oil water separator room

Hydrocarbons, metals

AEC 10

Former stockpile area

Hydrocarbons, metals, asbestos

AEC 11

Trucks manoeuvring area

Hydrocarbons, metals, asbestos


G EOTECHNIQUE PTY LTD

APPENDIX B

BUSHELL’S HISTORY

Nix Anderson Pty Ltd AN.sf/11.09.2014


8/28/2014

Bushells | History

BUSHELLS HISTORY Alfred Thomas Bushell, founder of Bushells Australia, was born 25th May 1833. The Bushells family were heavily involved in the tea business, Alfred being a Tea Dealer who employed 50 men and 45 boys, whilst his wife Agnes was the sister of the founder of Brooke Bond, the English Tea Company. Following the death of his wife, Agnes in the early 1880's, Alfred traveled to Brisbane and by 1883 was trading in Brisbane selling both tea and coffee from a shop. Some years later, two of Alfred's sons started selling tea in Sydney trading as Bushell and Company - the Tea Men. The Sydney business was expanded from selling tea on a roadside stall to selling tea wholesale. In 1899 the business expanded further when a branch was opened in Melbourne. By 1902 Alfred and his sons, Walter and Phillip, were well established as tea traders, but all was not well. The sons disagreed with the way their father was running the business and on 14th July 1903 the partnership with father Alfred was dissolved. Alfred retained Queensland while Walter and Phillip took control of Sydney and Melbourne. It appears to have been an amicable parting of the ways as the brothers continued to use their father's picture on the packet to attract the more conservative customers. In 1908, Alfred was contemplating retiring from business and was 'desirous of assigning' the Queensland business to the two sons. A memorandum of agreement stated that Alfred had the 'express desire that the surname shall continue to be identified with the business'. Following Alfred's death in 1910, Bushells Ltd was registered as public company. In 1915 an agent was appointed in Western Australia. By 1918 Bushells Ltd had expanded into Tasmania and South Australia, but this was not without its problems. The company had over extended itself and the bank was proving difficult in assisting with the cash flow problems. It was later reported that Phillip was 'really' worried and called the staff together to explain the situation. According to an interview at the time, 'The staff kicked in the money from their own resources. The crisis was overcome with money from the employees. Most of them decided to be paid back in shares rather than cash, and many finished up very well off'. Land was purchased in 1920 in the area now known as 'The Rocks' in Sydney. It was here that Bushells was to build its seven-story head office and incorporate new tea blending and packing methods of both tea and coffee. This was to remain the head office and tea factory for the next 40 years. In 1937 Bushells Ltd formed a company in New Zealand. To introduce their product to New Zealand the company sent every housewife on the electoral roll a personally addressed letter together with a card entitling her to a half pound (225g) of tea, completely free of charge. This quickly established the company and within a year it had a huge section of the tea market. In about 1945, J.A.D. Gibson Pty Ltd, who had previously sold the tea division of their business to Robert Timms, was itself taken over by Bushells. At this time Gibsons was manufacturing coffee essence and roasting coffee in Sydney and in Newcastle. In 1955 Bushells took over their long time rival in the New South Wales market, Inglis Ltd. The purchase of the company brought with it a significant number of brands ranging from matches (Red Head) to canned fish, sauces, wine and spirits and a flour mill in Ultimo that produced a type of porridge. There is even a record of owning a patent for a 'clothes drying apparatus'. Included in the beverage list were the teas 'Billy Tea' 'Goldena', Aromatte, 'Kofe-Kol' and 'Uncle Tom's Pure Coffee'. For a number of http://www.bushellscoffee.com.au/about/history.asp

1/3


8/28/2014

Bushells | History

years the company continued to trade in its own name, but gradually the factories and depots were amalgamated into Bushells. In the mid 50's a decision was made to move the Bushells Head Office. Employees at the time state that the main reason for deciding to move west was the belief that the city itself was expanding that way. Several sites were examined before the current Concord site was chosen. According to records the purchase date is identified as being on Christmas Eve, 1956 and was for 85,000 pounds ($170,000). It is believed that a timber yard was operating on the site prior to the purchase, with a weatherboard building along one boundary leading onto a jetty sitting on piles. Apart from this the site was substantially clear and ready for immediate development, so indicative plans were drawn up and spray drying equipment and six instant coffee extractors were ordered from America. The initial design of the Concord factory was to accommodate tea packing and warehousing. Indications are that some tea production commenced at the Concord site early in 1958 and that the equipment was transferred from The Rocks. The Newcastle tea plant was closed in 1963, as progressively were the other factories in Perth, Queensland and Victoria. In 1978 the Bushells family made the decision to sell their shares and approached their cousins, Brooke, in England. The Brooke Bond company was still substantially owned by the Brooke family, but operated under the name of Brooke Bond Liebig Ltd. At the time, newspaper reports indicated that there was some resistance to a nonAustralian company purchasing the business, but the government was in the process of relaxing its policy of overseas ownership. Objections to the take over by Brooke Bond Liebig Ltd were overcome and following the sale of the shares, Bushells donated and established a public plaza. The plaza, known as 'Bushell Place', is in The Rocks area in Sydney. Throughout the 1980's the company continued to make substantial investments in its coffee business. The instant coffee extraction plant was rebuilt in 1981, a new continuous roaster for the instant coffee was installed in 1982 and a new instant coffee agglomerator in was installed in 1985. Unilever acquired the company through their purchase of the Brooke Bond business in 1988. In 1998, as part of an acquisition of coffee brands from Unilever, FreshFood Services Pty Ltd purchased the Bushells coffee brand. The tea brand still remains with Unilever. The coffee continues to be produced at the Concord Factory. FreshFood also purchased the New Zealand division of Bushells coffee.

© FreshFood Services Pty Ltd 2010. All rights reserved. Privacy Policy

http://www.bushellscoffee.com.au/about/history.asp

TO TOP OF PAGE

2/3


APPENDIX C

ENVIROLAB SERVICES CERTIFICATES OF ANALYSIS AND SGS ENVIRONMENTAL SERVICES ANALYTICAL REPORT


CERTIFICATE OF ANALYSIS

114771

Client: Geotechnique Pty Ltd PO Box 880 Penrith NSW 2751 Attention:

An Nguyen

Sample log in details: Your Reference: No. of samples: Date samples received / completed instructions received

13188/2, Concord 1 Soil 18/08/14 /

18/08/14

Analysis Details: Please refer to the following pages for results, methodology summary and quality control data. Samples were analysed as received from the client. Results relate specifically to the samples as received. Results are reported on a dry weight basis for solids and on an as received basis for other matrices. Please refer to the last page of this report for any comments relating to the results. Report Details: Date results requested by: / Issue Date: 25/08/14 / 22/08/14 Date of Preliminary Report: Not Issued NATA accreditation number 2901. This document shall not be reproduced except in full. Accredited for compliance with ISO/IEC 17025. Tests not covered by NATA are denoted with *. Results Approved By:

Envirolab Reference: Revision No:

114771 R 00

Page 1 of 17


Client Reference:

13188/2, Concord

vTRH(C6-C10)/BTEXN in Soil Our Reference:

UNITS

Your Reference

-------------

S1

Date Sampled

------------

14/08/2014

Type of sample

114771-1

Soil

Date extracted

-

19/08/2014

Date analysed

-

20/08/2014

TRHC 6 - C 9

mg/kg

<25

TRHC 6 - C 10

mg/kg

<25

vTPH C6 - C 10 less BTEX (F1)

mg/kg

<25

Benzene

mg/kg

<0.2

Toluene

mg/kg

<0.5

Ethylbenzene

mg/kg

<1

m+p-xylene

mg/kg

<2

o-Xylene

mg/kg

<1

naphthalene

mg/kg

<1

Surrogate aaa-Trifluorotoluene

%

133

Envirolab Reference: Revision No:

114771 R 00

Page 2 of 17


Client Reference:

13188/2, Concord

svTRH (C10-C40) in Soil Our Reference:

UNITS

Your Reference

-------------

S1

Date Sampled

------------

14/08/2014

Type of sample

114771-1

Soil

Date extracted Date analysed

-

19/08/2014

-

19/08/2014

TRHC 10 - C 14

mg/kg

<50

TRHC 15 - C 28

mg/kg

<100

TRHC 29 - C 36

mg/kg

<100

TRH >C10-C 16

mg/kg

<50

TRH >C10 - C 16 less Naphthalene (F2)

mg/kg

<50

TRH >C16-C 34

mg/kg

<100

TRH >C34-C 40

mg/kg

<100

%

90

Surrogate o-Terphenyl

Envirolab Reference: Revision No:

114771 R 00

Page 3 of 17


Client Reference:

13188/2, Concord

PAHs in Soil Our Reference:

UNITS

Your Reference

-------------

S1

Date Sampled

------------

14/08/2014

Type of sample

114771-1

Soil

Date extracted

-

19/08/2014

Date analysed

-

19/08/2014

Naphthalene

mg/kg

<0.1

Acenaphthylene

mg/kg

<0.1

Acenaphthene

mg/kg

<0.1

Fluorene

mg/kg

<0.1

Phenanthrene

mg/kg

0.8

Anthracene

mg/kg

0.2

Fluoranthene

mg/kg

1.6

Pyrene

mg/kg

1.7

Benzo(a)anthracene

mg/kg

0.7

Chrysene

mg/kg

0.7

Benzo(b,j+k)fluoranthene

mg/kg

1.4

Benzo(a)pyrene

mg/kg

0.93

Indeno(1,2,3-c,d)pyrene

mg/kg

0.6

Dibenzo(a,h)anthracene

mg/kg

<0.1

Benzo(g,h,i)perylene

mg/kg

0.5

Benzo(a)pyrene TEQ NEPM B1

mg/kg

1.0

Total Positive PAHs

mg/kg

9.1

Surrogate p-Terphenyl-d14

%

102

Envirolab Reference: Revision No:

114771 R 00

Page 4 of 17


Client Reference:

13188/2, Concord

Organochlorine Pesticides in soil Our Reference:

UNITS

Your Reference

-------------

S1

Date Sampled

------------

14/08/2014

Type of sample

114771-1

Soil

Date extracted

-

19/08/2014

Date analysed

-

19/08/2014

HCB

mg/kg

<0.1

alpha-BHC

mg/kg

<0.1

gamma-BHC

mg/kg

<0.1

beta-BHC

mg/kg

<0.1

Heptachlor

mg/kg

<0.1

delta-BHC

mg/kg

<0.1

Aldrin

mg/kg

<0.1

Heptachlor Epoxide

mg/kg

<0.1

gamma-Chlordane

mg/kg

<0.1

alpha-chlordane

mg/kg

<0.1

Endosulfan I

mg/kg

<0.1

pp-DDE

mg/kg

<0.1

Dieldrin

mg/kg

<0.1

Endrin

mg/kg

<0.1

pp-DDD

mg/kg

<0.1

Endosulfan II

mg/kg

<0.1

pp-DDT

mg/kg

<0.1

Endrin Aldehyde

mg/kg

<0.1

Endosulfan Sulphate

mg/kg

<0.1

Methoxychlor

mg/kg

<0.1

Surrogate TCMX

%

85

Envirolab Reference: Revision No:

114771 R 00

Page 5 of 17


Client Reference:

13188/2, Concord

PCBs in Soil Our Reference:

UNITS

Your Reference

-------------

S1

Date Sampled

------------

14/08/2014

Type of sample

114771-1

Soil

Date extracted

-

19/08/2014

Date analysed

-

19/08/2014

Arochlor 1016

mg/kg

<0.1

Arochlor 1221

mg/kg

<0.1

Arochlor 1232

mg/kg

<0.1

Arochlor 1242

mg/kg

<0.1

Arochlor 1248

mg/kg

<0.1

Arochlor 1254

mg/kg

<0.1

Arochlor 1260

mg/kg

<0.1

Surrogate TCLMX

%

85

Envirolab Reference: Revision No:

114771 R 00

Page 6 of 17


Client Reference:

13188/2, Concord

Total Phenolics in Soil Our Reference:

UNITS

Your Reference

-------------

S1

Date Sampled

------------

14/08/2014

Type of sample

114771-1

Soil

Date extracted

-

19/08/2014

Date analysed

-

19/08/2014

Total Phenolics (as Phenol)

mg/kg

<5

Envirolab Reference: Revision No:

114771 R 00

Page 7 of 17


Client Reference:

13188/2, Concord

Acid Extractable metals in soil Our Reference:

UNITS

Your Reference

-------------

S1

Date Sampled

------------

14/08/2014

Type of sample

114771-1

Soil

Date digested

-

19/08/2014

Date analysed

-

20/08/2014

Arsenic

mg/kg

20

Cadmium

mg/kg

<0.4

Chromium

mg/kg

25

Copper

mg/kg

32

Lead

mg/kg

50

Mercury

mg/kg

0.3

Nickel

mg/kg

3

Zinc

mg/kg

100

Envirolab Reference: Revision No:

114771 R 00

Page 8 of 17


Client Reference:

13188/2, Concord

Miscellaneous Inorg - soil Our Reference:

UNITS

Your Reference

-------------

S1

Date Sampled

------------

14/08/2014

Type of sample

114771-1

Soil

Date prepared

-

19/08/2014

Date analysed

-

19/08/2014

pH 1:5 soil:water

pH Units

7.2

Total Cyanide

mg/kg

<0.5

Envirolab Reference: Revision No:

114771 R 00

Page 9 of 17


Client Reference:

13188/2, Concord

Moisture Our Reference:

UNITS

Your Reference

-------------

S1

Date Sampled

------------

14/08/2014

Type of sample

114771-1

Soil

Date prepared

-

19/08/2014

Date analysed

-

20/08/2014

Moisture

%

22

Envirolab Reference: Revision No:

114771 R 00

Page 10 of 17


Client Reference: Method ID

13188/2, Concord

Methodology Summary

Org-016

Soil samples are extracted with methanol and spiked into water prior to analysing by purge and trap GC-MS. Water samples are analysed directly by purge and trap GC-MS. F1 = (C6-C10)-BTEX as per NEPM B1 Guideline on Investigation Levels for Soil and Groundwater.

Org-014

Soil samples are extracted with methanol and spiked into water prior to analysing by purge and trap GC-MS.

Org-003

Soil samples are extracted with Dichloromethane/Acetone and waters with Dichloromethane and analysed by GC-FID. F2 = (>C10-C16)-Naphthalene as per NEPM B1 Guideline on Investigation Levels for Soil and Groundwater (HSLs Tables 1A (3, 4)). Note Naphthalene is determined from the VOC analysis.

Org-012 subset

Soil samples are extracted with Dichloromethane/Acetone and waters with Dichloromethane and analysed by GC-MS. Benzo(a)pyrene TEQ as per NEPM B1 Guideline on Investigation Levels for Soil and Groundwater 2013.

Org-005

Soil samples are extracted with dichloromethane/acetone and waters with dichloromethane and analysed by GC with dual ECD's.

Org-006

Soil samples are extracted with dichloromethane/acetone and waters with dichloromethane and analysed by GC-ECD.

Inorg-031

Total Phenolics by segmented flow analyser (in line distillation with colourimetric finish). Solids are extracted in a caustic media prior to analysis.

Metals-020 ICPAES

Determination of various metals by ICP-AES.

Metals-021 CVAAS

Determination of Mercury by Cold Vapour AAS.

Inorg-001

pH - Measured using pH meter and electrode in accordance with APHA 22nd ED, 4500-H+. Please note that the results for water analyses are indicative only, as analysis outside of the APHA storage times.

Inorg-014

Cyanide - free, total, weak acid dissociable by segmented flow analyser (in line dialysis with colourimetric finish). Solids are extracted in a caustic media prior to analysis.

Inorg-008

Moisture content determined by heating at 105+/-5 deg C for a minimum of 12 hours.

Envirolab Reference: Revision No:

114771 R 00

Page 11 of 17


Client Reference: QUALITY CONTROL

UNITS

PQL

METHOD

13188/2, Concord

Blank

Duplicate Sm#

vTRH(C6-C10)/BTEXN in Soil

Duplicate results

Spike Sm#

Spike % Recovery

Base ll Duplicate ll %RPD

Date extracted

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

Date analysed

-

20/08/2 014

[NT]

[NT]

LCS-1

20/08/2014

TRHC 6 - C 9

mg/kg

25

Org-016

<25

[NT]

[NT]

LCS-1

120%

TRHC 6 - C 10

mg/kg

25

Org-016

<25

[NT]

[NT]

LCS-1

120%

Benzene

mg/kg

0.2

Org-016

<0.2

[NT]

[NT]

LCS-1

115%

Toluene

mg/kg

0.5

Org-016

<0.5

[NT]

[NT]

LCS-1

121%

Ethylbenzene

mg/kg

1

Org-016

<1

[NT]

[NT]

LCS-1

120%

m+p-xylene

mg/kg

2

Org-016

<2

[NT]

[NT]

LCS-1

122%

o-Xylene

mg/kg

1

Org-016

<1

[NT]

[NT]

LCS-1

130%

naphthalene

mg/kg

1

Org-014

<1

[NT]

[NT]

[NR]

[NR]

Surrogate aaaTrifluorotoluene

%

Org-016

139

[NT]

[NT]

LCS-1

133%

Spike Sm#

Spike % Recovery

QUALITY CONTROL

UNITS

PQL

METHOD

Blank

Duplicate Sm#

svTRH (C10-C40) in Soil

Duplicate results Base ll Duplicate ll %RPD

Date extracted

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

Date analysed

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

TRHC 10 - C 14

mg/kg

50

Org-003

<50

[NT]

[NT]

LCS-1

85%

TRHC 15 - C 28

mg/kg

100

Org-003

<100

[NT]

[NT]

LCS-1

100%

TRHC 29 - C 36

mg/kg

100

Org-003

<100

[NT]

[NT]

LCS-1

86%

TRH >C10-C 16

mg/kg

50

Org-003

<50

[NT]

[NT]

LCS-1

85%

TRH >C16-C 34

mg/kg

100

Org-003

<100

[NT]

[NT]

LCS-1

100%

TRH >C34-C 40

mg/kg

100

Org-003

<100

[NT]

[NT]

LCS-1

86%

Org-003

85

[NT]

[NT]

LCS-1

93%

Spike Sm#

Spike % Recovery

Surrogate o-Terphenyl QUALITY CONTROL

% UNITS

PQL

METHOD

Blank

Duplicate Sm#

PAHs in Soil

Duplicate results Base ll Duplicate ll %RPD

Date extracted

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

Date analysed

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

Naphthalene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

LCS-1

101%

Acenaphthylene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

[NR]

[NR]

Acenaphthene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

[NR]

[NR]

Fluorene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

LCS-1

97%

Phenanthrene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

LCS-1

97%

Anthracene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

[NR]

[NR]

Fluoranthene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

LCS-1

100%

Envirolab Reference: Revision No:

114771 R 00

Page 12 of 17


Client Reference: QUALITY CONTROL

UNITS

PQL

METHOD

13188/2, Concord

Blank

Duplicate Sm#

PAHs in Soil

Duplicate results

Spike Sm#

Spike % Recovery

Base ll Duplicate ll %RPD

Pyrene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

LCS-1

100%

Benzo(a)anthracene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

[NR]

[NR]

Chrysene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

LCS-1

94%

Benzo(b,j+k) fluoranthene

mg/kg

0.2

Org-012 subset

<0.2

[NT]

[NT]

[NR]

[NR]

Benzo(a)pyrene

mg/kg

0.05

Org-012 subset

<0.05

[NT]

[NT]

LCS-1

104%

Indeno(1,2,3-c,d)pyrene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

[NR]

[NR]

Dibenzo(a,h)anthracene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

[NR]

[NR]

Benzo(g,h,i)perylene

mg/kg

0.1

Org-012 subset

<0.1

[NT]

[NT]

[NR]

[NR]

Surrogate p-Terphenyld14

%

Org-012 subset

99

[NT]

[NT]

LCS-1

98%

Spike Sm#

Spike % Recovery

QUALITY CONTROL

UNITS

PQL

METHOD

Blank

Duplicate Sm#

Organochlorine Pesticides in soil

Duplicate results Base ll Duplicate ll %RPD

Date extracted

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

Date analysed

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

HCB

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

[NR]

[NR]

alpha-BHC

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

LCS-1

89%

gamma-BHC

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

[NR]

[NR]

beta-BHC

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

LCS-1

86%

Heptachlor

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

LCS-1

86%

delta-BHC

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

[NR]

[NR]

Aldrin

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

LCS-1

92%

Heptachlor Epoxide

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

LCS-1

92%

gamma-Chlordane

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

[NR]

[NR]

alpha-chlordane

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

[NR]

[NR]

Endosulfan I

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

[NR]

[NR]

pp-DDE

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

LCS-1

95%

Dieldrin

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

LCS-1

82%

Endrin

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

LCS-1

94%

pp-DDD

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

LCS-1

96%

Endosulfan II

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

[NR]

[NR]

pp-DDT

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

[NR]

[NR]

Endrin Aldehyde

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

[NR]

[NR]

Endosulfan Sulphate

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

LCS-1

90%

Methoxychlor

mg/kg

0.1

Org-005

<0.1

[NT]

[NT]

[NR]

[NR]

Surrogate TCMX

%

Org-005

85

[NT]

[NT]

LCS-1

81%

Envirolab Reference: Revision No:

114771 R 00

Page 13 of 17


Client Reference: QUALITY CONTROL

UNITS

PQL

METHOD

13188/2, Concord

Blank

Duplicate Sm#

PCBs in Soil

Duplicate results

Spike Sm#

Spike % Recovery

Base ll Duplicate ll %RPD

Date extracted

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

Date analysed

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

Arochlor 1016

mg/kg

0.1

Org-006

<0.1

[NT]

[NT]

[NR]

[NR]

Arochlor 1221

mg/kg

0.1

Org-006

<0.1

[NT]

[NT]

[NR]

[NR]

Arochlor 1232

mg/kg

0.1

Org-006

<0.1

[NT]

[NT]

[NR]

[NR]

Arochlor 1242

mg/kg

0.1

Org-006

<0.1

[NT]

[NT]

[NR]

[NR]

Arochlor 1248

mg/kg

0.1

Org-006

<0.1

[NT]

[NT]

[NR]

[NR]

Arochlor 1254

mg/kg

0.1

Org-006

<0.1

[NT]

[NT]

LCS-1

106%

Arochlor 1260

mg/kg

0.1

Org-006

<0.1

[NT]

[NT]

[NR]

[NR]

Surrogate TCLMX QUALITY CONTROL

% UNITS

Org-006 PQL

METHOD

85 Blank

[NT] Duplicate Sm#

Total Phenolics in Soil

[NT] Duplicate results

LCS-1

76%

Spike Sm#

Spike % Recovery

Base ll Duplicate ll %RPD

Date extracted

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

Date analysed

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

Total Phenolics (as Phenol)

mg/kg

<5

[NT]

[NT]

LCS-1

101%

Blank

Duplicate Sm#

Spike Sm#

Spike % Recovery

QUALITY CONTROL

UNITS

5 PQL

Inorg-031 METHOD

Acid Extractable metals in soil

Duplicate results Base ll Duplicate ll %RPD

Date digested

-

19/08/2 014

[NT]

[NT]

LCS-2

19/08/2014

Date analysed

-

20/08/2 014

[NT]

[NT]

LCS-2

20/08/2014

Arsenic

mg/kg

4

Metals-020 ICP-AES

<4

[NT]

[NT]

LCS-2

103%

Cadmium

mg/kg

0.4

Metals-020 ICP-AES

<0.4

[NT]

[NT]

LCS-2

110%

Chromium

mg/kg

1

Metals-020 ICP-AES

<1

[NT]

[NT]

LCS-2

108%

Copper

mg/kg

1

Metals-020 ICP-AES

<1

[NT]

[NT]

LCS-2

106%

Lead

mg/kg

1

Metals-020 ICP-AES

<1

[NT]

[NT]

LCS-2

104%

Mercury

mg/kg

0.1

Metals-021 CV-AAS

<0.1

[NT]

[NT]

LCS-2

89%

Nickel

mg/kg

1

Metals-020 ICP-AES

<1

[NT]

[NT]

LCS-2

107%

Zinc

mg/kg

1

Metals-020 ICP-AES

<1

[NT]

[NT]

LCS-2

106%

Envirolab Reference: Revision No:

114771 R 00

Page 14 of 17


Client Reference: QUALITY CONTROL

UNITS

PQL

METHOD

13188/2, Concord

Blank

Duplicate Sm#

Miscellaneous Inorg - soil

Duplicate results

Spike Sm#

Spike % Recovery

Base ll Duplicate ll %RPD

Date prepared

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

Date analysed

-

19/08/2 014

[NT]

[NT]

LCS-1

19/08/2014

pH 1:5 soil:water

pH Units

Inorg-001

[NT]

[NT]

[NT]

LCS-1

101%

Total Cyanide

mg/kg

Inorg-014

<0.5

[NT]

[NT]

LCS-1

87%

Envirolab Reference: Revision No:

0.5

114771 R 00

Page 15 of 17


Client Reference:

13188/2, Concord

Report Comments:

Asbestos ID was analysed by Approved Identifier: Asbestos ID was authorised by Approved Signatory:

INS: Insufficient sample for this test NA: Test not required <: Less than

Envirolab Reference: Revision No:

114771 R 00

Not applicable for this job Not applicable for this job

PQL: Practical Quantitation Limit RPD: Relative Percent Difference >: Greater than

NT: Not tested NA: Test not required LCS: Laboratory Control Sample

Page 16 of 17


Client Reference:

13188/2, Concord

Quality Control Definitions Blank: This is the component of the analytical signal which is not derived from the sample but from reagents, glassware etc, can be determined by processing solvents and reagents in exactly the same manner as for samples. Duplicate : This is the complete duplicate analysis of a sample from the process batch. If possible, the sample selected should be one where the analyte concentration is easily measurable. Matrix Spike : A portion of the sample is spiked with a known concentration of target analyte. The purpose of the matrix spike is to monitor the performance of the analytical method used and to determine whether matrix interferences exist. LCS (Laboratory Control Sample) : This comprises either a standard reference material or a control matrix (such as a blank sand or water) fortified with analytes representative of the analyte class. It is simply a check sample. Surrogate Spike: Surrogates are known additions to each sample, blank, matrix spike and LCS in a batch, of compounds which are similar to the analyte of interest, however are not expected to be found in real samples. Laboratory Acceptance Criteria Duplicate sample and matrix spike recoveries may not be reported on smaller jobs, however, were analysed at a frequency to meet or exceed NEPM requirements. All samples are tested in batches of 20. The duplicate sample RPD and matrix spike recoveries for the batch were within the laboratory acceptance criteria. Filters, swabs, wipes, tubes and badges will not have duplicate data as the whole sample is generally extracted during sample extraction. Spikes for Physical and Aggregate Tests are not applicable. For VOCs in water samples, three vials are required for duplicate or spike analysis. Duplicates: <5xPQL - any RPD is acceptable; >5xPQL - 0-50% RPD is acceptable. Matrix Spikes, LCS and Surrogate recoveries: Generally 70-130% for inorganics/metals; 60-140% for organics and 10-140% for SVOC and speciated phenols is acceptable. In circumstances where no duplicate and/or sample spike has been reported at 1 in 10 and/or 1 in 20 samples respectively, the sample volume submitted was insufficient in order to satisfy laboratory QA/QC protocols. When samples are received where certain analytes are outside of recommended technical holding times (THTs), the analysis has proceeded. Where analytes are on the verge of breaching THTs, every effort will be made to analyse within the THT or as soon as practicable.

Envirolab Reference: Revision No:

114771 R 00

Page 17 of 17


ANALYTICAL REPORT

LABORATORY DETAILS

CLIENT DETAILS

Contact

An Nguyen

Manager

Huong Crawford

Client Address

Geotechnique

Laboratory Address

SGS Alexandria Environmental

Telephone

02 4722 2700

Telephone

+61 2 8594 0400

Facsimile

02 4722 6161

Facsimile

+61 2 8594 0499

Email

anguyen@geotech.com.au

Email

au.environmental.sydney@sgs.com

Project

13188-2 - Concord

SGS Reference

SE130614 R0

Order Number

(Not specified)

Report Number

0000089952

Samples

28

Date Reported

26/8/2014

Date Received

18/8/2014

Date Started

20/8/2014

P.O. Box 880 NSW 2751

Unit 16, 33 Maddox St Alexandria NSW 2015

COMMENTS

Accredited for compliance with ISO/IEC 17025. NATA accredited laboratory 2562(4354). Sample # 11:portion of the sample supplied has been sub-sampled for asbestos according to SGS In-house procedures. We therefore cannot guarantee that the sub-sample is representative of the entire sample supplied. SGS Environmental Services recommends supplying approximately 50-100g of sample in a separate container. No respirable fibres detected in all samples using trace analysis technique. Asbestos analysed by Approved Identifier Yusuf Kuthpudin.

SIGNATORIES

Andy Sutton

Dong Liang

Huong Crawford

Senior Organic Chemist

Metals/Inorganics Team Leader

Production Manager

Jaimie Cheung

Ly Kim Ha

Sheila Lepasana

Metals Chemist

Organic Section Head

Senior Technician

SGS Australia Pty Ltd ABN 44 000 964 278

Environmental Services

Unit 16 33 Maddox St PO Box 6432 Bourke Rd BC

Alexandria NSW 2015 Alexandria NSW 2015

Australia Australia

t +61 2 8594 0400

f +61 2 8594 0499

www.au.sgs.com

Member of the SGS Group


ANALYTICAL RESULTS

SE130614 R0

VOC’s in Soil [AN433/AN434] BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

BH3 1.5-1.8

BH5 0.1-0.4

BH5 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

11/8/2014

12/8/2014

13/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.004

SE130614.005

SE130614.006

SE130614.008

SE130614.010

SE130614.011

Benzene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Toluene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Ethylbenzene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

m/p-xylene

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

o-xylene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Naphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Total Xylenes*

mg/kg

0.30

<0.3

<0.3

<0.3

<0.3

<0.3

<0.3

Total BTEX*

mg/kg

0.60

<0.6

<0.6

<0.6

<0.6

<0.6

<0.6

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

14/8/2014

14/8/2014

14/8/2014

12/8/2014

12/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.016

SE130614.017

SE130614.018

SE130614.019

SE130614.020

SE130614.021

Benzene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Toluene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Ethylbenzene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

m/p-xylene

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

o-xylene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Naphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Total Xylenes*

mg/kg

0.30

<0.3

<0.3

<0.3

<0.3

<0.3

<0.3

Total BTEX*

mg/kg

0.60

<0.6

<0.6

<0.6

<0.6

<0.6

<0.6

Trip Spike TS1

Trip Spike TS2

SOIL

SOIL

-

-

12/8/2014

14/8/2014

PARAMETER

UOM

LOR

SE130614.022

SE130614.023

Benzene

mg/kg

0.10

[85%]

[79%]

Toluene

mg/kg

0.10

[79%]

[91%]

Ethylbenzene

mg/kg

0.10

[81%]

[95%]

m/p-xylene

mg/kg

0.20

[81%]

[97%]

o-xylene

mg/kg

0.10

[86%]

[97%]

Naphthalene

mg/kg

0.10

<0.1

<0.1

Total Xylenes*

mg/kg

0.30

-

-

Total BTEX*

mg/kg

0.60

-

-

26/08/2014

Page 2 of 25


ANALYTICAL RESULTS

SE130614 R0

Volatile Petroleum Hydrocarbons in Soil [AN433/AN434/AN410] BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

BH3 1.5-1.8

BH5 0.1-0.4

BH5 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

11/8/2014

12/8/2014

13/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.004

SE130614.005

SE130614.006

SE130614.008

SE130614.010

SE130614.011

Benzene (F0)

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

TRH C6-C9

mg/kg

20

<20

<20

<20

<20

<20

<20

TRH C6-C10

mg/kg

25.0

<25

<25

<25

<25

<25

<25

TRH C6-C10 minus BTEX (F1)

mg/kg

25.0

<25

<25

<25

<25

<25

<25

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

14/8/2014

14/8/2014

14/8/2014

12/8/2014

12/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.016

SE130614.017

SE130614.018

SE130614.019

SE130614.020

SE130614.021

Benzene (F0)

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

TRH C6-C9

mg/kg

20

<20

<20

<20

<20

<20

<20

TRH C6-C10

mg/kg

25.0

<25

<25

<25

<25

<25

<25

TRH C6-C10 minus BTEX (F1)

mg/kg

25.0

<25

<25

<25

<25

<25

<25

26/08/2014

Page 3 of 25


ANALYTICAL RESULTS

SE130614 R0

TRH (Total Recoverable Hydrocarbons) in Soil [AN403] BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

BH3 1.5-1.8

BH5 0.1-0.4

BH5 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

11/8/2014

12/8/2014

13/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.004

SE130614.005

SE130614.006

SE130614.008

SE130614.010

SE130614.011

TRH C10-C14

mg/kg

20

<20

<20

<20

<20

<20

<20

TRH C15-C28

mg/kg

45.0

<45

100

<45

<45

<45

<45

TRH C29-C36

mg/kg

45.0

<45

87

<45

<45

<45

<45

TRH C37-C40

mg/kg

100

<100

<100

<100

<100

<100

<100

TRH >C10-C16 (F2)

mg/kg

25.0

<25

<25

<25

<25

<25

<25

TRH >C10-C16 (F2) minus

mg/kg

25.0

<25

<25

<25

<25

<25

<25

Naphthalene TRH >C16-C34 (F3)

mg/kg

90

<90

160

<90

<90

<90

<90

TRH >C34-C40 (F4)

mg/kg

120

<120

<120

<120

<120

<120

<120

TRH C10-C36 Total

mg/kg

110

<110

190

<110

<110

<110

<110

TRH C10-C40 Total

mg/kg

210

<210

<210

<210

<210

<210

<210

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

14/8/2014

14/8/2014

14/8/2014

12/8/2014

12/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.016

SE130614.017

SE130614.018

SE130614.019

SE130614.020

SE130614.021

TRH C10-C14

mg/kg

20

<20

<20

<20

<20

<20

<20

TRH C15-C28

mg/kg

45.0

65

<45

<45

<45

<45

<45

TRH C29-C36

mg/kg

45.0

<45

<45

<45

<45

<45

<45

TRH C37-C40

mg/kg

100

<100

<100

<100

<100

<100

<100

TRH >C10-C16 (F2)

mg/kg

25.0

<25

<25

<25

<25

<25

<25

TRH >C10-C16 (F2) minus

mg/kg

25.0

<25

<25

<25

<25

<25

<25

Naphthalene TRH >C16-C34 (F3)

mg/kg

90

<90

<90

<90

<90

<90

<90

TRH >C34-C40 (F4)

mg/kg

120

<120

<120

<120

<120

<120

<120

TRH C10-C36 Total

mg/kg

110

<110

<110

<110

<110

<110

<110

TRH C10-C40 Total

mg/kg

210

<210

<210

<210

<210

<210

<210

26/08/2014

Page 4 of 25


ANALYTICAL RESULTS

SE130614 R0

PAH (Polynuclear Aromatic Hydrocarbons) in Soil [AN420] BH1 1.5-1.8

BH1 3.15-3.25

BH2 0-0.15

BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

7/8/2014

7/8/2014

11/8/2014

11/8/2014

11/8/2014

11/8/2014

PARAMETER

UOM

LOR

SE130614.001

SE130614.002

SE130614.003

SE130614.004

SE130614.005

SE130614.006

Naphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.3

<0.1

2-methylnaphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

1-methylnaphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Acenaphthylene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.2

<0.1

Acenaphthene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Fluorene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Phenanthrene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.8

<0.1

Anthracene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.2

<0.1

Fluoranthene

mg/kg

0.10

<0.1

0.5

<0.1

<0.1

2.4

<0.1

Pyrene

mg/kg

0.10

<0.1

0.5

<0.1

<0.1

3.1

<0.1

Benzo(a)anthracene

mg/kg

0.10

<0.1

0.3

<0.1

<0.1

1.1

<0.1

Chrysene

mg/kg

0.10

<0.1

0.3

<0.1

<0.1

1.1

<0.1

Benzo(b&j)fluoranthene

mg/kg

0.10

<0.1

0.5

<0.1

<0.1

1.8

<0.1

Benzo(k)fluoranthene

mg/kg

0.10

<0.1

0.3

<0.1

<0.1

0.8

<0.1

Benzo(b&j&k)fluoranthene

mg/kg

0.20

<0.2

0.7

<0.2

<0.2

2.6

<0.2

Benzo(a)pyrene

mg/kg

0.10

<0.1

0.4

<0.1

<0.1

1.6

<0.1

Indeno(1,2,3-cd)pyrene

mg/kg

0.10

<0.1

0.4

<0.1

<0.1

1.3

<0.1

Dibenzo(a&h)anthracene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.2

<0.1

Benzo(ghi)perylene

mg/kg

0.10

<0.1

0.4

<0.1

<0.1

1.2

<0.1

Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.20

<0.2

0.6

<0.2

<0.2

2.3

<0.2

-assume results <LOR=0* Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.30

<0.3

0.7

<0.3

<0.3

2.3

<0.3

-assume results <LOR=LOR* Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.20

<0.2

0.6

<0.2

<0.2

2.3

<0.2

mg/kg

0.80

<0.8

3.7

<0.8

<0.8

16

<0.8

BH3 0-0.1

BH3 1.5-1.8

BH4 0-0.15

BH5 0.1-0.4

BH5 0.6-0.7

BH6 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

12/8/2014

12/8/2014

12/8/2014

13/8/2014

13/8/2014

13/8/2014

-assume Total PAHresults <LOR=LOR/2*

PARAMETER

UOM

LOR

SE130614.007

SE130614.008

SE130614.009

SE130614.010

SE130614.011

SE130614.012

Naphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

2-methylnaphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

1-methylnaphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Acenaphthylene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Acenaphthene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Fluorene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Phenanthrene

mg/kg

0.10

<0.1

0.4

0.5

0.3

<0.1

<0.1

Anthracene

mg/kg

0.10

<0.1

0.1

0.1

<0.1

<0.1

<0.1

Fluoranthene

mg/kg

0.10

<0.1

1.0

1.0

0.5

0.2

<0.1

Pyrene

mg/kg

0.10

<0.1

1.2

1.2

0.4

0.2

<0.1

Benzo(a)anthracene

mg/kg

0.10

<0.1

0.6

0.5

0.2

<0.1

<0.1

Chrysene

mg/kg

0.10

<0.1

0.6

0.5

0.2

<0.1

<0.1

Benzo(b&j)fluoranthene

mg/kg

0.10

<0.1

0.7

0.6

0.2

<0.1

<0.1

Benzo(k)fluoranthene

mg/kg

0.10

<0.1

0.3

0.3

0.1

<0.1

<0.1

Benzo(b&j&k)fluoranthene

mg/kg

0.20

<0.2

1.0

0.9

0.3

<0.2

<0.2

Benzo(a)pyrene

mg/kg

0.10

<0.1

0.7

0.6

0.2

<0.1

<0.1

Indeno(1,2,3-cd)pyrene

mg/kg

0.10

<0.1

0.6

0.5

0.1

<0.1

<0.1

Dibenzo(a&h)anthracene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Benzo(ghi)perylene

mg/kg

0.10

<0.1

0.5

0.4

0.1

<0.1

<0.1

Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.20

<0.2

0.9

0.7

0.2

<0.2

<0.2

-assume results <LOR=0* Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.30

<0.3

1.0

0.8

0.3

<0.3

<0.3

-assume results <LOR=LOR* Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.20

<0.2

1.0

0.8

0.3

<0.2

<0.2

mg/kg

0.80

<0.8

6.8

6.1

2.4

<0.8

<0.8

-assume Total PAHresults <LOR=LOR/2*

26/08/2014

Page 5 of 25


ANALYTICAL RESULTS

SE130614 R0

PAH (Polynuclear Aromatic Hydrocarbons) in Soil [AN420] (continued) BH7 0.15-0.45

BH7 1.4-1.7

BH8 0.2-0.4

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

14/8/2014

14/8/2014

14/8/2014

14/8/2014

PARAMETER

UOM

LOR

SE130614.013

SE130614.014

SE130614.015

SE130614.016

SE130614.017

SE130614.018

Naphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

2-methylnaphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

1-methylnaphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Acenaphthylene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Acenaphthene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Fluorene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Phenanthrene

mg/kg

0.10

0.1

<0.1

0.1

<0.1

0.2

<0.1

Anthracene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Fluoranthene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.7

<0.1

Pyrene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.8

<0.1

Benzo(a)anthracene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.4

<0.1

Chrysene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.4

<0.1

Benzo(b&j)fluoranthene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.5

<0.1

Benzo(k)fluoranthene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.3

<0.1

Benzo(b&j&k)fluoranthene

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

0.8

<0.2

Benzo(a)pyrene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.5

<0.1

Indeno(1,2,3-cd)pyrene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.4

<0.1

Dibenzo(a&h)anthracene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Benzo(ghi)perylene

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

0.4

<0.1

Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.20

<0.2

<0.2

<0.2

<0.2

0.7

<0.2

-assume results <LOR=0* Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.30

<0.3

<0.3

<0.3

<0.3

0.8

<0.3

-assume results <LOR=LOR* Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.20

<0.2

<0.2

<0.2

<0.2

0.7

<0.2

mg/kg

0.80

<0.8

<0.8

<0.8

<0.8

4.8

<0.8

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

-

-

-

12/8/2014

12/8/2014

13/8/2014

-assume Total PAHresults <LOR=LOR/2*

PARAMETER

UOM

LOR

SE130614.019

SE130614.020

SE130614.021

Naphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

2-methylnaphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

1-methylnaphthalene

mg/kg

0.10

<0.1

<0.1

<0.1

Acenaphthylene

mg/kg

0.10

<0.1

<0.1

<0.1

Acenaphthene

mg/kg

0.10

<0.1

<0.1

<0.1

Fluorene

mg/kg

0.10

<0.1

<0.1

<0.1

Phenanthrene

mg/kg

0.10

<0.1

<0.1

0.2

Anthracene

mg/kg

0.10

<0.1

<0.1

<0.1

Fluoranthene

mg/kg

0.10

<0.1

<0.1

0.3

Pyrene

mg/kg

0.10

<0.1

<0.1

0.3

Benzo(a)anthracene

mg/kg

0.10

<0.1

<0.1

0.1

Chrysene

mg/kg

0.10

<0.1

<0.1

0.1

Benzo(b&j)fluoranthene

mg/kg

0.10

<0.1

<0.1

0.1

Benzo(k)fluoranthene

mg/kg

0.10

<0.1

<0.1

<0.1

Benzo(b&j&k)fluoranthene

mg/kg

0.20

<0.2

<0.2

<0.2

Benzo(a)pyrene

mg/kg

0.10

<0.1

<0.1

<0.1

Indeno(1,2,3-cd)pyrene

mg/kg

0.10

<0.1

<0.1

<0.1

Dibenzo(a&h)anthracene

mg/kg

0.10

<0.1

<0.1

<0.1

Benzo(ghi)perylene

mg/kg

0.10

<0.1

<0.1

<0.1

Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.20

<0.2

<0.2

<0.2

-assume results <LOR=0* Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.30

<0.3

<0.3

<0.3

-assume results <LOR=LOR* Carcinogenic PAHs (as BaP TEQ)

TEQ (mg/kg)

0.20

<0.2

<0.2

<0.2

mg/kg

0.80

<0.8

<0.8

1.5

-assume Total PAHresults <LOR=LOR/2*

26/08/2014

Page 6 of 25


ANALYTICAL RESULTS

SE130614 R0

OC Pesticides in Soil [AN400/AN420] BH1 1.5-1.8

BH1 3.15-3.25

BH2 0-0.15

BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

7/8/2014

7/8/2014

11/8/2014

11/8/2014

11/8/2014

11/8/2014

PARAMETER

UOM

LOR

SE130614.001

SE130614.002

SE130614.003

SE130614.004

SE130614.005

SE130614.006

Hexachlorobenzene (HCB)

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Alpha BHC

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Lindane

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Heptachlor

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Aldrin

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Beta BHC

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Delta BHC

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Heptachlor epoxide

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

o,p'-DDE

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Alpha Endosulfan

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Gamma Chlordane

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Alpha Chlordane

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

trans-Nonachlor

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

p,p'-DDE

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Dieldrin

mg/kg

0.050

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

Endrin

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

o,p'-DDD

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

o,p'-DDT

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Beta Endosulfan

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

p,p'-DDD

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

p,p'-DDT

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Endosulfan sulphate

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Endrin Aldehyde

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Methoxychlor

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Endrin Ketone

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Isodrin

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Mirex

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

26/08/2014

Page 7 of 25


ANALYTICAL RESULTS

SE130614 R0

OC Pesticides in Soil [AN400/AN420] (continued) BH3 0-0.1

BH3 1.5-1.8

BH4 0-0.15

BH5 0.1-0.4

BH5 0.6-0.7

BH6 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

12/8/2014

12/8/2014

12/8/2014

13/8/2014

13/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.007

SE130614.008

SE130614.009

SE130614.010

SE130614.011

SE130614.012

Hexachlorobenzene (HCB)

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Alpha BHC

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Lindane

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Heptachlor

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Aldrin

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Beta BHC

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Delta BHC

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Heptachlor epoxide

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

o,p'-DDE

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Alpha Endosulfan

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Gamma Chlordane

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Alpha Chlordane

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

trans-Nonachlor

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

p,p'-DDE

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Dieldrin

mg/kg

0.050

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

Endrin

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

o,p'-DDD

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

o,p'-DDT

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Beta Endosulfan

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

p,p'-DDD

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

p,p'-DDT

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Endosulfan sulphate

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Endrin Aldehyde

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Methoxychlor

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Endrin Ketone

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Isodrin

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Mirex

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

26/08/2014

Page 8 of 25


ANALYTICAL RESULTS

SE130614 R0

OC Pesticides in Soil [AN400/AN420] (continued) BH7 0.15-0.45

BH7 1.4-1.7

BH8 0.2-0.4

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

14/8/2014

14/8/2014

14/8/2014

14/8/2014

PARAMETER

UOM

LOR

SE130614.013

SE130614.014

SE130614.015

SE130614.016

SE130614.017

SE130614.018

Hexachlorobenzene (HCB)

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Alpha BHC

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Lindane

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Heptachlor

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Aldrin

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Beta BHC

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Delta BHC

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Heptachlor epoxide

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

o,p'-DDE

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Alpha Endosulfan

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Gamma Chlordane

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Alpha Chlordane

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

trans-Nonachlor

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

p,p'-DDE

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Dieldrin

mg/kg

0.050

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

Endrin

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

o,p'-DDD

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

o,p'-DDT

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Beta Endosulfan

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

p,p'-DDD

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

p,p'-DDT

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Endosulfan sulphate

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Endrin Aldehyde

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Methoxychlor

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Endrin Ketone

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Isodrin

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

Mirex

mg/kg

0.10

<0.1

<0.1

<0.1

<0.1

<0.1

<0.1

26/08/2014

Page 9 of 25


ANALYTICAL RESULTS

SE130614 R0

OC Pesticides in Soil [AN400/AN420] (continued) BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

-

-

-

12/8/2014

12/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.019

SE130614.020

SE130614.021

Hexachlorobenzene (HCB)

mg/kg

0.10

<0.1

<0.1

<0.1

Alpha BHC

mg/kg

0.10

<0.1

<0.1

<0.1

Lindane

mg/kg

0.10

<0.1

<0.1

<0.1

Heptachlor

mg/kg

0.10

<0.1

<0.1

<0.1

Aldrin

mg/kg

0.10

<0.1

<0.1

<0.1

Beta BHC

mg/kg

0.10

<0.1

<0.1

<0.1

Delta BHC

mg/kg

0.10

<0.1

<0.1

<0.1

Heptachlor epoxide

mg/kg

0.10

<0.1

<0.1

<0.1

o,p'-DDE

mg/kg

0.10

<0.1

<0.1

<0.1

Alpha Endosulfan

mg/kg

0.20

<0.2

<0.2

<0.2

Gamma Chlordane

mg/kg

0.10

<0.1

<0.1

<0.1

Alpha Chlordane

mg/kg

0.10

<0.1

<0.1

<0.1

trans-Nonachlor

mg/kg

0.10

<0.1

<0.1

<0.1

p,p'-DDE

mg/kg

0.10

<0.1

<0.1

<0.1

Dieldrin

mg/kg

0.050

<0.05

<0.05

<0.05

Endrin

mg/kg

0.20

<0.2

<0.2

<0.2

o,p'-DDD

mg/kg

0.10

<0.1

<0.1

<0.1

o,p'-DDT

mg/kg

0.10

<0.1

<0.1

<0.1

Beta Endosulfan

mg/kg

0.20

<0.2

<0.2

<0.2

p,p'-DDD

mg/kg

0.10

<0.1

<0.1

<0.1

p,p'-DDT

mg/kg

0.10

<0.1

<0.1

<0.1

Endosulfan sulphate

mg/kg

0.10

<0.1

<0.1

<0.1

Endrin Aldehyde

mg/kg

0.10

<0.1

<0.1

<0.1

Methoxychlor

mg/kg

0.10

<0.1

<0.1

<0.1

Endrin Ketone

mg/kg

0.10

<0.1

<0.1

<0.1

Isodrin

mg/kg

0.10

<0.1

<0.1

<0.1

Mirex

mg/kg

0.10

<0.1

<0.1

<0.1

26/08/2014

Page 10 of 25


ANALYTICAL RESULTS

SE130614 R0

PCBs in Soil [AN400/AN420] BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

BH3 1.5-1.8

BH5 0.1-0.4

BH5 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

11/8/2014

12/8/2014

13/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.004

SE130614.005

SE130614.006

SE130614.008

SE130614.010

SE130614.011

Arochlor 1016

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1221

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1232

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1242

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1248

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1254

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1260

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1262

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1268

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Total PCBs (Arochlors)

mg/kg

1.0

<1

<1

<1

<1

<1

<1

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

14/8/2014

14/8/2014

14/8/2014

12/8/2014

12/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.016

SE130614.017

SE130614.018

SE130614.019

SE130614.020

SE130614.021

Arochlor 1016

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1221

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1232

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1242

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1248

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1254

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1260

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1262

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Arochlor 1268

mg/kg

0.20

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

Total PCBs (Arochlors)

mg/kg

1.0

<1

<1

<1

<1

<1

<1

26/08/2014

Page 11 of 25


ANALYTICAL RESULTS

SE130614 R0

Total Phenolics in Soil [AN289] BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

BH3 1.5-1.8

BH5 0.1-0.4

BH5 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

11/8/2014

12/8/2014

13/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.004

SE130614.005

SE130614.006

SE130614.008

SE130614.010

SE130614.011

Total Phenols

mg/kg

0.10

0.6

0.4

<0.1

0.4

0.3

0.2

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

14/8/2014

14/8/2014

14/8/2014

12/8/2014

12/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.016

SE130614.017

SE130614.018

SE130614.019

SE130614.020

SE130614.021

Total Phenols

mg/kg

0.10

0.2

0.4

0.1

<0.1

<0.1

0.1

26/08/2014

Page 12 of 25


ANALYTICAL RESULTS

SE130614 R0

Total Cyanide in soil by Discrete Analyser (Aquakem) [AN077/AN287] BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

BH3 1.5-1.8

BH5 0.1-0.4

BH5 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

11/8/2014

12/8/2014

13/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.004

SE130614.005

SE130614.006

SE130614.008

SE130614.010

SE130614.011

Total Cyanide

mg/kg

0.10

0.2

<0.1

<0.1

0.1

0.2

0.1

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

14/8/2014

14/8/2014

14/8/2014

12/8/2014

12/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.016

SE130614.017

SE130614.018

SE130614.019

SE130614.020

SE130614.021

Total Cyanide

mg/kg

0.10

<0.1

0.1

<0.1

<0.1

<0.1

0.2

26/08/2014

Page 13 of 25


ANALYTICAL RESULTS

SE130614 R0

pH in soil (1:5) [AN101]

PARAMETER

pH

PARAMETER

pH

PARAMETER

pH

PARAMETER

pH

26/08/2014

BH1 1.5-1.8

BH1 3.15-3.25

BH2 0-0.15

BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

7/8/2014

7/8/2014

11/8/2014

11/8/2014

11/8/2014

11/8/2014

UOM

LOR

SE130614.001

SE130614.002

SE130614.003

SE130614.004

SE130614.005

SE130614.006

pH Units

-

4.3

5.9

5.3

5.8

8.0

7.6

BH3 0-0.1

BH3 1.5-1.8

BH4 0-0.15

BH5 0.1-0.4

BH5 0.6-0.7

BH6 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

12/8/2014

12/8/2014

12/8/2014

13/8/2014

13/8/2014

13/8/2014

UOM

LOR

SE130614.007

SE130614.008

SE130614.009

SE130614.010

SE130614.011

SE130614.012

pH Units

-

6.1

7.0

7.5

6.0

5.9

4.8

BH7 0.15-0.45

BH7 1.4-1.7

BH8 0.2-0.4

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

14/8/2014

14/8/2014

14/8/2014

14/8/2014

UOM

LOR

SE130614.013

SE130614.014

SE130614.015

SE130614.016

SE130614.017

SE130614.018

pH Units

-

9.1

6.2

7.8

8.4

6.5

5.2

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

-

-

-

12/8/2014

12/8/2014

13/8/2014

UOM

LOR

SE130614.019

SE130614.020

SE130614.021

pH Units

-

6.5

4.7

5.7

Page 14 of 25


ANALYTICAL RESULTS

SE130614 R0

Exchangeable Cations and Cation Exchange Capacity (CEC/ESP/SAR) [AN122] BH1 1.5-1.8

BH1 3.15-3.25

BH2 0-0.15

BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

7/8/2014

7/8/2014

11/8/2014

11/8/2014

11/8/2014

11/8/2014

PARAMETER

UOM

LOR

SE130614.001

SE130614.002

SE130614.003

SE130614.004

SE130614.005

SE130614.006

Exchangeable Sodium, Na

mg/kg

2.0

200

110

24

36

400

700

Exchangeable Sodium, Na

meq/100g

0.010

0.89

0.49

0.10

0.16

1.7

3.1

%

0.10

13.3

6.5

1.1

1.6

6.9

22.7

Exchangeable Sodium Percentage* Exchangeable Potassium, K

mg/kg

2.0

93

100

220

120

110

280

Exchangeable Potassium, K

meq/100g

0.010

0.24

0.26

0.56

0.30

0.29

0.70

Exchangeable Potassium

%

0.10

3.6

3.4

5.9

3.0

1.1

5.2

Percentage* Calcium, Ca Exchangeable

mg/kg

2.0

570

1000

1200

1400

3800

1000

Exchangeable Calcium, Ca

meq/100g

0.010

2.8

5.2

6.2

7.1

19

5.0

%

0.10

42.7

69.6

65.1

72.4

74.2

37.3 570

Exchangeable Calcium Percentage* Exchangeable Magnesium, Mg

mg/kg

2.0

330

190

320

280

550

Exchangeable Magnesium, Mg

meq/100g

0.020

2.7

1.5

2.7

2.3

4.5

4.7

Exchangeable Magnesium

%

0.10

40.5

20.5

27.9

23.0

17.8

34.8

Percentage* Cation Exchange Capacity

meq/100g

0.020

6.7

7.5

9.5

9.8

25

13

BH3 0-0.1

BH3 1.5-1.8

BH4 0-0.15

BH5 0.1-0.4

BH5 0.6-0.7

BH6 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

12/8/2014

12/8/2014

12/8/2014

13/8/2014

13/8/2014

13/8/2014 SE130614.012

PARAMETER

UOM

LOR

SE130614.007

SE130614.008

SE130614.009

SE130614.010

SE130614.011

Exchangeable Sodium, Na

mg/kg

2.0

33

26

31

48

22

63

Exchangeable Sodium, Na

meq/100g

0.010

0.14

0.11

0.14

0.21

0.10

0.27 4.7

Exchangeable Sodium Percentage*

%

0.10

2.0

1.0

0.8

1.9

1.4

Exchangeable Potassium, K

mg/kg

2.0

120

74

92

130

70

45

Exchangeable Potassium, K

meq/100g

0.010

0.31

0.19

0.24

0.34

0.18

0.12

Exchangeable Potassium

%

0.10

4.2

1.6

1.3

3.2

2.6

2.0

Percentage* Exchangeable Calcium, Ca

mg/kg

2.0

1100

2000

3300

1700

1200

530

Exchangeable Calcium, Ca

meq/100g

0.010

5.5

10

16

8.6

5.9

2.7

%

0.10

75.6

86.5

90.4

79.1

85.1

45.2 350

Exchangeable Calcium Percentage* Exchangeable Magnesium, Mg

mg/kg

2.0

160

160

170

210

91

Exchangeable Magnesium, Mg

meq/100g

0.020

1.3

1.3

1.4

1.7

0.75

2.8

Exchangeable Magnesium

%

0.10

18.2

10.9

7.6

15.8

10.9

48.1

Percentage* Cation Exchange Capacity

meq/100g

0.020

7.3

12

18

11

6.9

5.9

BH7 0.15-0.45

BH7 1.4-1.7

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

BH10 0.23-0.5

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

14/8/2014

14/8/2014

14/8/2014

12/8/2014 SE130614.019

PARAMETER

UOM

LOR

SE130614.013

SE130614.014

SE130614.016

SE130614.017

SE130614.018

Exchangeable Sodium, Na

mg/kg

2.0

170

180

300

170

180

140

Exchangeable Sodium, Na

meq/100g

0.010

0.73

0.80

1.3

0.74

0.79

0.59 3.9

Exchangeable Sodium Percentage*

%

0.10

8.3

10.2

3.8

4.9

14.2

Exchangeable Potassium, K

mg/kg

2.0

56

88

97

160

99

85

Exchangeable Potassium, K

meq/100g

0.010

0.14

0.23

0.25

0.41

0.25

0.22

Exchangeable Potassium

%

0.10

1.6

2.9

0.7

2.7

4.6

1.4

Percentage* Exchangeable Calcium, Ca

mg/kg

2.0

1100

820

5600

2400

320

1700

Exchangeable Calcium, Ca

meq/100g

0.010

5.6

4.1

28

12

1.6

8.4

%

0.10

64.0

52.8

83.0

79.1

29.2

56.2 700

Exchangeable Calcium Percentage* Exchangeable Magnesium, Mg

mg/kg

2.0

280

330

510

250

350

Exchangeable Magnesium, Mg

meq/100g

0.020

2.3

2.7

4.2

2.0

2.9

5.8

Exchangeable Magnesium

%

0.10

26.1

34.1

12.5

13.3

51.9

38.4

Percentage* Cation Exchange Capacity

meq/100g

0.020

8.8

7.8

34

15

5.5

15

26/08/2014

Page 15 of 25


ANALYTICAL RESULTS

SE130614 R0

Exchangeable Cations and Cation Exchange Capacity (CEC/ESP/SAR) [AN122] (continued) BH10 0.55-0.65 SOIL 12/8/2014 PARAMETER

UOM

LOR

Exchangeable Sodium, Na

mg/kg

2.0

96

Exchangeable Sodium, Na

meq/100g

0.010

0.42 6.9

Exchangeable Sodium Percentage*

SE130614.020

%

0.10

Exchangeable Potassium, K

mg/kg

2.0

74

Exchangeable Potassium, K

meq/100g

0.010

0.19

Exchangeable Potassium

%

0.10

3.1

Percentage* Calcium, Ca Exchangeable

mg/kg

2.0

540

Exchangeable Calcium, Ca

meq/100g

0.010

2.7

%

0.10

44.7 340

Exchangeable Calcium Percentage* Exchangeable Magnesium, Mg

mg/kg

2.0

Exchangeable Magnesium, Mg

meq/100g

0.020

2.7

Exchangeable Magnesium

%

0.10

45.3

Percentage* Cation Exchange Capacity

meq/100g

0.020

6.1

26/08/2014

Page 16 of 25


ANALYTICAL RESULTS

SE130614 R0

TOC in Soil [AN188] BH1 1.5-1.8

BH1 3.15-3.25

BH2 0-0.15

BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

7/8/2014

7/8/2014

11/8/2014

11/8/2014

11/8/2014

11/8/2014

PARAMETER

UOM

LOR

SE130614.001

SE130614.002

SE130614.003

SE130614.004

SE130614.005

SE130614.006

Total Organic Carbon

%w/w

0.050

0.10

1.6

4.3

1.9

3.3

0.19

BH3 0-0.1

BH3 1.5-1.8

BH4 0-0.15

BH5 0.1-0.4

BH5 0.6-0.7

BH6 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

12/8/2014

12/8/2014

12/8/2014

13/8/2014

13/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.007

SE130614.008

SE130614.009

SE130614.010

SE130614.011

SE130614.012

Total Organic Carbon

%w/w

0.050

1.6

1.5

1.5

1.2

0.62

0.14

BH7 0.15-0.45

BH7 1.4-1.7

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

BH10 0.23-0.5

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

14/8/2014

14/8/2014

14/8/2014

12/8/2014

PARAMETER

UOM

LOR

SE130614.013

SE130614.014

SE130614.016

SE130614.017

SE130614.018

SE130614.019

Total Organic Carbon

%w/w

0.050

0.46

0.23

0.38

1.3

0.31

0.19

BH10 0.55-0.65 SOIL 12/8/2014 PARAMETER

UOM

LOR

SE130614.020

Total Organic Carbon

%w/w

0.050

0.16

26/08/2014

Page 17 of 25


ANALYTICAL RESULTS

SE130614 R0

Total Recoverable Metals in Soil by ICPOES from EPA 200.8 Digest [AN040/AN320] BH1 1.5-1.8

BH1 3.15-3.25

BH2 0-0.15

BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

7/8/2014

7/8/2014

11/8/2014

11/8/2014

11/8/2014

11/8/2014 SE130614.006

PARAMETER

UOM

LOR

SE130614.001

SE130614.002

SE130614.003

SE130614.004

SE130614.005

Arsenic, As

mg/kg

3.0

7

9

<3

4

30

10

Cadmium, Cd

mg/kg

0.30

0.4

<0.3

<0.3

0.3

0.8

0.3

Chromium, Cr

mg/kg

0.30

16

14

9.1

12

52

18

Copper, Cu

mg/kg

0.50

6.7

4.1

17

15

130

8.5

Lead, Pb

mg/kg

1.0

18

18

28

20

120

22

Nickel, Ni

mg/kg

0.50

1.5

3.1

5.3

4.5

8.3

1.9

Zinc, Zn

mg/kg

0.50

7.7

11

54

38

260

19

BH3 0-0.1

BH3 1.5-1.8

BH4 0-0.15

BH5 0.1-0.4

BH5 0.6-0.7

BH6 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

12/8/2014

12/8/2014

12/8/2014

13/8/2014

13/8/2014

13/8/2014 SE130614.012

PARAMETER

UOM

LOR

SE130614.007

SE130614.008

SE130614.009

SE130614.010

SE130614.011

Arsenic, As

mg/kg

3.0

<3

7

12

520

62

7

Cadmium, Cd

mg/kg

0.30

<0.3

<0.3

0.4

0.6

0.4

0.6

Chromium, Cr

mg/kg

0.30

8.4

12

18

37

28

27

Copper, Cu

mg/kg

0.50

8.0

9.0

16

41

12

14

Lead, Pb

mg/kg

1.0

13

35

38

120

43

14

Nickel, Ni

mg/kg

0.50

5.5

2.6

4.9

10

2.1

15

Zinc, Zn

mg/kg

0.50

26

54

62

150

31

17

BH7 0.15-0.45

BH7 1.4-1.7

BH8 0.2-0.4

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

14/8/2014

14/8/2014

14/8/2014

14/8/2014 SE130614.018

PARAMETER

UOM

LOR

SE130614.013

SE130614.014

SE130614.015

SE130614.016

SE130614.017

Arsenic, As

mg/kg

3.0

<3

4

4

6

12

5

Cadmium, Cd

mg/kg

0.30

<0.3

<0.3

0.5

0.4

0.4

0.3

Chromium, Cr

mg/kg

0.30

11

11

97

23

20

9.3

Copper, Cu

mg/kg

0.50

8.6

9.3

15

18

20

12

Lead, Pb

mg/kg

1.0

9

13

10

23

42

24

Nickel, Ni

mg/kg

0.50

8.6

5.9

50

15

2.3

0.7

Zinc, Zn

mg/kg

0.50

20

17

35

43

67

13

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

-

-

-

12/8/2014

12/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.019

SE130614.020

SE130614.021

Arsenic, As

mg/kg

3.0

6

4

260

Cadmium, Cd

mg/kg

0.30

0.4

<0.3

0.7

Chromium, Cr

mg/kg

0.30

16

7.2

36

Copper, Cu

mg/kg

0.50

22

23

43

Lead, Pb

mg/kg

1.0

15

13

110

Nickel, Ni

mg/kg

0.50

19

19

9.5

Zinc, Zn

mg/kg

0.50

16

15

150

26/08/2014

Page 18 of 25


ANALYTICAL RESULTS

SE130614 R0

Mercury in Soil [AN312] BH1 1.5-1.8

BH1 3.15-3.25

BH2 0-0.15

BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

7/8/2014

7/8/2014

11/8/2014

11/8/2014

11/8/2014

11/8/2014

PARAMETER

UOM

LOR

SE130614.001

SE130614.002

SE130614.003

SE130614.004

SE130614.005

SE130614.006

Mercury

mg/kg

0.010

0.02

0.02

0.02

0.01

0.40

0.02

BH3 0-0.1

BH3 1.5-1.8

BH4 0-0.15

BH5 0.1-0.4

BH5 0.6-0.7

BH6 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

12/8/2014

12/8/2014

12/8/2014

13/8/2014

13/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.007

SE130614.008

SE130614.009

SE130614.010

SE130614.011

SE130614.012

Mercury

mg/kg

0.010

0.01

0.04

0.04

0.06

0.06

0.01

BH7 0.15-0.45

BH7 1.4-1.7

BH8 0.2-0.4

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

14/8/2014

14/8/2014

14/8/2014

14/8/2014

PARAMETER

UOM

LOR

SE130614.013

SE130614.014

SE130614.015

SE130614.016

SE130614.017

SE130614.018

Mercury

mg/kg

0.010

0.01

0.01

0.02

0.02

0.16

0.05

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

-

-

-

12/8/2014

12/8/2014

13/8/2014

PARAMETER

UOM

LOR

SE130614.019

SE130614.020

SE130614.021

Mercury

mg/kg

0.010

0.01

<0.01

0.08

26/08/2014

Page 19 of 25


ANALYTICAL RESULTS

SE130614 R0

Fibre Identification in soil [AN602]

PARAMETER

BH1 1.5-1.8

BH2 0-0.15

BH2 0.5-0.8

BH2 4.5-4.8

BH3 0-0.1

BH3 1.5-1.8

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

7/8/2014

11/8/2014

11/8/2014

11/8/2014

12/8/2014

12/8/2014 SE130614.008

UOM

LOR

SE130614.001

SE130614.003

SE130614.004

SE130614.005

SE130614.007

Asbestos Detected

No unit

-

No

No

No

No

No

No

Estimated Fibres

%w/w

0.010

<0.01

<0.01

<0.01

<0.01

<0.01

<0.01

BH4 0-0.15

BH5 0.1-0.4

BH5 0.6-0.7

BH7 0.15-0.45

BH7 1.4-1.7

BH9 0.2-0.5

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

12/8/2014

13/8/2014

13/8/2014

11/8/2014

11/8/2014

14/8/2014 SE130614.016

PARAMETER

UOM

LOR

SE130614.009

SE130614.010

SE130614.011

SE130614.013

SE130614.014

Asbestos Detected

No unit

-

No

No

No

No

No

No

Estimated Fibres

%w/w

0.010

<0.01

<0.01

<0.01

<0.01

<0.01

<0.01

BH9 2.0-2.3

BH10 0.23-0.5

SOIL

SOIL

PARAMETER

-

-

14/8/2014

12/8/2014 SE130614.019

UOM

LOR

SE130614.017

Asbestos Detected

No unit

-

No

No

Estimated Fibres

%w/w

0.010

<0.01

<0.01

26/08/2014

Page 20 of 25


ANALYTICAL RESULTS

SE130614 R0

Moisture Content [AN002]

PARAMETER

% Moisture

PARAMETER

% Moisture

PARAMETER

% Moisture

PARAMETER

% Moisture

26/08/2014

BH1 1.5-1.8

BH1 3.15-3.25

BH2 0-0.15

BH2 0.5-0.8

BH2 4.5-4.8

BH2 5.1-5.25

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

7/8/2014

7/8/2014

11/8/2014

11/8/2014

11/8/2014

11/8/2014

UOM

LOR

SE130614.001

SE130614.002

SE130614.003

SE130614.004

SE130614.005

SE130614.006

%

0.50

13

20

16

13

27

21

BH3 0-0.1

BH3 1.5-1.8

BH4 0-0.15

BH5 0.1-0.4

BH5 0.6-0.7

BH6 0.6-0.7

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

12/8/2014

12/8/2014

12/8/2014

13/8/2014

13/8/2014

13/8/2014

UOM

LOR

SE130614.007

SE130614.008

SE130614.009

SE130614.010

SE130614.011

SE130614.012

%

0.50

13

17

17

23

19

10

BH7 0.15-0.45

BH7 1.4-1.7

BH8 0.2-0.4

BH9 0.2-0.5

BH9 2.0-2.3

BH9 2.55-2.65

SOIL

SOIL

SOIL

SOIL

SOIL

SOIL

-

-

-

-

-

-

11/8/2014

11/8/2014

14/8/2014

14/8/2014

14/8/2014

14/8/2014

UOM

LOR

SE130614.013

SE130614.014

SE130614.015

SE130614.016

SE130614.017

SE130614.018

%

0.50

9.9

13

19

15

22

18

BH10 0.23-0.5

BH10 0.55-0.65

Duplicate D2

SOIL

SOIL

SOIL

-

-

-

12/8/2014

12/8/2014

13/8/2014

UOM

LOR

SE130614.019

SE130614.020

SE130614.021

%

0.50

17

16

21

Page 21 of 25


ANALYTICAL RESULTS

SE130614 R0

Metals in Water (Dissolved) by ICPOES [AN320/AN321] Rinsate R1

Rinsate R2

Rinsate R3

Rinsate R4

Rinsate R5

WATER

WATER

WATER

WATER

WATER

-

-

-

-

-

7/8/2014

11/8/2014

12/8/2014

13/8/2014

14/8/2014 SE130614.028

PARAMETER

UOM

LOR

SE130614.024

SE130614.025

SE130614.026

SE130614.027

Arsenic, As

mg/L

0.020

<0.02

<0.02

<0.02

<0.02

<0.02

Cadmium, Cd

mg/L

0.0010

<0.001

<0.001

<0.001

<0.001

<0.001

Chromium, Cr

mg/L

0.0050

<0.005

<0.005

<0.005

<0.005

<0.005

Copper, Cu

mg/L

0.0050

<0.005

<0.005

<0.005

<0.005

<0.005

Lead, Pb

mg/L

0.020

<0.02

<0.02

<0.02

<0.02

<0.02

Nickel, Ni

mg/L

0.0050

<0.005

<0.005

<0.005

<0.005

<0.005

Zinc, Zn

mg/L

0.010

<0.01

<0.01

<0.01

<0.01

<0.01

26/08/2014

Page 22 of 25


ANALYTICAL RESULTS

SE130614 R0

Mercury (dissolved) in Water [AN311/AN312] Rinsate R1

Rinsate R2

Rinsate R3

Rinsate R4

Rinsate R5

WATER

WATER

WATER

WATER

WATER

-

-

-

-

-

7/8/2014

11/8/2014

12/8/2014

13/8/2014

14/8/2014

PARAMETER

UOM

LOR

SE130614.024

SE130614.025

SE130614.026

SE130614.027

SE130614.028

Mercury

mg/L

0.00010

0.0002

<0.0001

<0.0001

<0.0001

<0.0001

26/08/2014

Page 23 of 25


METHOD SUMMARY

METHOD

SE130614 R0

METHODOLOGY SUMMARY

AN002

The test is carried out by drying (at either 40°C or 105°C) a known mass of sample in a weighed evaporating basin. After fully dry the sample is re-weighed. Samples such as sludge and sediment having high percentages of moisture will take some time in a drying oven for complete removal of water.

AN020

Unpreserved water sample is filtered through a 0.45µm membrane filter and acidified with nitric acid similar to APHA3030B.

AN040

A portion of sample is digested with Nitric acid to decompose organic matter and Hydrochloric acid to complete the digestion of metals and then filtered for analsysis by ASS or ICP as per USEPA Method 200.8.

AN040/AN320

A portion of sample is digested with nitric acid to decompose organic matter and hydrochloric acid to complete the digestion of metals. The digest is then analysed by ICP OES with metals results reported on the dried sample basis. Based on USEPA method 200.8 and 6010C.

AN077

Hydrogen cyanide is liberated from an acidified alkali soil extract by distillation and purging with air. The hydrogen cyanide gas is then collected by passing it through a sodium hydroxide scrubbing solution. The scrubbing solution will then be analysed for cyanide by the appropriate method.

AN088

Orbital rolling for Organic pollutants are extracted from soil /sediment by transferring an appropriate mass of sample to a clear soil jar and extracting with 1:1 Dichloromethane/Acetone. Orbital Rolling method is intended for the extraction of semi-volatile organic compounds from soil/sediment samples, and is based somewhat on USEPA method 3570 (Micro Organic extraction and sample preparation). Method 3700.

AN101

pH in Soil Sludge Sediment and Water: pH is measured electrometrically using a combination electrode (glass plus reference electrode) and is calibrated against 3 buffers purchased commercially. For soils, an extract with water (or 0.01M CaCl2) is made at a ratio of 1:5 and the pH determined and reported on the extract. Reference APHA 4500-H+.

AN122

Exchangeable Cations, CEC and ESP: Soil sample is extracted in 1M Ammonium Acetate at pH=7 (or 1M Ammonium Chloride at pH=7) with cations (Na, K, Ca & Mg) then determined by ICP OES/ICP MS and reported as Exchangeable Cations. For saline soils, these results can be corrected for water soluble cations and reported as Exchangeable cations in meq/100g or soil can be pretreated (aqueous ethanol/aqueous glycerol) prior to extraction. Cation Exchange Capacity (CEC) is the sum of the exchangeable cations in meq/100g.

AN188

The organic material in the soil sample is oxidised with chromic acid in the presence of excess sulphuric acid, without external heat being applied. The excess dichromate ion is determined by titration with standard ammonium iron (II) sulphate solution and the amount of oxidised material is calculated from the quantity of dichromate reduced. Referenced to NEPM 105 and AS1289.1.1.1.

AN287

A buffered distillate or water sample is treated with chloramine /barbituric acid reagents and the intensity of the colour developed is proportional to the cyanide concentration by Aquakem DA.

AN289

Analysis of Total Phenols in Soil Sediment and Water: Steam distillable phenols react with 4-aminoantipyrine at pH 7.9±0.1 in the presence of potassium ferricyanide to form a coloured antipyrine dye analysed by Discrete Analyser. Reference APHA 5530 B/D.

AN311/AN312

Mercury by Cold Vapour AAS in Waters: Mercury ions are reduced by stannous chloride reagent in acidic solution to elemental mercury. This mercury vapour is purged by nitrogen into a cold cell in an atomic absorption spectrometer or mercury analyser. Quantification is made by comparing absorbances to those of the calibration standards. Reference APHA 3112/3500.

AN312

Mercury by Cold Vapour AAS in Soils: After digestion with nitric acid, hydrogen peroxide and hydrochloric acid, mercury ions are reduced by stannous chloride reagent in acidic solution to elemental mercury. This mercury vapour is purged by nitrogen into a cold cell in an atomic absorption spectrometer or mercury analyser . Quantification is made by comparing absorbances to those of the calibration standards. Reference APHA 3112/3500

AN320/AN321

Metals by ICP-OES: Samples are preserved with 10% nitric acid for a wide range of metals and some non -metals. This solution is measured by Inductively Coupled Plasma. Solutions are aspirated into an argon plasma at 8000-10000K and emit characteristic energy or light as a result of electron transitions through unique energy levels. The emitted light is focused onto a diffraction grating where it is separated into components.

AN400

OC and OP Pesticides by GC-ECD: The determination of organochlorine (OC) and organophosphorus (OP) pesticides and polychlorinated biphenyls (PCBs) in soils, sludges and groundwater. (Based on USEPA methods 3510, 3550, 8140 and 8080.)

AN403

Total Recoverable Hydrocarbons: Determination of Hydrocarbons by gas chromatography after a solvent extraction. Detection is by flame ionisation detector (FID) that produces an electronic signal in proportion to the combustible matter passing through it. Total Recoverable Hydrocarbons (TRH) are routinely reported as four alkane groupings based on the carbon chain length of the compounds: C6-C9, C10-C14, C15-C28 and C29-C36 and in recognition of the NEPM 1999 (2013), >C10-C16 (F2), >C16-C34 (F3) and >C34-C40 (F4). F2 is reported directly and also corrected by subtracting Naphthalene (from VOC method AN433) where available.

AN420

(SVOCs) including OC, OP, PCB, Herbicides, PAH, Phthalates and Speciated Phenols (etc) in soils, sediments and waters are determined by GCMS/ECD technique following appropriate solvent extraction process (Based on USEPA 3500C and 8270D).

26/08/2014

Page 24 of 25


METHOD SUMMARY

SE130614 R0

AN433/AN434

VOCs and C6-C9 Hydrocarbons by GC-MS P&T: VOC`s are volatile organic compounds. The sample is presented to a gas chromatograph via a purge and trap (P&T) concentrator and autosampler and is detected with a Mass Spectrometer (MSD). Solid samples are initially extracted with methanol whilst liquid samples are processed directly. References: USEPA 5030B, 8020A, 8260.

AN433/AN434/AN410

VOCs and C6-C9/C6-C10 Hydrocarbons by GC-MS P&T: VOC`s are volatile organic compounds. The sample is presented to a gas chromatograph via a purge and trap (P&T) concentrator and autosampler and is detected with a Mass Spectrometer (MSD). Solid samples are initially extracted with methanol whilst liquid samples are processed directly. References: USEPA 5030B, 8020A, 8260.

AN602

Qualitative identification of chrysotile, amosite and crocidolite in bulk samples by polarised light microscopy (PLM) in conjunction with dispersion staining (DS). AS4964 provides the basis for this document. Unequivocal identification of the asbestos minerals present is made by obtaining sufficient diagnostic `clues`, which provide a reasonable degree of certainty, dispersion staining is a mandatory `clue` for positive identification. If sufficient `clues` are absent, then positive identification of asbestos is not possible. This procedure requires removal of suspect fibres/bundles from the sample which cannot be returned.

FOOTNOTES

* ** ^

Analysis not covered by the scope of accreditation. Indicative data, theoretical holding time exceeded. Performed by outside laboratory.

NVL IS LNR

Not analysed. Not validated. Insufficient sample for analysis. Sample listed, but not received.

UOM LOR ↑↓

Unit of Measure. Limit of Reporting. Raised/lowered Limit of Reporting.

Samples analysed as received. Solid samples expressed on a dry weight basis. Some totals may not appear to add up because the total is rounded after adding up the raw values. The QC criteria are subject to internal review according to the SGS QAQC plan and may be provided on request or alternatively can be found here: http://www.sgs.com.au/~/media/Local/Australia/Documents/Technical%20Documents/MP-AU-ENV-QU-022%20QA%20QC%20Plan.pdf This document is issued, on the Client's behalf, by the Company under its General Conditions of Service available on request and accessible at http://www.sgs.com/en/Terms-and-Conditions/General-Conditions-of-Services-English.aspx. The Client's attention is drawn to the limitation of liability, indemnification and jurisdiction issues defined therein. Any other holder of this document is advised that information contained hereon reflects the Company's findings at the time of its intervention only and within the limits of Client's instructions, if any. The Company's sole responsibility is to its Client and this document does not exonerate parties to a transaction from exercising all their rights and obligations under the transaction documents. This report must not be reproduced, except in full.

26/08/2014

Page 25 of 25


SE130614 R0

STATEMENT OF QA/QC PERFORMANCE

CLIENT DETAILS

LABORATORY DETAILS

Contact

An Nguyen

Manager

Huong Crawford

Client

Geotechnique

Laboratory

SGS Alexandria Environmental

Address

P.O. Box 880 NSW 2751

Address

Unit 16, 33 Maddox St Alexandria NSW 2015

Telephone

02 4722 2700

Telephone

+61 2 8594 0400

Facsimile Email

02 4722 6161

Facsimile

+61 2 8594 0499

anguyen@geotech.com.au

Email

au.environmental.sydney@sgs.com

Project

13188-2 - Concord

SGS Reference

Order Number

(Not specified)

Report Number

SE130614 R0 0000090000

Samples

28

Date Reported

27 Aug 2014

COMMENTS

All the laboratory data for each environmental matrix was compared to SGS Environmental Services' stated Data Quality Objectives (DQO). Comments arising from the comparison were made and are reported below. The data relating to sampling was taken from the Chain of Custody document and was supplied by the Client. This QA/QC Statement must be read in conjunction with the referenced Analytical Report. The Statement and the Analytical Report must not be reproduced except in full. All Data Quality Objectives were met with the exception of the following: Extraction Date

pH in soil (1:5)

8 items

Analysis Date

pH in soil (1:5)

21 items

Duplicate

Total Recoverable Metals in Soil by ICPOES from EPA 200.8 Digest

1 item

SAMPLE SUMMARY

Sample counts by matrix Date documentation received Samples received without headspace Sample container provider Samples received in correct containers Sample cooling method Complete documentation received

SGS Australia Pty Ltd ABN 44 000 964 278

Environmental Services

21 Soils, 5 Waters 18/08/2014@02:31pm Yes SGS Yes Ice Bricks Yes

Unit 16 33 Maddox St PO Box 6432 Bourke Rd BC

Type of documentation received Samples received in good order Sample temperature upon receipt Turnaround time requested Sufficient sample for analysis Samples clearly labelled

Alexandria NSW 2015 Alexandria NSW 2015

Australia Australia

t +61 2 8594 0400

COC Yes 4.5°C Standard Yes Yes

f +61 2 8594 0499

www.au.sgs.com

Member of the SGS Group

27/8/2014

Page 1 of 29


SE130614 R0

HOLDING TIME SUMMARY

SGS holding time criteria are drawn from current regulations and are highly dependent on sample container preservation as specified in the SGS “Field Sampling Guide for Containers and Holding Time” (ref: GU-(AU)-ENV.001). Soil samples guidelines are derived from NEPM "Schedule B(3) Guideline on Laboratory Analysis of Potentially Contaminated Soils". Water sample guidelines are derived from "AS/NZS 5667.1 : 1998 Water Quality - sampling part 1" and APHA "Standard Methods for the Examination of Water and Wastewater" 21st edition 2005. Extraction and analysis holding time due dates listed are calculated from the date sampled, although holding times may be extended after laboratory extraction for some analytes. The due dates are the suggested dates that samples may be held before extraction or analysis and still be considered valid. Extraction and analysis dates are shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria. If the sampled date is not supplied then compliance with criteria cannot be determined. If the received date is after one or both due dates then holding time will fail by default.

Exchangeable Cations and Cation Exchange Capacity (CEC/ESP/SAR)

Sample Name

Sample No.

QC Ref

BH1 1.5-1.8

SE130614.001

BH1 3.15-3.25 BH2 0-0.15

Method: ME-(AU)-[ENV]AN122

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

LB062800

07 Aug 2014

18 Aug 2014

04 Sep 2014

22 Aug 2014

04 Sep 2014

25 Aug 2014

SE130614.002

LB062800

07 Aug 2014

18 Aug 2014

04 Sep 2014

22 Aug 2014

04 Sep 2014

25 Aug 2014

SE130614.003

LB062800

11 Aug 2014

18 Aug 2014

08 Sep 2014

22 Aug 2014

08 Sep 2014

25 Aug 2014

BH2 0.5-0.8

SE130614.004

LB062800

11 Aug 2014

18 Aug 2014

08 Sep 2014

22 Aug 2014

08 Sep 2014

25 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062800

11 Aug 2014

18 Aug 2014

08 Sep 2014

22 Aug 2014

08 Sep 2014

25 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062800

11 Aug 2014

18 Aug 2014

08 Sep 2014

22 Aug 2014

08 Sep 2014

25 Aug 2014

BH3 0-0.1

SE130614.007

LB062800

12 Aug 2014

18 Aug 2014

09 Sep 2014

22 Aug 2014

09 Sep 2014

25 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062800

12 Aug 2014

18 Aug 2014

09 Sep 2014

22 Aug 2014

09 Sep 2014

25 Aug 2014

BH4 0-0.15

SE130614.009

LB062800

12 Aug 2014

18 Aug 2014

09 Sep 2014

22 Aug 2014

09 Sep 2014

25 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062800

13 Aug 2014

18 Aug 2014

10 Sep 2014

22 Aug 2014

10 Sep 2014

25 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062800

13 Aug 2014

18 Aug 2014

10 Sep 2014

22 Aug 2014

10 Sep 2014

25 Aug 2014

BH6 0.6-0.7

SE130614.012

LB062800

13 Aug 2014

18 Aug 2014

10 Sep 2014

22 Aug 2014

10 Sep 2014

25 Aug 2014

BH7 0.15-0.45

SE130614.013

LB062800

11 Aug 2014

18 Aug 2014

08 Sep 2014

22 Aug 2014

08 Sep 2014

25 Aug 2014

BH7 1.4-1.7

SE130614.014

LB062800

11 Aug 2014

18 Aug 2014

08 Sep 2014

22 Aug 2014

08 Sep 2014

25 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062800

14 Aug 2014

18 Aug 2014

11 Sep 2014

22 Aug 2014

11 Sep 2014

25 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062800

14 Aug 2014

18 Aug 2014

11 Sep 2014

22 Aug 2014

11 Sep 2014

25 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062801

14 Aug 2014

18 Aug 2014

11 Sep 2014

22 Aug 2014

11 Sep 2014

25 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062801

12 Aug 2014

18 Aug 2014

09 Sep 2014

22 Aug 2014

09 Sep 2014

25 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062801

12 Aug 2014

18 Aug 2014

09 Sep 2014

22 Aug 2014

09 Sep 2014

25 Aug 2014

Fibre Identification in soil

Method: ME-(AU)-[ENV]AN602

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH1 1.5-1.8

SE130614.001

LB062740

07 Aug 2014

18 Aug 2014

07 Aug 2015

21 Aug 2014

07 Aug 2015

25 Aug 2014

BH2 0-0.15

SE130614.003

LB062740

11 Aug 2014

18 Aug 2014

11 Aug 2015

21 Aug 2014

11 Aug 2015

25 Aug 2014

BH2 0.5-0.8

SE130614.004

LB062740

11 Aug 2014

18 Aug 2014

11 Aug 2015

21 Aug 2014

11 Aug 2015

25 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062740

11 Aug 2014

18 Aug 2014

11 Aug 2015

21 Aug 2014

11 Aug 2015

25 Aug 2014

BH3 0-0.1

SE130614.007

LB062740

12 Aug 2014

18 Aug 2014

12 Aug 2015

21 Aug 2014

12 Aug 2015

25 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062740

12 Aug 2014

18 Aug 2014

12 Aug 2015

21 Aug 2014

12 Aug 2015

25 Aug 2014

BH4 0-0.15

SE130614.009

LB062740

12 Aug 2014

18 Aug 2014

12 Aug 2015

21 Aug 2014

12 Aug 2015

25 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062740

13 Aug 2014

18 Aug 2014

13 Aug 2015

21 Aug 2014

13 Aug 2015

25 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062740

13 Aug 2014

18 Aug 2014

13 Aug 2015

21 Aug 2014

13 Aug 2015

25 Aug 2014

BH7 0.15-0.45

SE130614.013

LB062740

11 Aug 2014

18 Aug 2014

11 Aug 2015

21 Aug 2014

11 Aug 2015

25 Aug 2014

BH7 1.4-1.7

SE130614.014

LB062740

11 Aug 2014

18 Aug 2014

11 Aug 2015

21 Aug 2014

11 Aug 2015

25 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062740

14 Aug 2014

18 Aug 2014

14 Aug 2015

21 Aug 2014

14 Aug 2015

25 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062740

14 Aug 2014

18 Aug 2014

14 Aug 2015

21 Aug 2014

14 Aug 2015

25 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062740

12 Aug 2014

18 Aug 2014

12 Aug 2015

21 Aug 2014

12 Aug 2015

25 Aug 2014

Mercury (dissolved) in Water

Method: ME-(AU)-[ENV]AN311/AN312

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

Rinsate R1

SE130614.024

LB062755

07 Aug 2014

18 Aug 2014

04 Sep 2014

22 Aug 2014

04 Sep 2014

22 Aug 2014

Rinsate R2

SE130614.025

LB062755

11 Aug 2014

18 Aug 2014

08 Sep 2014

22 Aug 2014

08 Sep 2014

22 Aug 2014

Rinsate R3

SE130614.026

LB062755

12 Aug 2014

18 Aug 2014

09 Sep 2014

22 Aug 2014

09 Sep 2014

22 Aug 2014

Rinsate R4

SE130614.027

LB062755

13 Aug 2014

18 Aug 2014

10 Sep 2014

22 Aug 2014

10 Sep 2014

22 Aug 2014

Rinsate R5

SE130614.028

LB062755

14 Aug 2014

18 Aug 2014

11 Sep 2014

22 Aug 2014

11 Sep 2014

22 Aug 2014

Mercury in Soil

Method: ME-(AU)-[ENV]AN312

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH1 1.5-1.8

SE130614.001

LB062739

07 Aug 2014

18 Aug 2014

04 Sep 2014

21 Aug 2014

04 Sep 2014

25 Aug 2014

BH1 3.15-3.25

SE130614.002

LB062739

07 Aug 2014

18 Aug 2014

04 Sep 2014

21 Aug 2014

04 Sep 2014

25 Aug 2014

BH2 0-0.15

SE130614.003

LB062739

11 Aug 2014

18 Aug 2014

08 Sep 2014

21 Aug 2014

08 Sep 2014

25 Aug 2014

BH2 0.5-0.8

SE130614.004

LB062739

11 Aug 2014

18 Aug 2014

08 Sep 2014

21 Aug 2014

08 Sep 2014

25 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062739

11 Aug 2014

18 Aug 2014

08 Sep 2014

21 Aug 2014

08 Sep 2014

25 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062741

11 Aug 2014

18 Aug 2014

08 Sep 2014

21 Aug 2014

08 Sep 2014

25 Aug 2014

BH3 0-0.1

SE130614.007

LB062741

12 Aug 2014

18 Aug 2014

09 Sep 2014

21 Aug 2014

09 Sep 2014

25 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062741

12 Aug 2014

18 Aug 2014

09 Sep 2014

21 Aug 2014

09 Sep 2014

25 Aug 2014

BH4 0-0.15

SE130614.009

LB062741

12 Aug 2014

18 Aug 2014

09 Sep 2014

21 Aug 2014

09 Sep 2014

25 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062741

13 Aug 2014

18 Aug 2014

10 Sep 2014

21 Aug 2014

10 Sep 2014

25 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062741

13 Aug 2014

18 Aug 2014

10 Sep 2014

21 Aug 2014

10 Sep 2014

25 Aug 2014

BH6 0.6-0.7

SE130614.012

LB062741

13 Aug 2014

18 Aug 2014

10 Sep 2014

21 Aug 2014

10 Sep 2014

25 Aug 2014

BH7 0.15-0.45

SE130614.013

LB062741

11 Aug 2014

18 Aug 2014

08 Sep 2014

21 Aug 2014

08 Sep 2014

25 Aug 2014

BH7 1.4-1.7

SE130614.014

LB062741

11 Aug 2014

18 Aug 2014

08 Sep 2014

21 Aug 2014

08 Sep 2014

25 Aug 2014

27/8/2014

Page 2 of 29


SE130614 R0

HOLDING TIME SUMMARY

SGS holding time criteria are drawn from current regulations and are highly dependent on sample container preservation as specified in the SGS “Field Sampling Guide for Containers and Holding Time” (ref: GU-(AU)-ENV.001). Soil samples guidelines are derived from NEPM "Schedule B(3) Guideline on Laboratory Analysis of Potentially Contaminated Soils". Water sample guidelines are derived from "AS/NZS 5667.1 : 1998 Water Quality - sampling part 1" and APHA "Standard Methods for the Examination of Water and Wastewater" 21st edition 2005. Extraction and analysis holding time due dates listed are calculated from the date sampled, although holding times may be extended after laboratory extraction for some analytes. The due dates are the suggested dates that samples may be held before extraction or analysis and still be considered valid. Extraction and analysis dates are shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria. If the sampled date is not supplied then compliance with criteria cannot be determined. If the received date is after one or both due dates then holding time will fail by default.

Mercury in Soil (continued)

Method: ME-(AU)-[ENV]AN312

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

BH8 0.2-0.4

SE130614.015

Analysed

LB062741

14 Aug 2014

18 Aug 2014

11 Sep 2014

21 Aug 2014

11 Sep 2014

25 Aug 2014

BH9 0.2-0.5 BH9 2.0-2.3

SE130614.016

LB062741

14 Aug 2014

18 Aug 2014

11 Sep 2014

21 Aug 2014

11 Sep 2014

25 Aug 2014

SE130614.017

LB062741

14 Aug 2014

18 Aug 2014

11 Sep 2014

21 Aug 2014

11 Sep 2014

25 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062741

14 Aug 2014

18 Aug 2014

11 Sep 2014

21 Aug 2014

11 Sep 2014

25 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062741

12 Aug 2014

18 Aug 2014

09 Sep 2014

21 Aug 2014

09 Sep 2014

25 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062741

12 Aug 2014

18 Aug 2014

09 Sep 2014

21 Aug 2014

09 Sep 2014

25 Aug 2014

Duplicate D2

SE130614.021

LB062741

13 Aug 2014

18 Aug 2014

10 Sep 2014

21 Aug 2014

10 Sep 2014

25 Aug 2014

Metals in Water (Dissolved) by ICPOES

Method: ME-(AU)-[ENV]AN320/AN321

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

Rinsate R1

SE130614.024

LB062600

07 Aug 2014

18 Aug 2014

03 Feb 2015

20 Aug 2014

03 Feb 2015

20 Aug 2014

Rinsate R2

SE130614.025

LB062600

11 Aug 2014

18 Aug 2014

07 Feb 2015

20 Aug 2014

07 Feb 2015

20 Aug 2014

Rinsate R3

SE130614.026

LB062600

12 Aug 2014

18 Aug 2014

08 Feb 2015

20 Aug 2014

08 Feb 2015

20 Aug 2014

Rinsate R4

SE130614.027

LB062600

13 Aug 2014

18 Aug 2014

09 Feb 2015

20 Aug 2014

09 Feb 2015

20 Aug 2014

Rinsate R5

SE130614.028

LB062600

14 Aug 2014

18 Aug 2014

10 Feb 2015

20 Aug 2014

10 Feb 2015

20 Aug 2014

Moisture Content

Method: ME-(AU)-[ENV]AN002

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH1 1.5-1.8

SE130614.001

LB062788

07 Aug 2014

18 Aug 2014

21 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH1 3.15-3.25

SE130614.002

LB062788

07 Aug 2014

18 Aug 2014

21 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH2 0-0.15

SE130614.003

LB062788

11 Aug 2014

18 Aug 2014

25 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH2 0.5-0.8

SE130614.004

LB062788

11 Aug 2014

18 Aug 2014

25 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062788

11 Aug 2014

18 Aug 2014

25 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062788

11 Aug 2014

18 Aug 2014

25 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH3 0-0.1

SE130614.007

LB062788

12 Aug 2014

18 Aug 2014

26 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062788

12 Aug 2014

18 Aug 2014

26 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH4 0-0.15

SE130614.009

LB062788

12 Aug 2014

18 Aug 2014

26 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062788

13 Aug 2014

18 Aug 2014

27 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062788

13 Aug 2014

18 Aug 2014

27 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH6 0.6-0.7

SE130614.012

LB062788

13 Aug 2014

18 Aug 2014

27 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH7 0.15-0.45

SE130614.013

LB062788

11 Aug 2014

18 Aug 2014

25 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH7 1.4-1.7

SE130614.014

LB062788

11 Aug 2014

18 Aug 2014

25 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH8 0.2-0.4

SE130614.015

LB062788

14 Aug 2014

18 Aug 2014

28 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062788

14 Aug 2014

18 Aug 2014

28 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062788

14 Aug 2014

18 Aug 2014

28 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062788

14 Aug 2014

18 Aug 2014

28 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062788

12 Aug 2014

18 Aug 2014

26 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062788

12 Aug 2014

18 Aug 2014

26 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

Duplicate D2

SE130614.021

LB062788

13 Aug 2014

18 Aug 2014

27 Aug 2014

21 Aug 2014

26 Aug 2014

23 Aug 2014

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH1 1.5-1.8

SE130614.001

LB062562

07 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH1 3.15-3.25

SE130614.002

LB062562

07 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 0-0.15

SE130614.003

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 0.5-0.8

SE130614.004

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH3 0-0.1

SE130614.007

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH4 0-0.15

SE130614.009

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH6 0.6-0.7

SE130614.012

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH7 0.15-0.45

SE130614.013

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH7 1.4-1.7

SE130614.014

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH8 0.2-0.4

SE130614.015

LB062562

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062562

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062563

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062563

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062563

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

OC Pesticides in Soil

27/8/2014

Method: ME-(AU)-[ENV]AN400/AN420

Page 3 of 29


SE130614 R0

HOLDING TIME SUMMARY

SGS holding time criteria are drawn from current regulations and are highly dependent on sample container preservation as specified in the SGS “Field Sampling Guide for Containers and Holding Time” (ref: GU-(AU)-ENV.001). Soil samples guidelines are derived from NEPM "Schedule B(3) Guideline on Laboratory Analysis of Potentially Contaminated Soils". Water sample guidelines are derived from "AS/NZS 5667.1 : 1998 Water Quality - sampling part 1" and APHA "Standard Methods for the Examination of Water and Wastewater" 21st edition 2005. Extraction and analysis holding time due dates listed are calculated from the date sampled, although holding times may be extended after laboratory extraction for some analytes. The due dates are the suggested dates that samples may be held before extraction or analysis and still be considered valid. Extraction and analysis dates are shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria. If the sampled date is not supplied then compliance with criteria cannot be determined. If the received date is after one or both due dates then holding time will fail by default.

OC Pesticides in Soil (continued)

Method: ME-(AU)-[ENV]AN400/AN420

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

BH10 0.55-0.65

SE130614.020

Analysed

LB062563

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

Duplicate D2

SE130614.021

LB062563

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

PAH (Polynuclear Aromatic Hydrocarbons) in Soil

Method: ME-(AU)-[ENV]AN420

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH1 1.5-1.8

SE130614.001

LB062562

07 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH1 3.15-3.25

SE130614.002

LB062562

07 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 0-0.15

SE130614.003

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 0.5-0.8

SE130614.004

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH3 0-0.1

SE130614.007

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH4 0-0.15

SE130614.009

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH6 0.6-0.7

SE130614.012

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH7 0.15-0.45

SE130614.013

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH7 1.4-1.7

SE130614.014

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH8 0.2-0.4

SE130614.015

LB062562

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062562

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062563

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062563

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062563

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062563

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

Duplicate D2

SE130614.021

LB062563

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

PCBs in Soil

Method: ME-(AU)-[ENV]AN400/AN420

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH1 1.5-1.8

SE130614.001

LB062562

07 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH1 3.15-3.25

SE130614.002

LB062562

07 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 0-0.15

SE130614.003

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 0.5-0.8

SE130614.004

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH3 0-0.1

SE130614.007

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH4 0-0.15

SE130614.009

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH6 0.6-0.7

SE130614.012

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH7 0.15-0.45

SE130614.013

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH7 1.4-1.7

SE130614.014

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH8 0.2-0.4

SE130614.015

LB062562

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062562

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062563

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062563

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062563

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062563

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

Duplicate D2

SE130614.021

LB062563

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

pH in soil (1:5)

Method: ME-(AU)-[ENV]AN101

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH1 1.5-1.8

SE130614.001

LB062682

07 Aug 2014

18 Aug 2014

14 Aug 2014

19 Aug 2014†

20 Aug 2014

22 Aug 2014†

BH1 3.15-3.25

SE130614.002

LB062682

07 Aug 2014

18 Aug 2014

14 Aug 2014

19 Aug 2014†

20 Aug 2014

22 Aug 2014†

BH2 0-0.15

SE130614.003

LB062682

11 Aug 2014

18 Aug 2014

18 Aug 2014

19 Aug 2014†

20 Aug 2014

22 Aug 2014†

BH2 0.5-0.8

SE130614.004

LB062682

11 Aug 2014

18 Aug 2014

18 Aug 2014

19 Aug 2014†

20 Aug 2014

22 Aug 2014†

BH2 4.5-4.8

SE130614.005

LB062682

11 Aug 2014

18 Aug 2014

18 Aug 2014

19 Aug 2014†

20 Aug 2014

22 Aug 2014†

BH2 5.1-5.25

SE130614.006

LB062682

11 Aug 2014

18 Aug 2014

18 Aug 2014

19 Aug 2014†

20 Aug 2014

22 Aug 2014†

BH3 0-0.1

SE130614.007

LB062682

12 Aug 2014

18 Aug 2014

19 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

BH3 1.5-1.8

SE130614.008

LB062682

12 Aug 2014

18 Aug 2014

19 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

27/8/2014

Page 4 of 29


SE130614 R0

HOLDING TIME SUMMARY

SGS holding time criteria are drawn from current regulations and are highly dependent on sample container preservation as specified in the SGS “Field Sampling Guide for Containers and Holding Time” (ref: GU-(AU)-ENV.001). Soil samples guidelines are derived from NEPM "Schedule B(3) Guideline on Laboratory Analysis of Potentially Contaminated Soils". Water sample guidelines are derived from "AS/NZS 5667.1 : 1998 Water Quality - sampling part 1" and APHA "Standard Methods for the Examination of Water and Wastewater" 21st edition 2005. Extraction and analysis holding time due dates listed are calculated from the date sampled, although holding times may be extended after laboratory extraction for some analytes. The due dates are the suggested dates that samples may be held before extraction or analysis and still be considered valid. Extraction and analysis dates are shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria. If the sampled date is not supplied then compliance with criteria cannot be determined. If the received date is after one or both due dates then holding time will fail by default.

pH in soil (1:5) (continued)

Method: ME-(AU)-[ENV]AN101

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

BH4 0-0.15

SE130614.009

Analysed

LB062682

12 Aug 2014

18 Aug 2014

19 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

BH5 0.1-0.4 BH5 0.6-0.7

SE130614.010

LB062682

13 Aug 2014

18 Aug 2014

20 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

SE130614.011

LB062682

13 Aug 2014

18 Aug 2014

20 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

BH6 0.6-0.7

SE130614.012

LB062682

13 Aug 2014

18 Aug 2014

20 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

BH7 0.15-0.45

SE130614.013

LB062682

11 Aug 2014

18 Aug 2014

18 Aug 2014

19 Aug 2014†

20 Aug 2014

22 Aug 2014†

BH7 1.4-1.7

SE130614.014

LB062682

11 Aug 2014

18 Aug 2014

18 Aug 2014

19 Aug 2014†

20 Aug 2014

22 Aug 2014†

BH8 0.2-0.4

SE130614.015

LB062682

14 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

BH9 0.2-0.5

SE130614.016

LB062682

14 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

BH9 2.0-2.3

SE130614.017

LB062682

14 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

BH9 2.55-2.65

SE130614.018

LB062682

14 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

BH10 0.23-0.5

SE130614.019

LB062682

12 Aug 2014

18 Aug 2014

19 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

BH10 0.55-0.65

SE130614.020

LB062682

12 Aug 2014

18 Aug 2014

19 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

Duplicate D2

SE130614.021

LB062682

13 Aug 2014

18 Aug 2014

20 Aug 2014

19 Aug 2014

20 Aug 2014

22 Aug 2014†

TOC in Soil

Method: ME-(AU)-[ENV]AN188

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH1 1.5-1.8

SE130614.001

LB062858

07 Aug 2014

18 Aug 2014

04 Sep 2014

25 Aug 2014

04 Sep 2014

25 Aug 2014

BH1 3.15-3.25

SE130614.002

LB062858

07 Aug 2014

18 Aug 2014

04 Sep 2014

25 Aug 2014

04 Sep 2014

25 Aug 2014

BH2 0-0.15

SE130614.003

LB062858

11 Aug 2014

18 Aug 2014

08 Sep 2014

25 Aug 2014

08 Sep 2014

25 Aug 2014

BH2 0.5-0.8

SE130614.004

LB062858

11 Aug 2014

18 Aug 2014

08 Sep 2014

25 Aug 2014

08 Sep 2014

25 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062858

11 Aug 2014

18 Aug 2014

08 Sep 2014

25 Aug 2014

08 Sep 2014

25 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062858

11 Aug 2014

18 Aug 2014

08 Sep 2014

25 Aug 2014

08 Sep 2014

25 Aug 2014

BH3 0-0.1

SE130614.007

LB062858

12 Aug 2014

18 Aug 2014

09 Sep 2014

25 Aug 2014

09 Sep 2014

25 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062858

12 Aug 2014

18 Aug 2014

09 Sep 2014

25 Aug 2014

09 Sep 2014

25 Aug 2014

BH4 0-0.15

SE130614.009

LB062858

12 Aug 2014

18 Aug 2014

09 Sep 2014

25 Aug 2014

09 Sep 2014

25 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062858

13 Aug 2014

18 Aug 2014

10 Sep 2014

25 Aug 2014

10 Sep 2014

25 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062858

13 Aug 2014

18 Aug 2014

10 Sep 2014

25 Aug 2014

10 Sep 2014

25 Aug 2014

BH6 0.6-0.7

SE130614.012

LB062858

13 Aug 2014

18 Aug 2014

10 Sep 2014

25 Aug 2014

10 Sep 2014

25 Aug 2014

BH7 0.15-0.45

SE130614.013

LB062858

11 Aug 2014

18 Aug 2014

08 Sep 2014

25 Aug 2014

08 Sep 2014

25 Aug 2014

BH7 1.4-1.7

SE130614.014

LB062858

11 Aug 2014

18 Aug 2014

08 Sep 2014

25 Aug 2014

08 Sep 2014

25 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062858

14 Aug 2014

18 Aug 2014

11 Sep 2014

25 Aug 2014

11 Sep 2014

25 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062858

14 Aug 2014

18 Aug 2014

11 Sep 2014

25 Aug 2014

11 Sep 2014

25 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062858

14 Aug 2014

18 Aug 2014

11 Sep 2014

25 Aug 2014

11 Sep 2014

25 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062858

12 Aug 2014

18 Aug 2014

09 Sep 2014

25 Aug 2014

09 Sep 2014

25 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062858

12 Aug 2014

18 Aug 2014

09 Sep 2014

25 Aug 2014

09 Sep 2014

25 Aug 2014

Total Cyanide in soil by Discrete Analyser (Aquakem)

Method: ME-(AU)-[ENV]AN077/AN287

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH2 0.5-0.8

SE130614.004

LB062764

11 Aug 2014

18 Aug 2014

25 Aug 2014

22 Aug 2014

25 Aug 2014

25 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062764

11 Aug 2014

18 Aug 2014

25 Aug 2014

22 Aug 2014

25 Aug 2014

25 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062764

11 Aug 2014

18 Aug 2014

25 Aug 2014

22 Aug 2014

25 Aug 2014

25 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062764

12 Aug 2014

18 Aug 2014

26 Aug 2014

22 Aug 2014

26 Aug 2014

25 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062764

13 Aug 2014

18 Aug 2014

27 Aug 2014

22 Aug 2014

27 Aug 2014

25 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062764

13 Aug 2014

18 Aug 2014

27 Aug 2014

22 Aug 2014

27 Aug 2014

25 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062764

14 Aug 2014

18 Aug 2014

28 Aug 2014

22 Aug 2014

28 Aug 2014

25 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062764

14 Aug 2014

18 Aug 2014

28 Aug 2014

22 Aug 2014

28 Aug 2014

25 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062764

14 Aug 2014

18 Aug 2014

28 Aug 2014

22 Aug 2014

28 Aug 2014

25 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062764

12 Aug 2014

18 Aug 2014

26 Aug 2014

22 Aug 2014

26 Aug 2014

25 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062764

12 Aug 2014

18 Aug 2014

26 Aug 2014

22 Aug 2014

26 Aug 2014

25 Aug 2014

Duplicate D2

SE130614.021

LB062764

13 Aug 2014

18 Aug 2014

27 Aug 2014

22 Aug 2014

27 Aug 2014

25 Aug 2014

Total Phenolics in Soil

Method: ME-(AU)-[ENV]AN289

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH2 0.5-0.8

SE130614.004

LB062763

11 Aug 2014

18 Aug 2014

25 Aug 2014

22 Aug 2014

25 Aug 2014

22 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062763

11 Aug 2014

18 Aug 2014

25 Aug 2014

22 Aug 2014

25 Aug 2014

22 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062763

11 Aug 2014

18 Aug 2014

25 Aug 2014

22 Aug 2014

25 Aug 2014

22 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062763

12 Aug 2014

18 Aug 2014

26 Aug 2014

22 Aug 2014

26 Aug 2014

22 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062763

13 Aug 2014

18 Aug 2014

27 Aug 2014

22 Aug 2014

27 Aug 2014

22 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062763

13 Aug 2014

18 Aug 2014

27 Aug 2014

22 Aug 2014

27 Aug 2014

22 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062763

14 Aug 2014

18 Aug 2014

28 Aug 2014

22 Aug 2014

28 Aug 2014

22 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062763

14 Aug 2014

18 Aug 2014

28 Aug 2014

22 Aug 2014

28 Aug 2014

22 Aug 2014

27/8/2014

Page 5 of 29


SE130614 R0

HOLDING TIME SUMMARY

SGS holding time criteria are drawn from current regulations and are highly dependent on sample container preservation as specified in the SGS “Field Sampling Guide for Containers and Holding Time” (ref: GU-(AU)-ENV.001). Soil samples guidelines are derived from NEPM "Schedule B(3) Guideline on Laboratory Analysis of Potentially Contaminated Soils". Water sample guidelines are derived from "AS/NZS 5667.1 : 1998 Water Quality - sampling part 1" and APHA "Standard Methods for the Examination of Water and Wastewater" 21st edition 2005. Extraction and analysis holding time due dates listed are calculated from the date sampled, although holding times may be extended after laboratory extraction for some analytes. The due dates are the suggested dates that samples may be held before extraction or analysis and still be considered valid. Extraction and analysis dates are shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria. If the sampled date is not supplied then compliance with criteria cannot be determined. If the received date is after one or both due dates then holding time will fail by default.

Total Phenolics in Soil (continued)

Method: ME-(AU)-[ENV]AN289

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

BH9 2.55-2.65

SE130614.018

Analysed

LB062763

14 Aug 2014

18 Aug 2014

28 Aug 2014

22 Aug 2014

28 Aug 2014

22 Aug 2014

BH10 0.23-0.5 BH10 0.55-0.65

SE130614.019

LB062763

12 Aug 2014

18 Aug 2014

26 Aug 2014

22 Aug 2014

26 Aug 2014

22 Aug 2014

SE130614.020

LB062835

12 Aug 2014

18 Aug 2014

26 Aug 2014

23 Aug 2014

26 Aug 2014

Duplicate D2

26 Aug 2014

SE130614.021

LB062835

13 Aug 2014

18 Aug 2014

27 Aug 2014

23 Aug 2014

27 Aug 2014

23 Aug 2014

Total Recoverable Metals in Soil by ICPOES from EPA 200.8 Digest

Method: ME-(AU)-[ENV]AN040/AN320

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH1 1.5-1.8

SE130614.001

LB062732

07 Aug 2014

18 Aug 2014

03 Feb 2015

21 Aug 2014

03 Feb 2015

25 Aug 2014

BH1 3.15-3.25

SE130614.002

LB062732

07 Aug 2014

18 Aug 2014

03 Feb 2015

21 Aug 2014

03 Feb 2015

25 Aug 2014

BH2 0-0.15

SE130614.003

LB062732

11 Aug 2014

18 Aug 2014

07 Feb 2015

21 Aug 2014

07 Feb 2015

25 Aug 2014

BH2 0.5-0.8

SE130614.004

LB062732

11 Aug 2014

18 Aug 2014

07 Feb 2015

21 Aug 2014

07 Feb 2015

25 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062732

11 Aug 2014

18 Aug 2014

07 Feb 2015

21 Aug 2014

07 Feb 2015

25 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062733

11 Aug 2014

18 Aug 2014

07 Feb 2015

21 Aug 2014

07 Feb 2015

25 Aug 2014

BH3 0-0.1

SE130614.007

LB062733

12 Aug 2014

18 Aug 2014

08 Feb 2015

21 Aug 2014

08 Feb 2015

25 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062733

12 Aug 2014

18 Aug 2014

08 Feb 2015

21 Aug 2014

08 Feb 2015

25 Aug 2014

BH4 0-0.15

SE130614.009

LB062733

12 Aug 2014

18 Aug 2014

08 Feb 2015

21 Aug 2014

08 Feb 2015

25 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062733

13 Aug 2014

18 Aug 2014

09 Feb 2015

21 Aug 2014

09 Feb 2015

25 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062733

13 Aug 2014

18 Aug 2014

09 Feb 2015

21 Aug 2014

09 Feb 2015

25 Aug 2014

BH6 0.6-0.7

SE130614.012

LB062733

13 Aug 2014

18 Aug 2014

09 Feb 2015

21 Aug 2014

09 Feb 2015

25 Aug 2014

BH7 0.15-0.45

SE130614.013

LB062733

11 Aug 2014

18 Aug 2014

07 Feb 2015

21 Aug 2014

07 Feb 2015

25 Aug 2014

BH7 1.4-1.7

SE130614.014

LB062733

11 Aug 2014

18 Aug 2014

07 Feb 2015

21 Aug 2014

07 Feb 2015

25 Aug 2014

BH8 0.2-0.4

SE130614.015

LB062733

14 Aug 2014

18 Aug 2014

10 Feb 2015

21 Aug 2014

10 Feb 2015

25 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062733

14 Aug 2014

18 Aug 2014

10 Feb 2015

21 Aug 2014

10 Feb 2015

25 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062733

14 Aug 2014

18 Aug 2014

10 Feb 2015

21 Aug 2014

10 Feb 2015

25 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062733

14 Aug 2014

18 Aug 2014

10 Feb 2015

21 Aug 2014

10 Feb 2015

25 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062733

12 Aug 2014

18 Aug 2014

08 Feb 2015

21 Aug 2014

08 Feb 2015

25 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062733

12 Aug 2014

18 Aug 2014

08 Feb 2015

21 Aug 2014

08 Feb 2015

25 Aug 2014

Duplicate D2

SE130614.021

LB062733

13 Aug 2014

18 Aug 2014

09 Feb 2015

21 Aug 2014

09 Feb 2015

25 Aug 2014

TRH (Total Recoverable Hydrocarbons) in Soil

Method: ME-(AU)-[ENV]AN403

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH1 1.5-1.8

SE130614.001

LB062562

07 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH1 3.15-3.25

SE130614.002

LB062562

07 Aug 2014

18 Aug 2014

21 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 0-0.15

SE130614.003

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 0.5-0.8

SE130614.004

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH3 0-0.1

SE130614.007

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH4 0-0.15

SE130614.009

LB062562

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH6 0.6-0.7

SE130614.012

LB062562

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH7 0.15-0.45

SE130614.013

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH7 1.4-1.7

SE130614.014

LB062562

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH8 0.2-0.4

SE130614.015

LB062562

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062562

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062563

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062563

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062563

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062563

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

Duplicate D2

SE130614.021

LB062563

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

VOC’s in Soil

Method: ME-(AU)-[ENV]AN433/AN434

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH2 0.5-0.8

SE130614.004

LB062558

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062558

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062558

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062558

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062558

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062558

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

27/8/2014

Page 6 of 29


SE130614 R0

HOLDING TIME SUMMARY

SGS holding time criteria are drawn from current regulations and are highly dependent on sample container preservation as specified in the SGS “Field Sampling Guide for Containers and Holding Time” (ref: GU-(AU)-ENV.001). Soil samples guidelines are derived from NEPM "Schedule B(3) Guideline on Laboratory Analysis of Potentially Contaminated Soils". Water sample guidelines are derived from "AS/NZS 5667.1 : 1998 Water Quality - sampling part 1" and APHA "Standard Methods for the Examination of Water and Wastewater" 21st edition 2005. Extraction and analysis holding time due dates listed are calculated from the date sampled, although holding times may be extended after laboratory extraction for some analytes. The due dates are the suggested dates that samples may be held before extraction or analysis and still be considered valid. Extraction and analysis dates are shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria. If the sampled date is not supplied then compliance with criteria cannot be determined. If the received date is after one or both due dates then holding time will fail by default.

VOC’s in Soil (continued)

Method: ME-(AU)-[ENV]AN433/AN434

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

BH9 0.2-0.5

SE130614.016

Analysed

LB062558

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH9 2.0-2.3 BH9 2.55-2.65

SE130614.017

LB062558

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

SE130614.018

LB062558

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062558

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062558

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

Duplicate D2

SE130614.021

LB062558

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

Trip Spike TS1

SE130614.022

LB062558

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

Trip Spike TS2

SE130614.023

LB062558

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

Volatile Petroleum Hydrocarbons in Soil

Method: ME-(AU)-[ENV]AN433/AN434/AN410

Sample Name

Sample No.

QC Ref

Sampled

Received

Extraction Due

Extracted

Analysis Due

Analysed

BH2 0.5-0.8

SE130614.004

LB062558

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH2 4.5-4.8

SE130614.005

LB062558

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH2 5.1-5.25

SE130614.006

LB062558

11 Aug 2014

18 Aug 2014

25 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH3 1.5-1.8

SE130614.008

LB062558

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH5 0.1-0.4

SE130614.010

LB062558

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH5 0.6-0.7

SE130614.011

LB062558

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH9 0.2-0.5

SE130614.016

LB062558

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH9 2.0-2.3

SE130614.017

LB062558

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH9 2.55-2.65

SE130614.018

LB062558

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH10 0.23-0.5

SE130614.019

LB062558

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

BH10 0.55-0.65

SE130614.020

LB062558

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

Duplicate D2

SE130614.021

LB062558

13 Aug 2014

18 Aug 2014

27 Aug 2014

19 Aug 2014

28 Sep 2014

22 Aug 2014

Trip Spike TS1

SE130614.022

LB062558

12 Aug 2014

18 Aug 2014

26 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

Trip Spike TS2

SE130614.023

LB062558

14 Aug 2014

18 Aug 2014

28 Aug 2014

19 Aug 2014

28 Sep 2014

25 Aug 2014

27/8/2014

Page 7 of 29


SE130614 R0

SURROGATES

Surrogate results are evaluated against upper and lower limit criteria established in the SGS QA /QC plan (Ref: MP-(AU)-[ENV]QU-022). At least two of three routine level soil sample surrogate spike recoveries for BTEX /VOC are to be within 70-130% where control charts have not been developed and within the established control limits for charted surrogates. Matrix effects may void this as an acceptance criterion. Water sample surrogate spike recoveries are to be within 40-130%. The presence of emulsions, surfactants and particulates may void this as an acceptance criterion. Result is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

OC Pesticides in Soil

Parameter Tetrachloro-m-xylene (TCMX) (Surrogate)

Method: ME-(AU)-[ENV]AN400/AN420

Sample Name

Sample Number

Units

Criteria

Recovery %

BH1 1.5-1.8

SE130614.001

%

60 - 130%

107

BH1 3.15-3.25

SE130614.002

%

60 - 130%

106

BH2 0-0.15

SE130614.003

%

60 - 130%

105

BH2 0.5-0.8

SE130614.004

%

60 - 130%

109

BH2 4.5-4.8

SE130614.005

%

60 - 130%

111

BH2 5.1-5.25

SE130614.006

%

60 - 130%

111

BH3 0-0.1

SE130614.007

%

60 - 130%

105

BH3 1.5-1.8

SE130614.008

%

60 - 130%

107

BH4 0-0.15

SE130614.009

%

60 - 130%

109

BH5 0.1-0.4

SE130614.010

%

60 - 130%

111

BH5 0.6-0.7

SE130614.011

%

60 - 130%

107

BH6 0.6-0.7

SE130614.012

%

60 - 130%

105

BH7 0.15-0.45

SE130614.013

%

60 - 130%

105

BH7 1.4-1.7

SE130614.014

%

60 - 130%

107

BH8 0.2-0.4

SE130614.015

%

60 - 130%

109

BH9 0.2-0.5

SE130614.016

%

60 - 130%

109

BH9 2.0-2.3

SE130614.017

%

60 - 130%

111

BH9 2.55-2.65

SE130614.018

%

60 - 130%

110

BH10 0.23-0.5

SE130614.019

%

60 - 130%

107

BH10 0.55-0.65

SE130614.020

%

60 - 130%

103

Duplicate D2

SE130614.021

%

60 - 130%

99

PAH (Polynuclear Aromatic Hydrocarbons) in Soil

Parameter 2-fluorobiphenyl (Surrogate)

d14-p-terphenyl (Surrogate)

27/8/2014

Method: ME-(AU)-[ENV]AN420

Sample Name

Units

Criteria

Recovery %

BH1 1.5-1.8

Sample Number SE130614.001

%

60 - 130%

84

BH1 3.15-3.25

SE130614.002

%

60 - 130%

84

BH2 0-0.15

SE130614.003

%

60 - 130%

90

BH2 0.5-0.8

SE130614.004

%

60 - 130%

88

BH2 4.5-4.8

SE130614.005

%

60 - 130%

88

BH2 5.1-5.25

SE130614.006

%

60 - 130%

86

BH3 0-0.1

SE130614.007

%

60 - 130%

88

BH3 1.5-1.8

SE130614.008

%

60 - 130%

84

BH4 0-0.15

SE130614.009

%

60 - 130%

88

BH5 0.1-0.4

SE130614.010

%

60 - 130%

86

BH5 0.6-0.7

SE130614.011

%

60 - 130%

80

BH6 0.6-0.7

SE130614.012

%

60 - 130%

84

BH7 0.15-0.45

SE130614.013

%

60 - 130%

86

BH7 1.4-1.7

SE130614.014

%

60 - 130%

82

BH8 0.2-0.4

SE130614.015

%

60 - 130%

84

BH9 0.2-0.5

SE130614.016

%

60 - 130%

86

BH9 2.0-2.3

SE130614.017

%

60 - 130%

88

BH9 2.55-2.65

SE130614.018

%

60 - 130%

86

BH10 0.23-0.5

SE130614.019

%

60 - 130%

82

BH10 0.55-0.65

SE130614.020

%

60 - 130%

80

Duplicate D2

SE130614.021

%

60 - 130%

86

BH1 1.5-1.8

SE130614.001

%

60 - 130%

94

BH1 3.15-3.25

SE130614.002

%

60 - 130%

94

BH2 0-0.15

SE130614.003

%

60 - 130%

100

BH2 0.5-0.8

SE130614.004

%

60 - 130%

96

BH2 4.5-4.8

SE130614.005

%

60 - 130%

94

BH2 5.1-5.25

SE130614.006

%

60 - 130%

98

BH3 0-0.1

SE130614.007

%

60 - 130%

98

BH3 1.5-1.8

SE130614.008

%

60 - 130%

94

BH4 0-0.15

SE130614.009

%

60 - 130%

96

BH5 0.1-0.4

SE130614.010

%

60 - 130%

96

BH5 0.6-0.7

SE130614.011

%

60 - 130%

90

BH6 0.6-0.7

SE130614.012

%

60 - 130%

96

BH7 0.15-0.45

SE130614.013

%

60 - 130%

98

BH7 1.4-1.7

SE130614.014

%

60 - 130%

92

BH8 0.2-0.4

SE130614.015

%

60 - 130%

92

BH9 0.2-0.5

SE130614.016

%

60 - 130%

100

Page 8 of 29


SE130614 R0

SURROGATES

Surrogate results are evaluated against upper and lower limit criteria established in the SGS QA /QC plan (Ref: MP-(AU)-[ENV]QU-022). At least two of three routine level soil sample surrogate spike recoveries for BTEX /VOC are to be within 70-130% where control charts have not been developed and within the established control limits for charted surrogates. Matrix effects may void this as an acceptance criterion. Water sample surrogate spike recoveries are to be within 40-130%. The presence of emulsions, surfactants and particulates may void this as an acceptance criterion. Result is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

PAH (Polynuclear Aromatic Hydrocarbons) in Soil (continued)

Parameter d14-p-terphenyl (Surrogate)

d5-nitrobenzene (Surrogate)

Method: ME-(AU)-[ENV]AN420

Sample Name

Sample Number

Units

Criteria

Recovery %

BH9 2.0-2.3

SE130614.017

%

60 - 130%

98

BH9 2.55-2.65

SE130614.018

%

60 - 130%

98

BH10 0.23-0.5

SE130614.019

%

60 - 130%

96

BH10 0.55-0.65

SE130614.020

%

60 - 130%

96

Duplicate D2

SE130614.021

%

60 - 130%

94

BH1 1.5-1.8

SE130614.001

%

60 - 130%

86

BH1 3.15-3.25

SE130614.002

%

60 - 130%

86

BH2 0-0.15

SE130614.003

%

60 - 130%

92

BH2 0.5-0.8

SE130614.004

%

60 - 130%

90

BH2 4.5-4.8

SE130614.005

%

60 - 130%

90

BH2 5.1-5.25

SE130614.006

%

60 - 130%

92

BH3 0-0.1

SE130614.007

%

60 - 130%

92

BH3 1.5-1.8

SE130614.008

%

60 - 130%

86

BH4 0-0.15

SE130614.009

%

60 - 130%

88

BH5 0.1-0.4

SE130614.010

%

60 - 130%

92

BH5 0.6-0.7

SE130614.011

%

60 - 130%

86

BH6 0.6-0.7

SE130614.012

%

60 - 130%

86

BH7 0.15-0.45

SE130614.013

%

60 - 130%

86

BH7 1.4-1.7

SE130614.014

%

60 - 130%

86

BH8 0.2-0.4

SE130614.015

%

60 - 130%

86

BH9 0.2-0.5

SE130614.016

%

60 - 130%

88

BH9 2.0-2.3

SE130614.017

%

60 - 130%

90

BH9 2.55-2.65

SE130614.018

%

60 - 130%

90

BH10 0.23-0.5

SE130614.019

%

60 - 130%

88

BH10 0.55-0.65

SE130614.020

%

60 - 130%

84

Duplicate D2

SE130614.021

%

60 - 130%

88

PCBs in Soil

Parameter Tetrachloro-m-xylene (TCMX) (Surrogate)

Method: ME-(AU)-[ENV]AN400/AN420

Sample Name

Units

Criteria

Recovery %

BH2 0.5-0.8

Sample Number SE130614.004

%

60 - 130%

109

BH2 4.5-4.8

SE130614.005

%

60 - 130%

111

BH2 5.1-5.25

SE130614.006

%

60 - 130%

111

BH3 1.5-1.8

SE130614.008

%

60 - 130%

107

BH5 0.1-0.4

SE130614.010

%

60 - 130%

111

BH5 0.6-0.7

SE130614.011

%

60 - 130%

107

BH9 0.2-0.5

SE130614.016

%

60 - 130%

109

BH9 2.0-2.3

SE130614.017

%

60 - 130%

111

BH9 2.55-2.65

SE130614.018

%

60 - 130%

110

BH10 0.23-0.5

SE130614.019

%

60 - 130%

107

BH10 0.55-0.65

SE130614.020

%

60 - 130%

103

Duplicate D2

SE130614.021

%

60 - 130%

99

VOC’s in Soil

Parameter Bromofluorobenzene (Surrogate)

d4-1,2-dichloroethane (Surrogate)

27/8/2014

Method: ME-(AU)-[ENV]AN433/AN434

Sample Name

Units

Criteria

Recovery %

BH2 0.5-0.8

Sample Number SE130614.004

%

60 - 130%

108

BH2 4.5-4.8

SE130614.005

%

60 - 130%

122

BH2 5.1-5.25

SE130614.006

%

60 - 130%

104

BH3 1.5-1.8

SE130614.008

%

60 - 130%

114

BH5 0.1-0.4

SE130614.010

%

60 - 130%

114

BH5 0.6-0.7

SE130614.011

%

60 - 130%

114

BH9 0.2-0.5

SE130614.016

%

60 - 130%

119

BH9 2.0-2.3

SE130614.017

%

60 - 130%

100

BH9 2.55-2.65

SE130614.018

%

60 - 130%

90

BH10 0.23-0.5

SE130614.019

%

60 - 130%

116

BH10 0.55-0.65

SE130614.020

%

60 - 130%

116

Duplicate D2

SE130614.021

%

60 - 130%

118

Trip Spike TS1

SE130614.022

%

60 - 130%

116

Trip Spike TS2

SE130614.023

%

60 - 130%

110

BH2 0.5-0.8

SE130614.004

%

60 - 130%

79

BH2 4.5-4.8

SE130614.005

%

60 - 130%

93

BH2 5.1-5.25

SE130614.006

%

60 - 130%

96

BH3 1.5-1.8

SE130614.008

%

60 - 130%

114

Page 9 of 29


SE130614 R0

SURROGATES

Surrogate results are evaluated against upper and lower limit criteria established in the SGS QA /QC plan (Ref: MP-(AU)-[ENV]QU-022). At least two of three routine level soil sample surrogate spike recoveries for BTEX /VOC are to be within 70-130% where control charts have not been developed and within the established control limits for charted surrogates. Matrix effects may void this as an acceptance criterion. Water sample surrogate spike recoveries are to be within 40-130%. The presence of emulsions, surfactants and particulates may void this as an acceptance criterion. Result is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

VOC’s in Soil (continued)

Parameter d4-1,2-dichloroethane (Surrogate)

d8-toluene (Surrogate)

Dibromofluoromethane (Surrogate)

Method: ME-(AU)-[ENV]AN433/AN434

Sample Name

Sample Number

Units

Criteria

Recovery %

BH5 0.1-0.4

SE130614.010

%

60 - 130%

114

BH5 0.6-0.7

SE130614.011

%

60 - 130%

114

BH9 0.2-0.5

SE130614.016

%

60 - 130%

119

BH9 2.0-2.3

SE130614.017

%

60 - 130%

97

BH9 2.55-2.65

SE130614.018

%

60 - 130%

104

BH10 0.23-0.5

SE130614.019

%

60 - 130%

107

BH10 0.55-0.65

SE130614.020

%

60 - 130%

115

Duplicate D2

SE130614.021

%

60 - 130%

108

Trip Spike TS1

SE130614.022

%

60 - 130%

117

Trip Spike TS2

SE130614.023

%

60 - 130%

106

BH2 0.5-0.8

SE130614.004

%

60 - 130%

110

BH2 4.5-4.8

SE130614.005

%

60 - 130%

117

BH2 5.1-5.25

SE130614.006

%

60 - 130%

99

BH3 1.5-1.8

SE130614.008

%

60 - 130%

115

BH5 0.1-0.4

SE130614.010

%

60 - 130%

116

BH5 0.6-0.7

SE130614.011

%

60 - 130%

119

BH9 0.2-0.5

SE130614.016

%

60 - 130%

119

BH9 2.0-2.3

SE130614.017

%

60 - 130%

96

BH9 2.55-2.65

SE130614.018

%

60 - 130%

90

BH10 0.23-0.5

SE130614.019

%

60 - 130%

111

BH10 0.55-0.65

SE130614.020

%

60 - 130%

118

Duplicate D2

SE130614.021

%

60 - 130%

105

Trip Spike TS1

SE130614.022

%

60 - 130%

123

Trip Spike TS2

SE130614.023

%

60 - 130%

100

BH2 0.5-0.8

SE130614.004

%

60 - 130%

89

BH2 4.5-4.8

SE130614.005

%

60 - 130%

101

BH2 5.1-5.25

SE130614.006

%

60 - 130%

107

BH3 1.5-1.8

SE130614.008

%

60 - 130%

124

BH5 0.1-0.4

SE130614.010

%

60 - 130%

122

BH5 0.6-0.7

SE130614.011

%

60 - 130%

120

BH9 0.2-0.5

SE130614.016

%

60 - 130%

127

BH9 2.0-2.3

SE130614.017

%

60 - 130%

104

BH9 2.55-2.65

SE130614.018

%

60 - 130%

108

BH10 0.23-0.5

SE130614.019

%

60 - 130%

113

BH10 0.55-0.65

SE130614.020

%

60 - 130%

114

Duplicate D2

SE130614.021

%

60 - 130%

115

Trip Spike TS1

SE130614.022

%

60 - 130%

122

Trip Spike TS2

SE130614.023

%

60 - 130%

110

Volatile Petroleum Hydrocarbons in Soil

Parameter Bromofluorobenzene (Surrogate)

d4-1,2-dichloroethane (Surrogate)

27/8/2014

Method: ME-(AU)-[ENV]AN433/AN434/AN410

Sample Name

Units

Criteria

Recovery %

BH2 0.5-0.8

Sample Number SE130614.004

%

60 - 130%

108

BH2 4.5-4.8

SE130614.005

%

60 - 130%

122

BH2 5.1-5.25

SE130614.006

%

60 - 130%

104

BH3 1.5-1.8

SE130614.008

%

60 - 130%

114

BH5 0.1-0.4

SE130614.010

%

60 - 130%

114

BH5 0.6-0.7

SE130614.011

%

60 - 130%

114

BH9 0.2-0.5

SE130614.016

%

60 - 130%

119

BH9 2.0-2.3

SE130614.017

%

60 - 130%

100

BH9 2.55-2.65

SE130614.018

%

60 - 130%

90

BH10 0.23-0.5

SE130614.019

%

60 - 130%

116

BH10 0.55-0.65

SE130614.020

%

60 - 130%

116

Duplicate D2

SE130614.021

%

60 - 130%

118

BH2 0.5-0.8

SE130614.004

%

60 - 130%

79

BH2 4.5-4.8

SE130614.005

%

60 - 130%

93

BH2 5.1-5.25

SE130614.006

%

60 - 130%

96

BH3 1.5-1.8

SE130614.008

%

60 - 130%

114

BH5 0.1-0.4

SE130614.010

%

60 - 130%

114

BH5 0.6-0.7

SE130614.011

%

60 - 130%

114

BH9 0.2-0.5

SE130614.016

%

60 - 130%

119

BH9 2.0-2.3

SE130614.017

%

60 - 130%

97

Page 10 of 29


SE130614 R0

SURROGATES

Surrogate results are evaluated against upper and lower limit criteria established in the SGS QA /QC plan (Ref: MP-(AU)-[ENV]QU-022). At least two of three routine level soil sample surrogate spike recoveries for BTEX /VOC are to be within 70-130% where control charts have not been developed and within the established control limits for charted surrogates. Matrix effects may void this as an acceptance criterion. Water sample surrogate spike recoveries are to be within 40-130%. The presence of emulsions, surfactants and particulates may void this as an acceptance criterion. Result is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

Volatile Petroleum Hydrocarbons in Soil (continued)

Parameter d4-1,2-dichloroethane (Surrogate)

d8-toluene (Surrogate)

Dibromofluoromethane (Surrogate)

27/8/2014

Method: ME-(AU)-[ENV]AN433/AN434/AN410

Sample Name

Sample Number

Units

Criteria

Recovery %

BH9 2.55-2.65

SE130614.018

%

60 - 130%

104

BH10 0.23-0.5

SE130614.019

%

60 - 130%

107

BH10 0.55-0.65

SE130614.020

%

60 - 130%

115

Duplicate D2

SE130614.021

%

60 - 130%

108

BH2 0.5-0.8

SE130614.004

%

60 - 130%

110

BH2 4.5-4.8

SE130614.005

%

60 - 130%

117

BH2 5.1-5.25

SE130614.006

%

60 - 130%

99

BH3 1.5-1.8

SE130614.008

%

60 - 130%

115

BH5 0.1-0.4

SE130614.010

%

60 - 130%

116

BH5 0.6-0.7

SE130614.011

%

60 - 130%

119

BH9 0.2-0.5

SE130614.016

%

60 - 130%

119

BH9 2.0-2.3

SE130614.017

%

60 - 130%

96

BH9 2.55-2.65

SE130614.018

%

60 - 130%

90

BH10 0.23-0.5

SE130614.019

%

60 - 130%

111

BH10 0.55-0.65

SE130614.020

%

60 - 130%

118

Duplicate D2

SE130614.021

%

60 - 130%

105

BH2 0.5-0.8

SE130614.004

%

60 - 130%

89

BH2 4.5-4.8

SE130614.005

%

60 - 130%

101

BH2 5.1-5.25

SE130614.006

%

60 - 130%

107

BH3 1.5-1.8

SE130614.008

%

60 - 130%

124

BH5 0.1-0.4

SE130614.010

%

60 - 130%

122

BH5 0.6-0.7

SE130614.011

%

60 - 130%

120

BH9 0.2-0.5

SE130614.016

%

60 - 130%

127

BH9 2.0-2.3

SE130614.017

%

60 - 130%

104

BH9 2.55-2.65

SE130614.018

%

60 - 130%

108

BH10 0.23-0.5

SE130614.019

%

60 - 130%

113

BH10 0.55-0.65

SE130614.020

%

60 - 130%

114

Duplicate D2

SE130614.021

%

60 - 130%

115

Page 11 of 29


SE130614 R0

METHOD BLANKS

Blank results are evaluated against the limit of reporting (LOR), for the chosen method and its associated instrumentation, method detection limit (MDL).

typically 2.5 times the statistically determined

Result is shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria.

Exchangeable Cations and Cation Exchange Capacity (CEC/ESP/SAR)

Sample Number

Method: ME-(AU)-[ENV]AN122

Parameter

Units

Sample Number

Parameter

Units

LOR

Result

LB062755.001

Mercury

mg/L

0.0001

<0.0001

Sample Number

Parameter

Units

LOR

Result

LB062739.001

Mercury

mg/kg

0.01

<0.01

LB062741.001

Mercury

mg/kg

0.01

<0.01

Sample Number

Parameter

Units

LOR

LB062600.001

Arsenic, As

mg/L

0.02

<0.02

Cadmium, Cd

mg/L

0.001

<0.001

Chromium, Cr

mg/L

0.005

<0.005

Copper, Cu

mg/L

0.005

<0.005

Lead, Pb

mg/L

0.02

<0.02

Nickel, Ni

mg/L

0.005

<0.005

Zinc, Zn

mg/L

0.01

<0.01

Mercury (dissolved) in Water

LOR

Method: ME-(AU)-[ENV]AN311/AN312

Mercury in Soil

Method: ME-(AU)-[ENV]AN312

Metals in Water (Dissolved) by ICPOES

Method: ME-(AU)-[ENV]AN320/AN321

OC Pesticides in Soil

Result

Method: ME-(AU)-[ENV]AN400/AN420

Sample Number

Parameter

Units

LOR

Result

LB062562.001

Hexachlorobenzene (HCB)

mg/kg

0.1

<0.1

Alpha BHC

mg/kg

0.1

<0.1

Lindane

mg/kg

0.1

<0.1

Heptachlor

mg/kg

0.1

<0.1

Aldrin

mg/kg

0.1

<0.1

Beta BHC

mg/kg

0.1

<0.1

Delta BHC

mg/kg

0.1

<0.1

Heptachlor epoxide

mg/kg

0.1

<0.1

Alpha Endosulfan

mg/kg

0.2

<0.2

Gamma Chlordane

mg/kg

0.1

<0.1

Alpha Chlordane

mg/kg

0.1

<0.1

p,p'-DDE

mg/kg

0.1

<0.1

Dieldrin

mg/kg

0.05

<0.05

Endrin

mg/kg

0.2

<0.2

Beta Endosulfan

mg/kg

0.2

<0.2

p,p'-DDD

mg/kg

0.1

<0.1

p,p'-DDT

mg/kg

0.1

<0.1

Endosulfan sulphate

mg/kg

0.1

<0.1

Endrin Aldehyde

mg/kg

0.1

<0.1

Methoxychlor

mg/kg

0.1

<0.1

Endrin Ketone

mg/kg

0.1

<0.1

Isodrin

mg/kg

0.1

<0.1

Mirex

mg/kg

0.1

<0.1

%

-

101

Hexachlorobenzene (HCB)

mg/kg

0.1

<0.1

Alpha BHC

mg/kg

0.1

<0.1

Lindane

mg/kg

0.1

<0.1

Heptachlor

mg/kg

0.1

<0.1

Aldrin

mg/kg

0.1

<0.1

Beta BHC

mg/kg

0.1

<0.1

Delta BHC

mg/kg

0.1

<0.1

Heptachlor epoxide

mg/kg

0.1

<0.1

Alpha Endosulfan

mg/kg

0.2

<0.2

Gamma Chlordane

mg/kg

0.1

<0.1

Alpha Chlordane

mg/kg

0.1

<0.1

Surrogates LB062563.001

27/8/2014

Tetrachloro-m-xylene (TCMX) (Surrogate)

Page 12 of 29


SE130614 R0

METHOD BLANKS

Blank results are evaluated against the limit of reporting (LOR), for the chosen method and its associated instrumentation, method detection limit (MDL).

typically 2.5 times the statistically determined

Result is shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria.

OC Pesticides in Soil (continued)

Method: ME-(AU)-[ENV]AN400/AN420

Sample Number

Parameter

Units

LOR

LB062563.001

p,p'-DDE

mg/kg

0.1

<0.1

Dieldrin

mg/kg

0.05

<0.05

Endrin

mg/kg

0.2

<0.2

Beta Endosulfan

mg/kg

0.2

<0.2

p,p'-DDD

mg/kg

0.1

<0.1

p,p'-DDT

mg/kg

0.1

<0.1

Endosulfan sulphate

mg/kg

0.1

<0.1

Endrin Aldehyde

mg/kg

0.1

<0.1

Methoxychlor

mg/kg

0.1

<0.1

Endrin Ketone

mg/kg

0.1

<0.1

Isodrin

mg/kg

0.1

<0.1

Mirex

mg/kg

0.1

<0.1

%

-

Surrogates

Tetrachloro-m-xylene (TCMX) (Surrogate)

PAH (Polynuclear Aromatic Hydrocarbons) in Soil

Result

103

Method: ME-(AU)-[ENV]AN420

Sample Number

Parameter

Units

LOR

Result

LB062562.001

Naphthalene

mg/kg

0.1

<0.1

2-methylnaphthalene

mg/kg

0.1

<0.1

1-methylnaphthalene

mg/kg

0.1

<0.1

Acenaphthylene

mg/kg

0.1

<0.1

Acenaphthene

mg/kg

0.1

<0.1

Fluorene

mg/kg

0.1

<0.1

Phenanthrene

mg/kg

0.1

<0.1

Anthracene

mg/kg

0.1

<0.1

Fluoranthene

mg/kg

0.1

<0.1

Pyrene

mg/kg

0.1

<0.1

Benzo(a)anthracene

mg/kg

0.1

<0.1

Chrysene

mg/kg

0.1

<0.1

Benzo(b&j&k)fluoranthene

mg/kg

0.2

<0.2

Benzo(a)pyrene

mg/kg

0.1

<0.1

Indeno(1,2,3-cd)pyrene

mg/kg

0.1

<0.1

Dibenzo(a&h)anthracene

mg/kg

0.1

<0.1

Benzo(ghi)perylene

mg/kg

0.1

<0.1

Total PAH

mg/kg

0.8

<0.8

d5-nitrobenzene (Surrogate)

%

-

102

2-fluorobiphenyl (Surrogate)

%

-

96

d14-p-terphenyl (Surrogate)

%

-

102

Naphthalene

mg/kg

0.1

<0.1

2-methylnaphthalene

mg/kg

0.1

<0.1

1-methylnaphthalene

mg/kg

0.1

<0.1

Acenaphthylene

mg/kg

0.1

<0.1

Acenaphthene

mg/kg

0.1

<0.1

Fluorene

mg/kg

0.1

<0.1

Phenanthrene

mg/kg

0.1

<0.1

Anthracene

mg/kg

0.1

<0.1

Fluoranthene

mg/kg

0.1

<0.1

Pyrene

mg/kg

0.1

<0.1

Benzo(a)anthracene

mg/kg

0.1

<0.1

Chrysene

mg/kg

0.1

<0.1

Benzo(b&j&k)fluoranthene

mg/kg

0.2

<0.2

Benzo(a)pyrene

mg/kg

0.1

<0.1

Indeno(1,2,3-cd)pyrene

mg/kg

0.1

<0.1

Dibenzo(a&h)anthracene

mg/kg

0.1

<0.1

Benzo(ghi)perylene

mg/kg

0.1

<0.1

Total PAH

mg/kg

0.8

<0.8

d5-nitrobenzene (Surrogate)

%

-

86

2-fluorobiphenyl (Surrogate)

%

-

80

d14-p-terphenyl (Surrogate)

%

-

90

Surrogates

LB062563.001

Surrogates

PCBs in Soil

Sample Number

27/8/2014

Method: ME-(AU)-[ENV]AN400/AN420

Parameter

Units

LOR

Page 13 of 29


SE130614 R0

METHOD BLANKS

Blank results are evaluated against the limit of reporting (LOR), for the chosen method and its associated instrumentation, method detection limit (MDL).

typically 2.5 times the statistically determined

Result is shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria.

PCBs in Soil (continued)

Method: ME-(AU)-[ENV]AN400/AN420

Sample Number

Parameter

Units

LOR

Result

LB062562.001

Arochlor 1016

mg/kg

0.2

<0.2

Arochlor 1221

mg/kg

0.2

<0.2

Arochlor 1232

mg/kg

0.2

<0.2

Arochlor 1242

mg/kg

0.2

<0.2

Arochlor 1248

mg/kg

0.2

<0.2

Arochlor 1254

mg/kg

0.2

<0.2

Arochlor 1260

mg/kg

0.2

<0.2

Arochlor 1262

mg/kg

0.2

<0.2

Arochlor 1268

mg/kg

0.2

<0.2

Total PCBs (Arochlors)

mg/kg

1

<1

%

-

101

Arochlor 1016

mg/kg

0.2

<0.2

Arochlor 1221

mg/kg

0.2

<0.2

Arochlor 1232

mg/kg

0.2

<0.2

Arochlor 1242

mg/kg

0.2

<0.2

Arochlor 1248

mg/kg

0.2

<0.2

Arochlor 1254

mg/kg

0.2

<0.2

Arochlor 1260

mg/kg

0.2

<0.2

Arochlor 1262

mg/kg

0.2

<0.2

Arochlor 1268

mg/kg

0.2

<0.2

Total PCBs (Arochlors)

mg/kg

1

<1

%

-

103

Surrogates LB062563.001

Surrogates

Tetrachloro-m-xylene (TCMX) (Surrogate)

Tetrachloro-m-xylene (TCMX) (Surrogate)

Total Cyanide in soil by Discrete Analyser (Aquakem)

Method: ME-(AU)-[ENV]AN077/AN287

Sample Number

Parameter

Units

LOR

Result

LB062764.001

Total Cyanide

mg/kg

0.1

<0.1

Sample Number

Parameter

Units

LOR

Result

LB062763.001

Total Phenols

mg/kg

0.1

<0.1

LB062835.001

Total Phenols

mg/kg

0.1

<0.1

Total Phenolics in Soil

Method: ME-(AU)-[ENV]AN289

Total Recoverable Metals in Soil by ICPOES from EPA 200.8 Digest

Method: ME-(AU)-[ENV]AN040/AN320

Sample Number

Parameter

Units

LOR

LB062732.001

Arsenic, As

mg/kg

3

<3

Cadmium, Cd

mg/kg

0.3

<0.3

Chromium, Cr

mg/kg

0.3

<0.3

Copper, Cu

mg/kg

0.5

<0.5

Lead, Pb

mg/kg

1

<1

Nickel, Ni

mg/kg

0.5

<0.5

Zinc, Zn

mg/kg

0.5

<0.5

Arsenic, As

mg/kg

3

<3

Cadmium, Cd

mg/kg

0.3

<0.3

Chromium, Cr

mg/kg

0.3

<0.3

Copper, Cu

mg/kg

0.5

<0.5

Lead, Pb

mg/kg

1

<1

Nickel, Ni

mg/kg

0.5

<0.5

Zinc, Zn

mg/kg

0.5

LB062733.001

TRH (Total Recoverable Hydrocarbons) in Soil

Result

<0.5

Method: ME-(AU)-[ENV]AN403

Sample Number

Parameter

Units

LOR

Result

LB062562.001

TRH C10-C14

mg/kg

20

<20

TRH C15-C28

mg/kg

45

<45

TRH C29-C36

mg/kg

45

<45

TRH C37-C40

mg/kg

100

<100

TRH C10-C36 Total

mg/kg

110

<110

TRH C10-C14

mg/kg

20

<20

TRH C15-C28

mg/kg

45

<45

TRH C29-C36

mg/kg

45

<45

TRH C37-C40

mg/kg

100

<100

LB062563.001

27/8/2014

Page 14 of 29


SE130614 R0

METHOD BLANKS

Blank results are evaluated against the limit of reporting (LOR), for the chosen method and its associated instrumentation, method detection limit (MDL).

typically 2.5 times the statistically determined

Result is shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria.

TRH (Total Recoverable Hydrocarbons) in Soil (continued)

Method: ME-(AU)-[ENV]AN403

Sample Number

Parameter

Units

LOR

Result

LB062563.001

TRH C10-C36 Total

mg/kg

110

<110

VOC’s in Soil

Method: ME-(AU)-[ENV]AN433/AN434

Sample Number LB062558.001

Parameter

Units

LOR

Result

Monocyclic Aromatic

Benzene

mg/kg

0.1

<0.1

Hydrocarbons

Toluene

mg/kg

0.1

<0.1

Ethylbenzene

mg/kg

0.1

<0.1

m/p-xylene

mg/kg

0.2

<0.2

o-xylene

mg/kg

0.1

<0.1

Polycyclic VOCs

Naphthalene

mg/kg

0.1

<0.1

Surrogates

Dibromofluoromethane (Surrogate)

%

-

96

d4-1,2-dichloroethane (Surrogate)

%

-

92

d8-toluene (Surrogate)

%

-

107

Bromofluorobenzene (Surrogate)

%

-

96

Total BTEX*

mg/kg

0.6

<0.3

Sample Number

Parameter

Units

LOR

Result

LB062558.001

TRH C6-C9

mg/kg

20

<20

Dibromofluoromethane (Surrogate)

%

-

96

d4-1,2-dichloroethane (Surrogate)

%

-

92

d8-toluene (Surrogate)

%

-

107

Totals

Volatile Petroleum Hydrocarbons in Soil

Surrogates

27/8/2014

Method: ME-(AU)-[ENV]AN433/AN434/AN410

Page 15 of 29


SE130614 R0

DUPLICATES

Duplicates are calculated as Relative Percentage Difference (RPD) using the formula: RPD = | OriginalResult - ReplicateResult | x 100 / Mean The RPD is evaluated against the Maximum Allowable Difference (MAD) criteria and can be graphically represented by a curve calculated from the Statistical Detection Limit (SDL) and Limiting Repeatability (LR) using the formula: MAD = 100 x SDL / Mean + LR Where the Maximum Allowable Difference evaluates to a number larger than 200 it is displayed as 200. RPD is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

Mercury (dissolved) in Water

Method: ME-(AU)-[ENV]AN311/AN312

Original

Duplicate

Parameter

Units

LOR

Original

SE130689.001

LB062755.014

Duplicate

Criteria %

RPD %

Mercury

µg/L

0.0001

<0.00005

0.00000

200

SE130742.002

6

LB062755.019

Mercury

µg/L

0.0001

<0.0001

<0.0001

200

0

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

SE130591.008

LB062739.014

Mercury

mg/kg

0.01

<0.01

<0.01

200

0

SE130614.005

LB062739.024

Mercury

mg/kg

0.01

0.40

0.46

42

14

SE130614.015

LB062741.014

Mercury

mg/kg

0.01

0.02

0.02

200

0

SE130617.003

LB062741.024

Mercury

mg/kg

0.01

0.02

0.02

200

0

Mercury in Soil

Method: ME-(AU)-[ENV]AN312

Moisture Content

RPD %

Method: ME-(AU)-[ENV]AN002

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.010

LB062788.011

% Moisture

%w/w

0.5

23

23

34

1

SE130614.020

LB062788.022

% Moisture

%

0.5

16

17

36

8

SE130614.021

LB062788.024

% Moisture

%

0.5

21

21

35

1

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.011

LB062562.020

Hexachlorobenzene (HCB)

mg/kg

0.1

<0.1

<0.1

200

0

Alpha BHC

mg/kg

0.1

<0.1

<0.1

200

0

Lindane

mg/kg

0.1

<0.1

<0.1

200

0

Heptachlor

mg/kg

0.1

<0.1

<0.1

200

0

Aldrin

mg/kg

0.1

<0.1

<0.1

200

0

Beta BHC

mg/kg

0.1

<0.1

<0.1

200

0

Delta BHC

mg/kg

0.1

<0.1

<0.1

200

0

Heptachlor epoxide

mg/kg

0.1

<0.1

<0.1

200

0

o,p'-DDE

mg/kg

0.1

<0.1

<0.1

200

0

Alpha Endosulfan

mg/kg

0.2

<0.2

<0.2

200

0

Gamma Chlordane

mg/kg

0.1

<0.1

<0.1

200

0

Alpha Chlordane

mg/kg

0.1

<0.1

<0.1

200

0

trans-Nonachlor

mg/kg

0.1

<0.1

<0.1

200

0

p,p'-DDE

mg/kg

0.1

<0.1

<0.1

200

0

Dieldrin

mg/kg

0.05

<0.05

<0.05

200

0

Endrin

mg/kg

0.2

<0.2

<0.2

200

0

o,p'-DDD

mg/kg

0.1

<0.1

<0.1

200

0

o,p'-DDT

mg/kg

0.1

<0.1

<0.1

200

0

Beta Endosulfan

mg/kg

0.2

<0.2

<0.2

200

0

p,p'-DDD

mg/kg

0.1

<0.1

<0.1

200

0

p,p'-DDT

mg/kg

0.1

<0.1

<0.1

200

0

Endosulfan sulphate

mg/kg

0.1

<0.1

<0.1

200

0

Endrin Aldehyde

mg/kg

0.1

<0.1

<0.1

200

0

Methoxychlor

mg/kg

0.1

<0.1

<0.1

200

0

Endrin Ketone

mg/kg

0.1

<0.1

<0.1

200

0

Isodrin

mg/kg

0.1

<0.1

<0.1

200

0

Mirex

mg/kg

0.1

<0.1

<0.1

200

0

Tetrachloro-m-xylene (TCMX) (Surrogate)

mg/kg

-

0.16

0.16

30

1

Hexachlorobenzene (HCB)

mg/kg

0.1

<0.1

<0.1

200

0

Alpha BHC

mg/kg

0.1

<0.1

<0.1

200

0

Lindane

mg/kg

0.1

<0.1

<0.1

200

0

Heptachlor

mg/kg

0.1

<0.1

<0.1

200

0

Aldrin

mg/kg

0.1

<0.1

<0.1

200

0

Beta BHC

mg/kg

0.1

<0.1

<0.1

200

0

Delta BHC

mg/kg

0.1

<0.1

<0.1

200

0

Heptachlor epoxide

mg/kg

0.1

<0.1

<0.1

200

0

o,p'-DDE

mg/kg

0.1

<0.1

<0.1

200

0

Alpha Endosulfan

mg/kg

0.2

<0.2

<0.2

200

0

Gamma Chlordane

mg/kg

0.1

<0.1

<0.1

200

0

Alpha Chlordane

mg/kg

0.1

<0.1

<0.1

200

0

trans-Nonachlor

mg/kg

0.1

<0.1

<0.1

200

0

p,p'-DDE

mg/kg

0.1

<0.1

<0.1

200

0

OC Pesticides in Soil

Method: ME-(AU)-[ENV]AN400/AN420

Surrogates SE130614.020

27/8/2014

LB062563.008

Page 16 of 29


SE130614 R0

DUPLICATES

Duplicates are calculated as Relative Percentage Difference (RPD) using the formula: RPD = | OriginalResult - ReplicateResult | x 100 / Mean The RPD is evaluated against the Maximum Allowable Difference (MAD) criteria and can be graphically represented by a curve calculated from the Statistical Detection Limit (SDL) and Limiting Repeatability (LR) using the formula: MAD = 100 x SDL / Mean + LR Where the Maximum Allowable Difference evaluates to a number larger than 200 it is displayed as 200. RPD is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

OC Pesticides in Soil (continued)

Method: ME-(AU)-[ENV]AN400/AN420

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.020

LB062563.008

Dieldrin

mg/kg

0.05

<0.05

<0.05

200

0

Endrin

mg/kg

0.2

<0.2

<0.2

200

0

o,p'-DDD

mg/kg

0.1

<0.1

<0.1

200

0

o,p'-DDT

mg/kg

0.1

<0.1

<0.1

200

0

Beta Endosulfan

mg/kg

0.2

<0.2

<0.2

200

0

p,p'-DDD

mg/kg

0.1

<0.1

<0.1

200

0

p,p'-DDT

mg/kg

0.1

<0.1

<0.1

200

0

Endosulfan sulphate

mg/kg

0.1

<0.1

<0.1

200

0

Endrin Aldehyde

mg/kg

0.1

<0.1

<0.1

200

0

Methoxychlor

mg/kg

0.1

<0.1

<0.1

200

0

Endrin Ketone

mg/kg

0.1

<0.1

<0.1

200

0

Isodrin

mg/kg

0.1

<0.1

<0.1

200

0

Mirex

mg/kg

0.1

<0.1

<0.1

200

0

Tetrachloro-m-xylene (TCMX) (Surrogate)

mg/kg

-

0.16

0.16

30

1

Surrogates

PAH (Polynuclear Aromatic Hydrocarbons) in Soil

Method: ME-(AU)-[ENV]AN420

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

SE130602.001

LB062562.004

Naphthalene

mg/kg

0.1

<0.1

<0.1

148

0

2-methylnaphthalene

mg/kg

0.1

0.7

0.5

46

33

1-methylnaphthalene

mg/kg

0.1

0.9

0.6

43

37

Acenaphthylene

mg/kg

0.1

<0.1

<0.1

200

0

Acenaphthene

mg/kg

0.1

<0.1

<0.1

200

0

Fluorene

mg/kg

0.1

<0.1

<0.1

200

0

Phenanthrene

mg/kg

0.1

<0.1

<0.1

200

0

Anthracene

mg/kg

0.1

<0.1

<0.1

200

0

Fluoranthene

mg/kg

0.1

<0.1

<0.1

200

0

Pyrene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(a)anthracene

mg/kg

0.1

<0.1

<0.1

200

0

Chrysene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(b&j)fluoranthene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(k)fluoranthene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(b&j&k)fluoranthene

mg/kg

0.2

<0.2

<0.2

200

0

Benzo(a)pyrene

mg/kg

0.1

<0.1

<0.1

200

0

Indeno(1,2,3-cd)pyrene

mg/kg

0.1

<0.1

<0.1

200

0

Dibenzo(a&h)anthracene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(ghi)perylene

mg/kg

0.1

<0.1

<0.1

200

0

Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.2

<0.2

<0.2

200

0

<LOR=0* Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.3

<0.3

<0.3

134

0

<LOR=LOR* PAHs (as BaP TEQ)-assume results Carcinogenic

TEQ (mg/kg)

0.2

<0.2

<0.2

175

0

<LOR=LOR/2* Total PAH

mg/kg

0.8

1.8

1.2

83

38

d5-nitrobenzene (Surrogate)

mg/kg

-

0.50

0.53

30

6

2-fluorobiphenyl (Surrogate)

mg/kg

-

0.45

0.49

30

9

d14-p-terphenyl (Surrogate)

mg/kg

-

0.46

0.50

30

8

Naphthalene

mg/kg

0.1

<0.1

<0.1

200

0

2-methylnaphthalene

mg/kg

0.1

<0.1

<0.1

200

0

1-methylnaphthalene

mg/kg

0.1

<0.1

<0.1

200

0

Acenaphthylene

mg/kg

0.1

<0.1

<0.1

200

0

Acenaphthene

mg/kg

0.1

<0.1

<0.1

200

0

Fluorene

mg/kg

0.1

<0.1

<0.1

200

0

Phenanthrene

mg/kg

0.1

<0.1

<0.1

197

0

Anthracene

mg/kg

0.1

<0.1

<0.1

200

0

Fluoranthene

mg/kg

0.1

0.2

0.1

101

29

Pyrene

mg/kg

0.1

0.2

0.1

110

40

Benzo(a)anthracene

mg/kg

0.1

<0.1

<0.1

184

0

Chrysene

mg/kg

0.1

<0.1

<0.1

184

0

Benzo(b&j)fluoranthene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(k)fluoranthene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(b&j&k)fluoranthene

mg/kg

0.2

<0.2

<0.2

200

0

Benzo(a)pyrene

mg/kg

0.1

<0.1

<0.1

197

0

Indeno(1,2,3-cd)pyrene

mg/kg

0.1

<0.1

<0.1

200

0

Dibenzo(a&h)anthracene

mg/kg

0.1

<0.1

<0.1

200

0

Surrogates

SE130614.011

27/8/2014

LB062562.023

RPD %

Page 17 of 29


SE130614 R0

DUPLICATES

Duplicates are calculated as Relative Percentage Difference (RPD) using the formula: RPD = | OriginalResult - ReplicateResult | x 100 / Mean The RPD is evaluated against the Maximum Allowable Difference (MAD) criteria and can be graphically represented by a curve calculated from the Statistical Detection Limit (SDL) and Limiting Repeatability (LR) using the formula: MAD = 100 x SDL / Mean + LR Where the Maximum Allowable Difference evaluates to a number larger than 200 it is displayed as 200. RPD is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

PAH (Polynuclear Aromatic Hydrocarbons) in Soil (continued)

Method: ME-(AU)-[ENV]AN420

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.011

LB062562.023

Benzo(ghi)perylene

mg/kg

0.1

<0.1

<0.1

200

0

Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.2

<0.2

<0.2

200

0

<LOR=0* Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.3

<0.3

<0.3

134

0

<LOR=LOR* PAHs (as BaP TEQ)-assume results Carcinogenic

TEQ (mg/kg)

0.2

<0.2

<0.2

175

0

<LOR=LOR/2* Total PAH

mg/kg

0.8

<0.8

<0.8

155

0

d5-nitrobenzene (Surrogate)

mg/kg

-

0.43

0.43

30

0

2-fluorobiphenyl (Surrogate)

mg/kg

-

0.40

0.41

30

2

d14-p-terphenyl (Surrogate)

mg/kg

-

0.45

0.47

30

4

Naphthalene

mg/kg

0.1

<0.1

<0.1

200

0

2-methylnaphthalene

mg/kg

0.1

<0.1

<0.1

200

0

1-methylnaphthalene

mg/kg

0.1

<0.1

<0.1

200

0

Acenaphthylene

mg/kg

0.1

<0.1

<0.1

200

0

Acenaphthene

mg/kg

0.1

<0.1

<0.1

200

0

Fluorene

mg/kg

0.1

<0.1

<0.1

200

0

Phenanthrene

mg/kg

0.1

<0.1

<0.1

200

0

Anthracene

mg/kg

0.1

<0.1

<0.1

200

0

Fluoranthene

mg/kg

0.1

<0.1

<0.1

200

0

Pyrene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(a)anthracene

mg/kg

0.1

<0.1

<0.1

200

0

Chrysene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(b&j)fluoranthene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(k)fluoranthene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(b&j&k)fluoranthene

mg/kg

0.2

<0.2

<0.2

200

0

Benzo(a)pyrene

mg/kg

0.1

<0.1

<0.1

200

0

Indeno(1,2,3-cd)pyrene

mg/kg

0.1

<0.1

<0.1

200

0

Dibenzo(a&h)anthracene

mg/kg

0.1

<0.1

<0.1

200

0

Benzo(ghi)perylene

mg/kg

0.1

<0.1

<0.1

200

0

Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.2

<0.2

<0.2

200

0

<LOR=0* Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.3

<0.3

<0.3

134

0

<LOR=LOR* PAHs (as BaP TEQ)-assume results Carcinogenic

TEQ (mg/kg)

0.2

<0.2

<0.2

175

0

<LOR=LOR/2* Total PAH

mg/kg

0.8

<0.8

<0.8

200

0

d5-nitrobenzene (Surrogate)

mg/kg

-

0.42

0.42

30

0

2-fluorobiphenyl (Surrogate)

mg/kg

-

0.40

0.40

30

0

d14-p-terphenyl (Surrogate)

mg/kg

-

0.48

0.48

30

0

Surrogates

SE130614.020

LB062563.008

Surrogates

PCBs in Soil

Method: ME-(AU)-[ENV]AN400/AN420

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.011

LB062562.020

Arochlor 1016

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1221

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1232

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1242

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1248

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1254

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1260

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1262

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1268

mg/kg

0.2

<0.2

<0.2

200

0

Total PCBs (Arochlors)

mg/kg

1

<1

<1

200

0

Tetrachloro-m-xylene (TCMX) (Surrogate)

mg/kg

-

0

0

30

1

Arochlor 1016

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1221

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1232

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1242

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1248

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1254

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1260

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1262

mg/kg

0.2

<0.2

<0.2

200

0

Arochlor 1268

mg/kg

0.2

<0.2

<0.2

200

0

Total PCBs (Arochlors)

mg/kg

1

<1

<1

200

0

Tetrachloro-m-xylene (TCMX) (Surrogate)

mg/kg

-

0

0

30

1

Surrogates SE130614.020

LB062563.008

Surrogates

pH in soil (1:5)

Original

27/8/2014

Method: ME-(AU)-[ENV]AN101

Duplicate

Parameter

Units

LOR

Page 18 of 29


SE130614 R0

DUPLICATES

Duplicates are calculated as Relative Percentage Difference (RPD) using the formula: RPD = | OriginalResult - ReplicateResult | x 100 / Mean The RPD is evaluated against the Maximum Allowable Difference (MAD) criteria and can be graphically represented by a curve calculated from the Statistical Detection Limit (SDL) and Limiting Repeatability (LR) using the formula: MAD = 100 x SDL / Mean + LR Where the Maximum Allowable Difference evaluates to a number larger than 200 it is displayed as 200. RPD is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

pH in soil (1:5) (continued)

Method: ME-(AU)-[ENV]AN101

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

SE130614.011

LB062682.014

Criteria %

RPD %

pH

pH Units

-

5.9

5.9

32

SE130614.020

1

LB062682.024

pH

pH Units

-

4.7

4.5

32

3

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.011

LB062858.015

Total Organic Carbon

%w/w

0.05

0.62

0.59

23

4

SE130614.020

LB062858.024

Total Organic Carbon

%w/w

0.05

0.16

0.16

46

3

TOC in Soil

Method: ME-(AU)-[ENV]AN188

Total Cyanide in soil by Discrete Analyser (Aquakem)

Method: ME-(AU)-[ENV]AN077/AN287

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.004

LB062764.004

Total Cyanide

mg/kg

0.1

0.2

0.2

200

0

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.004

LB062763.004

Total Phenols

mg/kg

0.1

0.6

0.7

30

13

SE130614.020

LB062835.004

Total Phenols

mg/kg

0.1

<0.1

0.2

94

56

SE130633.001

LB062763.015

Total Phenols

mg/kg

0.1

1.8

1.9

21

6

Total Phenolics in Soil

Method: ME-(AU)-[ENV]AN289

Total Recoverable Metals in Soil by ICPOES from EPA 200.8 Digest

Method: ME-(AU)-[ENV]AN040/AN320

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130591.008

LB062732.014

Arsenic, As

mg/kg

3

<3

<3

200

0

Cadmium, Cd

mg/kg

0.3

<0.3

<0.3

200

0

Chromium, Cr

mg/kg

0.3

2.8

2.7

48

2

Copper, Cu

mg/kg

0.5

<0.5

<0.5

200

0

Lead, Pb

mg/kg

1

<1

<1

200

0

Nickel, Ni

mg/kg

0.5

1.3

1.3

69

1

Zinc, Zn

mg/kg

0.5

0.9

0.5

200

0

Arsenic, As

mg/kg

3

30

29

33

1

Cadmium, Cd

mg/kg

0.3

0.8

0.7

70

4

Chromium, Cr

mg/kg

0.3

52

50

31

4

Copper, Cu

mg/kg

0.5

130

130

30

1

Lead, Pb

mg/kg

1

120

110

31

5

Nickel, Ni

mg/kg

0.5

8.3

7.7

36

7

Zinc, Zn

mg/kg

0.5

260

240

31

7

Arsenic, As

mg/kg

3

4

5

51

13

Cadmium, Cd

mg/kg

0.3

0.5

0.5

95

4

Chromium, Cr

mg/kg

0.3

97

57

31

52 ②

Copper, Cu

mg/kg

0.5

15

14

33

9

Lead, Pb

mg/kg

1

10

9

41

2

Nickel, Ni

mg/kg

0.5

50

42

31

17

Zinc, Zn

mg/kg

0.5

35

32

36

8

Arsenic, As

mg/kg

3

<3

<3

200

0

Cadmium, Cd

mg/kg

0.3

<0.3

<0.3

200

0

Chromium, Cr

mg/kg

0.3

3.6

3.5

44

5

Copper, Cu

mg/kg

0.5

2.9

2.8

48

5

Lead, Pb

mg/kg

1

15

19

36

24

Nickel, Ni

mg/kg

0.5

2.6

2.5

49

4

Zinc, Zn

mg/kg

0.5

12

15

45

18

SE130614.005

SE130614.015

SE130617.003

LB062732.024

LB062733.014

LB062733.024

TRH (Total Recoverable Hydrocarbons) in Soil

Method: ME-(AU)-[ENV]AN403

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130602.001

LB062562.004

TRH C10-C14

mg/kg

20

140

120

45

14

TRH C15-C28

mg/kg

45

<45

<45

200

0

TRH C29-C36

mg/kg

45

<45

<45

200

0

TRH C37-C40

mg/kg

100

<100

<100

200

0

TRH C10-C36 Total

mg/kg

110

140

120

114

14

TRH C10-C40 Total

mg/kg

210

<210

<210

190

0

TRH >C10-C16 (F2)

mg/kg

25

150

130

48

15

TRH F Bands

27/8/2014

Page 19 of 29


SE130614 R0

DUPLICATES

Duplicates are calculated as Relative Percentage Difference (RPD) using the formula: RPD = | OriginalResult - ReplicateResult | x 100 / Mean The RPD is evaluated against the Maximum Allowable Difference (MAD) criteria and can be graphically represented by a curve calculated from the Statistical Detection Limit (SDL) and Limiting Repeatability (LR) using the formula: MAD = 100 x SDL / Mean + LR Where the Maximum Allowable Difference evaluates to a number larger than 200 it is displayed as 200. RPD is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

TRH (Total Recoverable Hydrocarbons) in Soil (continued)

Original

Duplicate

SE130602.001

LB062562.004

SE130614.011

TRH F Bands

LB062562.021

TRH F Bands

SE130614.020

LB062563.008

TRH F Bands

Method: ME-(AU)-[ENV]AN403

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

TRH >C16-C34 (F3)

mg/kg

90

<90

<90

200

0

TRH >C34-C40 (F4)

mg/kg

120

<120

<120

200

0

TRH C10-C14

mg/kg

20

<20

<20

200

0

TRH C15-C28

mg/kg

45

<45

<45

200

0

TRH C29-C36

mg/kg

45

<45

<45

200

0

TRH C37-C40

mg/kg

100

<100

<100

200

0

TRH C10-C36 Total

mg/kg

110

<110

<110

200

0

TRH C10-C40 Total

mg/kg

210

<210

<210

200

0

TRH >C10-C16 (F2)

mg/kg

25

<25

<25

200

0

TRH >C10-C16 (F2) minus Naphthalene

mg/kg

25

<25

<25

200

0

TRH >C16-C34 (F3)

mg/kg

90

<90

<90

200

0

TRH >C34-C40 (F4)

mg/kg

120

<120

<120

200

0

TRH C10-C14

mg/kg

20

<20

<20

200

0

TRH C15-C28

mg/kg

45

<45

<45

200

0

TRH C29-C36

mg/kg

45

<45

<45

200

0

TRH C37-C40

mg/kg

100

<100

<100

200

0

TRH C10-C36 Total

mg/kg

110

<110

<110

200

0

TRH C10-C40 Total

mg/kg

210

<210

<210

200

0

TRH >C10-C16 (F2)

mg/kg

25

<25

<25

200

0

TRH >C10-C16 (F2) minus Naphthalene

mg/kg

25

<25

<25

200

0

TRH >C16-C34 (F3)

mg/kg

90

<90

<90

200

0

TRH >C34-C40 (F4)

mg/kg

120

<120

<120

200

0

VOC’s in Soil

Method: ME-(AU)-[ENV]AN433/AN434

Original

Duplicate

SE130614.011

LB062558.015

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

Monocyclic

Benzene

mg/kg

0.1

<0.1

<0.1

200

0

Aromatic

Toluene

mg/kg

0.1

<0.1

<0.1

200

0

Ethylbenzene

mg/kg

0.1

<0.1

<0.1

200

0

m/p-xylene

mg/kg

0.2

<0.2

<0.2

200

0

o-xylene

mg/kg

0.1

<0.1

<0.1

200

0

Polycyclic

Naphthalene

mg/kg

0.1

<0.1

<0.1

200

0

VOCs Surrogates

Dibromofluoromethane (Surrogate)

mg/kg

-

6.0

5.6

50

7

d4-1,2-dichloroethane (Surrogate)

mg/kg

-

5.7

5.2

50

10

d8-toluene (Surrogate)

mg/kg

-

5.9

5.4

50

9

Bromofluorobenzene (Surrogate)

mg/kg

-

5.7

5.8

50

3

Total Xylenes*

mg/kg

0.3

<0.3

<0.3

200

0

Total BTEX*

mg/kg

0.6

<0.6

<0.3

200

0

Monocyclic

Benzene

mg/kg

0.1

<0.1

<0.1

200

0

Aromatic

Toluene

mg/kg

0.1

<0.1

<0.1

200

0

Ethylbenzene

mg/kg

0.1

<0.1

<0.1

200

0

m/p-xylene

mg/kg

0.2

<0.2

<0.2

200

0

o-xylene

mg/kg

0.1

<0.1

<0.1

200

0

Polycyclic

Naphthalene

mg/kg

0.1

<0.1

<0.1

200

0

VOCs Surrogates

Dibromofluoromethane (Surrogate)

mg/kg

-

5.8

5.6

50

2

d4-1,2-dichloroethane (Surrogate)

mg/kg

-

5.4

5.3

50

2

d8-toluene (Surrogate)

mg/kg

-

5.2

5.2

50

1

Bromofluorobenzene (Surrogate)

mg/kg

-

5.9

5.4

50

9

Total Xylenes*

mg/kg

0.3

<0.3

<0.3

200

0

Total BTEX*

mg/kg

0.6

<0.6

<0.6

200

0

Totals SE130614.021

LB062558.022

Totals

Volatile Petroleum Hydrocarbons in Soil

Method: ME-(AU)-[ENV]AN433/AN434/AN410

Original

Duplicate

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.011

LB062558.015

TRH C6-C10

mg/kg

25

<25

<25

200

0

TRH C6-C9

mg/kg

20

<20

<20

200

0

Dibromofluoromethane (Surrogate)

mg/kg

-

6.0

5.6

30

7

d4-1,2-dichloroethane (Surrogate)

mg/kg

-

5.7

5.2

30

10

d8-toluene (Surrogate)

mg/kg

-

5.9

5.4

30

9

Bromofluorobenzene (Surrogate)

mg/kg

-

5.7

5.8

30

3

Benzene (F0)

mg/kg

0.1

<0.1

<0.1

200

0

TRH C6-C10 minus BTEX (F1)

mg/kg

25

<25

<25

200

0

TRH C6-C10

mg/kg

25

<25

<25

200

0

TRH C6-C9

mg/kg

20

<20

<20

200

0

Surrogates

VPH F Bands SE130614.021

27/8/2014

LB062558.022

Page 20 of 29


SE130614 R0

DUPLICATES

Duplicates are calculated as Relative Percentage Difference (RPD) using the formula: RPD = | OriginalResult - ReplicateResult | x 100 / Mean The RPD is evaluated against the Maximum Allowable Difference (MAD) criteria and can be graphically represented by a curve calculated from the Statistical Detection Limit (SDL) and Limiting Repeatability (LR) using the formula: MAD = 100 x SDL / Mean + LR Where the Maximum Allowable Difference evaluates to a number larger than 200 it is displayed as 200. RPD is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

Volatile Petroleum Hydrocarbons in Soil (continued)

Original

Duplicate

SE130614.021

LB062558.022

Surrogates

VPH F Bands

27/8/2014

Method: ME-(AU)-[ENV]AN433/AN434/AN410

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

Dibromofluoromethane (Surrogate)

mg/kg

-

5.8

5.6

30

2

d4-1,2-dichloroethane (Surrogate)

mg/kg

-

5.4

5.3

30

2

d8-toluene (Surrogate)

mg/kg

-

5.2

5.2

30

1

Bromofluorobenzene (Surrogate)

mg/kg

-

5.9

5.4

30

9

Benzene (F0)

mg/kg

0.1

<0.1

<0.1

200

0

TRH C6-C10 minus BTEX (F1)

mg/kg

25

<25

<25

200

0

Page 21 of 29


SE130614 R0

LABORATORY CONTROL SAMPLES

Laboratory Control Standard (LCS) results are evaluated against an expected result, typically the concentration of analyte spiked into the control during the sample preparation stage, producing a percentage recovery. The criteria applied to the percentage recovery is established in the SGS QA /QC plan (Ref: MP-(AU)-[ENV]QU-022). For more information refer to the footnotes in the concluding page of this report. Recovery is shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria.

Exchangeable Cations and Cation Exchange Capacity (CEC/ESP/SAR)

Sample Number

Parameter

LB062800.002

LB062801.002

Method: ME-(AU)-[ENV]AN122

Units

LOR

Result

Expected

Criteria %

Recovery %

Exchangeable Sodium, Na

mg/kg

2

NA

160

80 - 120

119

Exchangeable Potassium, K

mg/kg

2

NA

330

80 - 120

101

Exchangeable Calcium, Ca

mg/kg

2

NA

4347

80 - 120

99

Exchangeable Magnesium, Mg

mg/kg

2

NA

1578

80 - 120

97

Exchangeable Sodium, Na

mg/kg

2

NA

160

80 - 120

118

Exchangeable Potassium, K

mg/kg

2

NA

330

80 - 120

102

Exchangeable Calcium, Ca

mg/kg

2

NA

4347

80 - 120

97

Exchangeable Magnesium, Mg

mg/kg

2

NA

1578

80 - 120

96

Mercury in Soil

Method: ME-(AU)-[ENV]AN312

Sample Number

Result

Expected

Criteria %

Recovery %

LB062739.002

Mercury

Parameter

mg/kg

Units

0.01

LOR

0.20

0.2

70 - 130

101

LB062741.002

Mercury

mg/kg

0.01

0.22

0.2

70 - 130

109

Result

Expected

Metals in Water (Dissolved) by ICPOES

Sample Number

Method: ME-(AU)-[ENV]AN320/AN321

Parameter

LB062600.002

Units

LOR

Criteria %

Recovery %

Arsenic, As

mg/L

0.02

1.9

2

80 - 120

97

Cadmium, Cd

mg/L

0.001

2.0

2

80 - 120

98

Chromium, Cr

mg/L

0.005

2.0

2

80 - 120

98

Copper, Cu

mg/L

0.005

2.0

2

80 - 120

98

Lead, Pb

mg/L

0.02

2.0

2

80 - 120

98

Nickel, Ni

mg/L

0.005

2.0

2

80 - 120

98

Zinc, Zn

mg/L

0.01

2.0

2

80 - 120

99

OC Pesticides in Soil

Method: ME-(AU)-[ENV]AN400/AN420

Sample Number

Parameter

LB062562.002

Surrogates LB062563.002

Surrogates

Result

Expected

Criteria %

Recovery %

Heptachlor

mg/kg

Units

0.1

LOR

0.2

0.2

60 - 140

117

Aldrin

mg/kg

0.1

0.2

0.2

60 - 140

122

Delta BHC

mg/kg

0.1

0.2

0.2

60 - 140

112

Dieldrin

mg/kg

0.05

0.23

0.2

60 - 140

115

Endrin

mg/kg

0.2

0.2

0.2

60 - 140

121

p,p'-DDT

mg/kg

0.1

0.2

0.2

60 - 140

100

Tetrachloro-m-xylene (TCMX) (Surrogate)

mg/kg

-

0.16

0.15

40 - 130

104

Heptachlor

mg/kg

0.1

0.2

0.2

60 - 140

118

Aldrin

mg/kg

0.1

0.2

0.2

60 - 140

120

Delta BHC

mg/kg

0.1

0.2

0.2

60 - 140

112

Dieldrin

mg/kg

0.05

0.23

0.2

60 - 140

116

Endrin

mg/kg

0.2

0.2

0.2

60 - 140

121

p,p'-DDT

mg/kg

0.1

0.2

0.2

60 - 140

100

Tetrachloro-m-xylene (TCMX) (Surrogate)

mg/kg

-

0.15

0.15

40 - 130

99

PAH (Polynuclear Aromatic Hydrocarbons) in Soil

Sample Number

Parameter

LB062562.002

Surrogates

LB062563.002

27/8/2014

Method: ME-(AU)-[ENV]AN420

Result

Expected

Criteria %

Recovery %

Naphthalene

mg/kg

Units

0.1

LOR

3.7

4

60 - 140

93

Acenaphthylene

mg/kg

0.1

3.8

4

60 - 140

95

Acenaphthene

mg/kg

0.1

4.0

4

60 - 140

99

Phenanthrene

mg/kg

0.1

3.5

4

60 - 140

87

Anthracene

mg/kg

0.1

3.3

4

60 - 140

84

Fluoranthene

mg/kg

0.1

3.6

4

60 - 140

90

Pyrene

mg/kg

0.1

3.6

4

60 - 140

89

Benzo(a)pyrene

mg/kg

0.1

4.0

4

60 - 140

99

d5-nitrobenzene (Surrogate)

mg/kg

-

0.47

0.5

40 - 130

94

2-fluorobiphenyl (Surrogate)

mg/kg

-

0.46

0.5

40 - 130

92

d14-p-terphenyl (Surrogate)

mg/kg

-

0.43

0.5

40 - 130

86

Naphthalene

mg/kg

0.1

3.6

4

60 - 140

90

Acenaphthylene

mg/kg

0.1

3.6

4

60 - 140

89

Acenaphthene

mg/kg

0.1

3.7

4

60 - 140

93

Phenanthrene

mg/kg

0.1

3.7

4

60 - 140

93

Anthracene

mg/kg

0.1

3.5

4

60 - 140

87

Fluoranthene

mg/kg

0.1

4.0

4

60 - 140

100

Pyrene

mg/kg

0.1

3.8

4

60 - 140

94

Benzo(a)pyrene

mg/kg

0.1

3.9

4

60 - 140

98

Page 22 of 29


SE130614 R0

LABORATORY CONTROL SAMPLES

Laboratory Control Standard (LCS) results are evaluated against an expected result, typically the concentration of analyte spiked into the control during the sample preparation stage, producing a percentage recovery. The criteria applied to the percentage recovery is established in the SGS QA /QC plan (Ref: MP-(AU)-[ENV]QU-022). For more information refer to the footnotes in the concluding page of this report. Recovery is shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria.

PAH (Polynuclear Aromatic Hydrocarbons) in Soil (continued)

Sample Number LB062563.002

Parameter Surrogates

Method: ME-(AU)-[ENV]AN420

Units

LOR

Result

Expected

Criteria %

Recovery %

d5-nitrobenzene (Surrogate)

mg/kg

-

0.44

0.5

40 - 130

88

2-fluorobiphenyl (Surrogate)

mg/kg

-

0.43

0.5

40 - 130

86

d14-p-terphenyl (Surrogate)

mg/kg

-

0.44

0.5

40 - 130

88

PCBs in Soil

Method: ME-(AU)-[ENV]AN400/AN420

Sample Number

Result

Expected

Criteria %

Recovery %

LB062562.002

Arochlor 1260

Parameter

mg/kg

Units

0.2

LOR

0.5

0.4

60 - 140

119

LB062563.002

Arochlor 1260

mg/kg

0.2

0.5

0.4

60 - 140

125

Result

Expected

pH in soil (1:5)

Method: ME-(AU)-[ENV]AN101

Sample Number

Parameter

Units

LOR

Criteria %

Recovery %

LB062682.001

pH

pH Units

-

7.4

7.415

98 - 102

100

LB062682.025

pH

pH Units

-

7.4

7.415

98 - 102

100

Result

Expected

Criteria %

Recovery %

0.31

0.325

80 - 120

96

Result

Expected

Criteria %

Recovery %

0.3

0.25

70 - 130

104

Result

Expected

TOC in Soil

Method: ME-(AU)-[ENV]AN188

Sample Number

Parameter

LB062858.002

Total Organic Carbon

Units %w/w

LOR 0.05

Total Cyanide in soil by Discrete Analyser (Aquakem)

Sample Number

Parameter

LB062764.002

Total Cyanide

Method: ME-(AU)-[ENV]AN077/AN287

Units mg/kg

LOR 0.1

Total Phenolics in Soil

Sample Number

Method: ME-(AU)-[ENV]AN289

Parameter

Units

LOR

Criteria %

Recovery %

LB062763.002

Total Phenols

mg/kg

0.1

2.2

2.5

70 - 130

88

LB062835.002

Total Phenols

mg/kg

0.1

2.2

2.5

70 - 130

90

Result

Expected

Total Recoverable Metals in Soil by ICPOES from EPA 200.8 Digest

Sample Number

Parameter

LB062732.002

LB062733.002

Method: ME-(AU)-[ENV]AN040/AN320

Units

LOR

Criteria %

Recovery %

Arsenic, As

mg/kg

3

53

50

80 - 120

105

Cadmium, Cd

mg/kg

0.3

53

50

80 - 120

105

Chromium, Cr

mg/kg

0.3

53

50

80 - 120

105

Copper, Cu

mg/kg

0.5

52

50

80 - 120

103

Lead, Pb

mg/kg

1

53

50

80 - 120

106

Nickel, Ni

mg/kg

0.5

53

50

80 - 120

106

Zinc, Zn

mg/kg

0.5

53

50

80 - 120

107

Arsenic, As

mg/kg

3

52

50

80 - 120

103

Cadmium, Cd

mg/kg

0.3

53

50

80 - 120

105

Chromium, Cr

mg/kg

0.3

52

50

80 - 120

104

Copper, Cu

mg/kg

0.5

52

50

80 - 120

103

Lead, Pb

mg/kg

1

53

50

80 - 120

105

Nickel, Ni

mg/kg

0.5

53

50

80 - 120

105

Zinc, Zn

mg/kg

0.5

53

50

80 - 120

106

TRH (Total Recoverable Hydrocarbons) in Soil

Sample Number

Parameter

LB062562.002

TRH F Bands

LB062563.002

TRH F Bands

27/8/2014

Method: ME-(AU)-[ENV]AN403

Result

Expected

Criteria %

Recovery %

TRH C10-C14

mg/kg

Units

LOR 20

37

40

60 - 140

93

TRH C15-C28

mg/kg

45

<45

40

60 - 140

90

TRH C29-C36

mg/kg

45

<45

40

60 - 140

85

TRH >C10-C16 (F2)

mg/kg

25

37

40

60 - 140

93

TRH >C16-C34 (F3)

mg/kg

90

<90

40

60 - 140

90

TRH >C34-C40 (F4)

mg/kg

120

<120

20

60 - 140

95

TRH C10-C14

mg/kg

20

40

40

60 - 140

100

TRH C15-C28

mg/kg

45

<45

40

60 - 140

98

TRH C29-C36

mg/kg

45

<45

40

60 - 140

78

TRH >C10-C16 (F2)

mg/kg

25

39

40

60 - 140

98

TRH >C16-C34 (F3)

mg/kg

90

<90

40

60 - 140

93

Page 23 of 29


SE130614 R0

LABORATORY CONTROL SAMPLES

Laboratory Control Standard (LCS) results are evaluated against an expected result, typically the concentration of analyte spiked into the control during the sample preparation stage, producing a percentage recovery. The criteria applied to the percentage recovery is established in the SGS QA /QC plan (Ref: MP-(AU)-[ENV]QU-022). For more information refer to the footnotes in the concluding page of this report. Recovery is shown in Green when within suggested criteria or Red with an appended dagger symbol (†) when outside suggested criteria.

TRH (Total Recoverable Hydrocarbons) in Soil (continued)

Sample Number LB062563.002

Parameter TRH F Bands

TRH >C34-C40 (F4)

Method: ME-(AU)-[ENV]AN403

Units mg/kg

LOR 120

Result

Expected

Criteria %

Recovery %

<120

20

60 - 140

75

VOC’s in Soil

Method: ME-(AU)-[ENV]AN433/AN434

Sample Number LB062558.002

Result

Expected

Criteria %

Recovery %

Monocyclic

Benzene

Parameter

mg/kg

0.1

2.1

2.9

60 - 140

73

Aromatic

Toluene

mg/kg

0.1

2.6

2.9

60 - 140

89

Ethylbenzene

mg/kg

0.1

2.4

2.9

60 - 140

83

m/p-xylene

mg/kg

0.2

4.6

5.8

60 - 140

80

o-xylene

mg/kg

0.1

2.4

2.9

60 - 140

82

Dibromofluoromethane (Surrogate)

mg/kg

-

4.5

5

60 - 140

90

d4-1,2-dichloroethane (Surrogate)

mg/kg

-

4.5

5

60 - 140

89

d8-toluene (Surrogate)

mg/kg

-

5.2

5

60 - 140

104

Bromofluorobenzene (Surrogate)

mg/kg

-

5.1

5

60 - 140

102

Surrogates

Units

LOR

Volatile Petroleum Hydrocarbons in Soil

Sample Number

Parameter

LB062558.002 Surrogates

VPH F Bands

27/8/2014

Method: ME-(AU)-[ENV]AN433/AN434/AN410

Result

Expected

Criteria %

Recovery %

TRH C6-C10

mg/kg

Units

LOR 25

<25

24.65

60 - 140

92

TRH C6-C9

mg/kg

20

20

23.2

60 - 140

87

Dibromofluoromethane (Surrogate)

mg/kg

-

4.5

5

60 - 140

90

d4-1,2-dichloroethane (Surrogate)

mg/kg

-

4.5

5

60 - 140

89

d8-toluene (Surrogate)

mg/kg

-

5.2

5

60 - 140

104

Bromofluorobenzene (Surrogate)

mg/kg

-

5.1

5

60 - 140

102

TRH C6-C10 minus BTEX (F1)

mg/kg

25

<25

7.25

60 - 140

119

Page 24 of 29


SE130614 R0

MATRIX SPIKES

Matrix Spike (MS) results are evaluated as the percentage recovery of an expected result, typically the concentration of analyte spiked into a field sub -sample during the sample preparation stage. The original sample's result is subtracted from the sub -sample result before determining the percentage recovery. The criteria applied to the percentage recovery is established in the SGS QA/QC plan (ref: MP-(AU)-[ENV]QU-022). For more information refer to the footnotes in the concluding page of this report. Recovery is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

Mercury (dissolved) in Water

Method: ME-(AU)-[ENV]AN311/AN312

QC Sample

Sample Number

Parameter

Units

LOR

Result

Original

Spike

Recovery%

SE130614.024

LB062755.004

Mercury

mg/L

0.0001

0.0076

0.0002

0.008

93

QC Sample

Sample Number

Parameter

Units

LOR

Result

Original

Spike

Recovery%

SE130590.012

LB062739.004

Mercury

mg/kg

0.01

0.19

<0.01

0.2

92

SE130614.006

LB062741.004

Mercury

mg/kg

0.01

0.21

0.02

0.2

94

Mercury in Soil

Method: ME-(AU)-[ENV]AN312

Metals in Water (Dissolved) by ICPOES

Method: ME-(AU)-[ENV]AN320/AN321

QC Sample

Sample Number

Parameter

Units

LOR

Result

Original

Spike

Recovery%

SE130614.024

LB062600.004

Arsenic, As

mg/L

0.02

2.0

<0.02

2

100

Cadmium, Cd

mg/L

0.001

2.0

<0.001

2

100

Chromium, Cr

mg/L

0.005

2.0

<0.005

2

100

Copper, Cu

mg/L

0.005

2.0

<0.005

2

100

Lead, Pb

mg/L

0.02

2.0

<0.02

2

101

Nickel, Ni

mg/L

0.005

2.0

<0.005

2

101

Zinc, Zn

mg/L

0.01

2.0

<0.01

2

102

OC Pesticides in Soil

Method: ME-(AU)-[ENV]AN400/AN420

QC Sample

Sample Number

Parameter

Units

LOR

Result

Original

Spike

Recovery%

SE130614.012

LB062562.022

Hexachlorobenzene (HCB)

mg/kg

0.1

<0.1

<0.1

-

-

Alpha BHC

mg/kg

0.1

<0.1

<0.1

-

-

Lindane

mg/kg

0.1

<0.1

<0.1

-

-

Heptachlor

mg/kg

0.1

0.3

<0.1

0.2

126

Aldrin

mg/kg

0.1

0.3

<0.1

0.2

128

Beta BHC

mg/kg

0.1

<0.1

<0.1

-

-

Delta BHC

mg/kg

0.1

0.2

<0.1

0.2

119

Heptachlor epoxide

mg/kg

0.1

<0.1

<0.1

-

-

o,p'-DDE

mg/kg

0.1

<0.1

<0.1

-

-

Alpha Endosulfan

mg/kg

0.2

<0.2

<0.2

-

-

Gamma Chlordane

mg/kg

0.1

<0.1

<0.1

-

-

Alpha Chlordane

mg/kg

0.1

<0.1

<0.1

-

-

trans-Nonachlor

mg/kg

0.1

<0.1

<0.1

-

-

p,p'-DDE

mg/kg

0.1

<0.1

<0.1

-

-

Dieldrin

mg/kg

0.05

0.24

<0.05

0.2

122

Endrin

mg/kg

0.2

0.3

<0.2

0.2

127

o,p'-DDD

mg/kg

0.1

<0.1

<0.1

-

-

o,p'-DDT

mg/kg

0.1

<0.1

<0.1

-

-

Beta Endosulfan

mg/kg

0.2

<0.2

<0.2

-

-

p,p'-DDD

mg/kg

0.1

<0.1

<0.1

-

-

p,p'-DDT

mg/kg

0.1

0.2

<0.1

0.2

109

Endosulfan sulphate

mg/kg

0.1

<0.1

<0.1

-

-

Endrin Aldehyde

mg/kg

0.1

<0.1

<0.1

-

-

Methoxychlor

mg/kg

0.1

<0.1

<0.1

-

-

Endrin Ketone

mg/kg

0.1

<0.1

<0.1

-

-

Isodrin

mg/kg

0.1

<0.1

<0.1

-

-

Mirex

mg/kg

0.1

<0.1

<0.1

-

-

Tetrachloro-m-xylene (TCMX) (Surrogate)

mg/kg

-

0.16

0.16

-

106

Surrogates

PAH (Polynuclear Aromatic Hydrocarbons) in Soil

Method: ME-(AU)-[ENV]AN420

QC Sample

Sample Number

Parameter

Units

LOR

Result

Original

Spike

Recovery%

SE130614.001

LB062562.010

Naphthalene

mg/kg

0.1

3.6

<0.1

4

90

2-methylnaphthalene

mg/kg

0.1

<0.1

<0.1

-

-

1-methylnaphthalene

mg/kg

0.1

<0.1

<0.1

-

-

Acenaphthylene

mg/kg

0.1

3.4

<0.1

4

86

Acenaphthene

mg/kg

0.1

3.7

<0.1

4

93

Fluorene

mg/kg

0.1

<0.1

<0.1

-

-

Phenanthrene

mg/kg

0.1

3.6

<0.1

4

91

Anthracene

mg/kg

0.1

3.5

<0.1

4

86

Fluoranthene

mg/kg

0.1

4.4

<0.1

4

111

27/8/2014

Page 25 of 29


SE130614 R0

MATRIX SPIKES

Matrix Spike (MS) results are evaluated as the percentage recovery of an expected result, typically the concentration of analyte spiked into a field sub -sample during the sample preparation stage. The original sample's result is subtracted from the sub -sample result before determining the percentage recovery. The criteria applied to the percentage recovery is established in the SGS QA/QC plan (ref: MP-(AU)-[ENV]QU-022). For more information refer to the footnotes in the concluding page of this report. Recovery is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

PAH (Polynuclear Aromatic Hydrocarbons) in Soil (continued)

Method: ME-(AU)-[ENV]AN420

QC Sample

Sample Number

Parameter

Units

LOR

Result

Original

Spike

Recovery%

SE130614.001

LB062562.010

Pyrene

mg/kg

0.1

3.7

<0.1

4

92

Benzo(a)anthracene

mg/kg

0.1

<0.1

<0.1

-

-

Chrysene

mg/kg

0.1

<0.1

<0.1

-

-

Benzo(b&j)fluoranthene

mg/kg

0.1

<0.1

<0.1

-

-

Benzo(k)fluoranthene

mg/kg

0.1

<0.1

<0.1

-

-

Benzo(b&j&k)fluoranthene

mg/kg

0.2

<0.2

<0.2

-

-

Benzo(a)pyrene

mg/kg

0.1

3.7

<0.1

4

93

Indeno(1,2,3-cd)pyrene

mg/kg

0.1

<0.1

<0.1

-

-

Dibenzo(a&h)anthracene

mg/kg

0.1

<0.1

<0.1

-

-

Benzo(ghi)perylene

mg/kg

0.1

<0.1

<0.1

-

-

Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.2

3.7

<0.2

-

-

<LOR=0* Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.3

3.9

<0.3

-

-

<LOR=LOR* Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.2

3.8

<0.2

-

-

mg/kg

0.8

30

<0.8

-

-

d5-nitrobenzene (Surrogate)

mg/kg

-

0.43

0.43

-

86

2-fluorobiphenyl (Surrogate)

mg/kg

-

0.42

0.42

-

84

d14-p-terphenyl (Surrogate)

mg/kg

-

0.45

0.47

-

90

<LOR=LOR/2* Total PAH Surrogates

TOC in Soil

Method: ME-(AU)-[ENV]AN188

QC Sample

Sample Number

Parameter

Units

LOR

Result

Original

Spike

Recovery%

SE130614.001

LB062858.004

Total Organic Carbon

%w/w

0.05

0.42

0.10

-

-

Total Phenolics in Soil

Method: ME-(AU)-[ENV]AN289

QC Sample

Sample Number

Parameter

Units

LOR

Result

Original

Spike

Recovery%

SE130617.008

LB062835.014

Total Phenols

mg/kg

0.1

2.3

<0.1

2.5

92

Total Recoverable Metals in Soil by ICPOES from EPA 200.8 Digest

Method: ME-(AU)-[ENV]AN040/AN320

QC Sample

Sample Number

Parameter

Units

LOR

Result

Original

Spike

Recovery%

SE130590.012

LB062732.004

Arsenic, As

mg/kg

3

47

<3

50

88

Cadmium, Cd

mg/kg

0.3

46

<0.3

50

92

Chromium, Cr

mg/kg

0.3

58

12

50

92

Copper, Cu

mg/kg

0.5

47

<0.5

50

94

Lead, Pb

mg/kg

1

63

17

50

91

Nickel, Ni

mg/kg

0.5

47

0.8

50

93

Zinc, Zn

mg/kg

0.5

49

1.5

50

94

Arsenic, As

mg/kg

3

52

10

50

85

Cadmium, Cd

mg/kg

0.3

44

0.3

50

88

Chromium, Cr

mg/kg

0.3

60

18

50

85

Copper, Cu

mg/kg

0.5

53

8.5

50

88

Lead, Pb

mg/kg

1

61

22

50

78

Nickel, Ni

mg/kg

0.5

46

1.9

50

89

Zinc, Zn

mg/kg

0.5

60

19

50

83

SE130614.006

LB062733.004

VOC’s in Soil

Method: ME-(AU)-[ENV]AN433/AN434

QC Sample

Sample Number

SE130602.004

LB062558.009

Monocyclic Aromatic

Polycyclic VOCs Surrogates

Totals

27/8/2014

Parameter

Units

LOR

Result

Original

Spike

Recovery%

Benzene

mg/kg

0.1

2.1

<0.1

2.9

73

Toluene

mg/kg

0.1

2.5

<0.1

2.9

87

Ethylbenzene

mg/kg

0.1

2.2

<0.1

2.9

75

m/p-xylene

mg/kg

0.2

4.1

<0.2

5.8

71

o-xylene

mg/kg

0.1

2.2

<0.1

2.9

74

Naphthalene

mg/kg

0.1

<0.1

<1.0

-

-

Dibromofluoromethane (Surrogate)

mg/kg

-

4.7

4.1

5

95

d4-1,2-dichloroethane (Surrogate)

mg/kg

-

4.7

3.9

5

93

d8-toluene (Surrogate)

mg/kg

-

5.2

4.8

5

104

Bromofluorobenzene (Surrogate)

mg/kg

-

4.6

5.2

5

92

Total Xylenes*

mg/kg

0.3

6.3

<0.3

-

-

Total BTEX*

mg/kg

0.6

13

<0.3

-

-

Page 26 of 29


SE130614 R0

MATRIX SPIKES

Matrix Spike (MS) results are evaluated as the percentage recovery of an expected result, typically the concentration of analyte spiked into a field sub -sample during the sample preparation stage. The original sample's result is subtracted from the sub -sample result before determining the percentage recovery. The criteria applied to the percentage recovery is established in the SGS QA/QC plan (ref: MP-(AU)-[ENV]QU-022). For more information refer to the footnotes in the concluding page of this report. Recovery is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

Volatile Petroleum Hydrocarbons in Soil

Method: ME-(AU)-[ENV]AN433/AN434/AN410

QC Sample

Sample Number

Parameter

Units

LOR

Result

Original

Spike

Recovery%

SE130614.004

LB062558.009

TRH C6-C10

mg/kg

25

<25

<25

24.65

86

TRH C6-C9

mg/kg

20

<20

<20

23.2

81

Dibromofluoromethane (Surrogate)

mg/kg

-

4.7

4.5

5

95

d4-1,2-dichloroethane (Surrogate)

mg/kg

-

4.7

4.0

5

93

d8-toluene (Surrogate)

mg/kg

-

5.2

5.5

5

104

Bromofluorobenzene (Surrogate)

mg/kg

-

4.6

5.4

5

92

Benzene (F0)

mg/kg

0.1

2.1

<0.1

-

-

TRH C6-C10 minus BTEX (F1)

mg/kg

25

<25

<25

7.25

112

Surrogates

VPH F Bands

27/8/2014

Page 27 of 29


SE130614 R0

MATRIX SPIKE DUPLICATES

Matrix spike duplicates are calculated as Relative Percent Difference (RPD) using the formula: RPD = | OriginalResult - ReplicateResult | x 100 / Mean The original result is the analyte concentration of the matrix spike. The Duplicate result is the analyte concentration of the matrix spike duplicate. The RPD is evaluated against the Maximum Allowable Difference (MAD) criteria and can be graphically represented by a curve calculated from the Statistical Detection Limit (SDL) and Limiting Repeatability (LR) using the formula: MAD = 100 x SDL / Mean + LR Where the Maximum Allowable Difference evaluates to a number larger than 200 it is displayed as 200. RPD is shown in Green when within suggested criteria or Red with an appended reason identifer when outside suggested criteria. Refer to the footnotes section at the end of this report for failure reasons.

OC Pesticides in Soil

Method: ME-(AU)-[ENV]AN400/AN420

QC Sample

Sample Number

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.012

LB062562.023

Hexachlorobenzene (HCB)

mg/kg

0.1

<0.1

<0.1

200

-

Alpha BHC

mg/kg

0.1

<0.1

<0.1

200

-

Lindane

mg/kg

0.1

<0.1

<0.1

200

-

Heptachlor

mg/kg

0.1

0.3

0.3

69

1

Aldrin

mg/kg

0.1

0.3

0.3

69

2

Beta BHC

mg/kg

0.1

<0.1

<0.1

200

-

Delta BHC

mg/kg

0.1

0.2

0.2

72

3

Heptachlor epoxide

mg/kg

0.1

<0.1

<0.1

200

-

o,p'-DDE

mg/kg

0.1

<0.1

<0.1

200

-

Alpha Endosulfan

mg/kg

0.2

<0.2

<0.2

200

-

Gamma Chlordane

mg/kg

0.1

<0.1

<0.1

200

-

Alpha Chlordane

mg/kg

0.1

<0.1

<0.1

200

-

trans-Nonachlor

mg/kg

0.1

<0.1

<0.1

200

-

p,p'-DDE

mg/kg

0.1

<0.1

<0.1

200

-

Dieldrin

mg/kg

0.05

0.24

0.25

71

1

Endrin

mg/kg

0.2

0.3

0.3

69

2

o,p'-DDD

mg/kg

0.1

<0.1

<0.1

200

-

o,p'-DDT

mg/kg

0.1

<0.1

<0.1

200

-

Beta Endosulfan

mg/kg

0.2

<0.2

<0.2

200

-

p,p'-DDD

mg/kg

0.1

<0.1

<0.1

200

-

p,p'-DDT

mg/kg

0.1

0.2

0.2

76

0

Endosulfan sulphate

mg/kg

0.1

<0.1

<0.1

200

-

Endrin Aldehyde

mg/kg

0.1

<0.1

<0.1

200

-

Methoxychlor

mg/kg

0.1

<0.1

<0.1

200

-

Endrin Ketone

mg/kg

0.1

<0.1

<0.1

200

-

Isodrin

mg/kg

0.1

<0.1

<0.1

200

-

Mirex

mg/kg

0.1

<0.1

<0.1

200

-

Tetrachloro-m-xylene (TCMX) (Surrogate)

mg/kg

-

0.16

0.16

30

1

Surrogates

PAH (Polynuclear Aromatic Hydrocarbons) in Soil

Method: ME-(AU)-[ENV]AN420

QC Sample

Sample Number

Parameter

Units

LOR

Original

Duplicate

Criteria %

RPD %

SE130614.001

LB062562.011

Naphthalene

mg/kg

0.1

3.6

3.7

33

2

2-methylnaphthalene

mg/kg

0.1

<0.1

<0.1

200

-

1-methylnaphthalene

mg/kg

0.1

<0.1

<0.1

200

-

Acenaphthylene

mg/kg

0.1

3.4

3.7

33

7

Acenaphthene

mg/kg

0.1

3.7

3.8

33

2

Fluorene

mg/kg

0.1

<0.1

<0.1

200

-

Phenanthrene

mg/kg

0.1

3.6

3.7

33

2

Anthracene

mg/kg

0.1

3.5

3.5

33

2

Fluoranthene

mg/kg

0.1

4.4

4.3

32

2

Pyrene

mg/kg

0.1

3.7

3.8

33

5

Benzo(a)anthracene

mg/kg

0.1

<0.1

<0.1

200

-

Chrysene

mg/kg

0.1

<0.1

<0.1

200

-

Benzo(b&j)fluoranthene

mg/kg

0.1

<0.1

<0.1

200

-

Benzo(k)fluoranthene

mg/kg

0.1

<0.1

<0.1

200

-

Benzo(b&j&k)fluoranthene

mg/kg

0.2

<0.2

<0.2

200

-

Benzo(a)pyrene

mg/kg

0.1

3.7

3.8

33

3

Indeno(1,2,3-cd)pyrene

mg/kg

0.1

<0.1

<0.1

200

-

Dibenzo(a&h)anthracene

mg/kg

0.1

<0.1

<0.1

200

-

Benzo(ghi)perylene

mg/kg

0.1

<0.1

<0.1

200

-

Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.2

3.7

3.8

15

-

<LOR=0* Carcinogenic PAHs (as BaP TEQ)-assume results

TEQ (mg/kg)

0.3

3.9

4.0

18

-

<LOR=LOR* PAHs (as BaP TEQ)-assume results Carcinogenic

TEQ (mg/kg)

0.2

3.8

3.9

15

-

<LOR=LOR/2* Total PAH

mg/kg

0.8

30

30

33

-

d5-nitrobenzene (Surrogate)

mg/kg

-

0.43

0.44

30

2

2-fluorobiphenyl (Surrogate)

mg/kg

-

0.42

0.43

30

2

d14-p-terphenyl (Surrogate)

mg/kg

-

0.45

0.46

30

2

Surrogates

27/8/2014

Page 28 of 29


FOOTNOTES

SE130614 R0

Samples analysed as received. Solid samples expressed on a dry weight basis. QC criteria are subject to internal review according to the SGS QA/QC plan and may be provided on request or alternatively can be found here: http://www.sgs.com.au/~/media/Local/Australia/Documents/Technical%20Documents/MP-AU-ENV-QU-022%20QA%20QC%20Plan.pdf

* ^ IS LNR LOR QFH QFL

Non-accredited analysis. Sample not analysed for this analyte. Analysis performed by external laboratory. Insufficient sample for analysis. Sample listed, but not received. Limit of reporting. QC result is above the upper tolerance. QC result is below the lower tolerance.

At least 2 of 3 surrogates are within acceptance criteria.

RPD failed acceptance criteria due to sample heterogeneity.

Results less than 5 times LOR preclude acceptance criteria for RPD.

Recovery failed acceptance criteria due to matrix interference.

⑤ ⑥

Recovery failed acceptance criteria due to the presence of significant concentration of analyte (i.e. the concentration of analyte exceeds the spike level). LOR was raised due to sample matrix interference.

LOR was raised due to dilution of significantly high concentration of analyte in sample.

Reanalysis of sample in duplicate confirmed sample heterogeneity and inconsistency of results.

Recovery failed acceptance criteria due to sample heterogeneity.

LOR was raised due to high conductivity of the sample (required dilution).

Refer to Analytical Report comments for further information.

This document is issued, on the Client's behalf, by the Company under its General Conditions of Service, available on request and accessible at http://www.sgs.com/en/Terms-and-Conditions/General-Conditions-of-Services-English.aspx . The Client's attention is drawn to the limitation of liability, indemnification and jurisdiction issues defined therein. Any other holder of this document is advised that information contained herein reflects the Company's findings at the time of its intervention only and within the limits of Client's instructions, if any. The Company's sole responsibility is to its Client and this document does not exonerate parties to a transaction from exercising all their rights and obligations under the transaction documents. This test report shall not be reproduced, except in full.

27/8/2014

Page 29 of 29


ANALYTICAL REPORT

LABORATORY DETAILS

CLIENT DETAILS

Contact

An Nguyen

Manager

Huong Crawford

Client

Geotechnique

Laboratory

SGS Alexandria Environmental

Address

P.O. Box 880 NSW 2751

Address

Unit 16, 33 Maddox St Alexandria NSW 2015

Telephone

02 4722 2700

Telephone

+61 2 8594 0400

Facsimile

02 4722 6161

Facsimile

+61 2 8594 0499

Email

anguyen@geotech.com.au

Email

au.environmental.sydney@sgs.com

Project

13188-2 - Concord

SGS Reference

Order Number

(Not specified)

Report Number

SE130614 R0 0000089956

Samples

28

Date Reported Date Received

26 Aug 2014 18 Aug 2014

COMMENTS

Accredited for compliance with ISO/IEC 17025. NATA accredited laboratory 2562(4354).

Sample # 11:portion of the sample supplied has been sub-sampled for asbestos according to SGS In-house procedures. We therefore cannot guarantee that the sub-sample is representative of the entire sample supplied. SGS Environmental Services recommends supplying approximately 50-100g of sample in a separate container. No respirable fibres detected in all samples using trace analysis technique. Asbestos analysed by Approved Identifier Yusuf Kuthpudin.

SIGNATORIES

Andy Sutton Senior Organic Chemist

Dong Liang Metals/Inorganics Team Leader

Huong Crawford Production Manager

Jaimie Cheung Metals Chemist

Ly Kim Ha Organic Section Head

Sheila Lepasana Senior Technician

SGS Australia Pty Ltd ABN 44 000 964 278

Environmental Services

Unit 16 33 Maddox St PO Box 6432 Bourke Rd BC

Alexandria NSW 2015 Alexandria NSW 2015

Australia Australia

t +61 2 8594 0400

f +61 2 8594 0499

www.au.sgs.com

Member of the SGS Group

26/08/2014

Page 1 of 3


SE130614 R0

ANALYTICAL REPORT

RESULTS

Method

Fibre Identification in soil Laboratory Reference

Client Reference

Matrix

SE130614.001

BH1 1.5-1.8

Soil

SE130614.003

BH2 0-0.15

SE130614.004

Sample Description

AN602

Date Sampled

Fibre Identification

56 g Clay

07 Aug 2014

No Asbestos Found

<0.01

Soil

80 g Clay,sand,soil,r ocks

11 Aug 2014

No Asbestos Found Organic Fibres Detected

<0.01

BH2 0.5-0.8

Soil

182 g Clay,sand,soil,r ocks

11 Aug 2014

No Asbestos Found

<0.01

SE130614.005

BH2 4.5-4.8

Soil

180 g Clay,sand,soil,r ocks

11 Aug 2014

No Asbestos Found Organic Fibres Detected

<0.01

SE130614.007

BH3 0-0.1

Soil

81 g Sand,soil,rocks

12 Aug 2014

No Asbestos Found Organic Fibres Detected

<0.01

SE130614.008

BH3 1.5-1.8

Soil

142 g Clay,sand,soil

12 Aug 2014

No Asbestos Found Organic Fibres Detected

<0.01

SE130614.009

BH4 0-0.15

Soil

102 g Clay,sand,soil,r ocks

12 Aug 2014

No Asbestos Found Organic Fibres Detected

<0.01

SE130614.010

BH5 0.1-0.4

Soil

145 g Clay,soil,rocks

13 Aug 2014

No Asbestos Found Organic Fibres Detected

<0.01

SE130614.011

BH5 0.6-0.7

Soil

104 g Clay,sand,soil

13 Aug 2014

No Asbestos Found

<0.01

SE130614.013

BH7 0.15-0.45

Soil

120 g Sand,soil,rocks

11 Aug 2014

No Asbestos Found

<0.01

SE130614.014

BH7 1.4-1.7

Soil

125 g Clay,sand,rocks

11 Aug 2014

No Asbestos Found

<0.01

SE130614.016

BH9 0.2-0.5

Soil

148 g Clay,soil,rocks

14 Aug 2014

No Asbestos Found

<0.01

SE130614.017

BH9 2.0-2.3

Soil

132 g Clay,soil,rocks

14 Aug 2014

No Asbestos Found

<0.01

SE130614.019

BH10 0.23-0.5

Soil

88 g Clay,soil

12 Aug 2014

No Asbestos Found

<0.01

26/08/2014

Est.%w/w

Page 2 of 3


SE130614 R0

METHOD SUMMARY

METHOD

METHODOLOGY SUMMARY

AN602

Qualitative identification of chrysotile, amosite and crocidolite in bulk samples by polarised light microscopy (PLM) in conjunction with dispersion staining (DS). AS4964 provides the basis for this document. Unequivocal identification of the asbestos minerals present is made by obtaining sufficient diagnostic `clues`, which provide a reasonable degree of certainty, dispersion staining is a mandatory `clue` for positive identification. If sufficient `clues` are absent, then positive identification of asbestos is not possible. This procedure requires removal of suspect fibres/bundles from the sample which cannot be returned.

AN602

Fibres/material that cannot be unequivocably identified as one of the three asbestos forms, will be reported as unknown mineral fibres (umf).

AN602

AS4964.2004 Method for the Qualitative Identification of Asbestos in Bulk Samples, Section 8.4, Trace Analysis Criteria, Note 4 states:"Depending upon sample condition and fibre type, the detection limit of this technique has been found to lie generally in the range of 1 in 1,000 to 1 in 10,000 parts by weight, equivalent to 1 to 0.1 g/kg."

FOOTNOTES

Amosite Chrysotile Crocidolite Amphiboles

-

Brown Asbestos White Asbestos Blue Asbestos Amosite and/or Crocidolite

NA LNR * **

-

Not Analysed Listed, Not Required Not Accredited Indicative data, theoretical holding time exceeded.

This report does not comply with the analytical reporting recommendations in the Western Australian Department of Health Guidelines for the Assessment and Remediation and Management of Asbestos Contaminated sites in Western Australia - May 2009. Sampled by the client. Where reported: 'Asbestos Detected': Asbestos detected by polarized light microscopy, including dispersion staining. Where reported: 'No Asbestos Found': No Asbestos Found by polarized light microscopy, including dispersion staining. Where reported: 'UMF Detected': Mineral fibres of unknown type detected by polarized light microscopy, including dispersion staining. by another independent analytical technique may be necessary.

Confirmation

Even after disintegration it can be very difficult, or impossible, to detect the presence of asbestos in some asbestos -containing bulk materials using polarised light microscopy. This is due to the low grade or small length or diameter of asbestos fibres present in the material, or to the fact that very fine fibres have been distributed intimately throughout the materials. The QC criteria are subject to internal review according to the SGS QAQC plan and may be provided on request or alternatively can be found here : http://www.sgs.com.au/~/media/Local/Australia/Documents/Technical%20Documents/MP-AU-ENV-QU-022%20QA%20QC%20Plan.pdf This document is issued, on the Client's behalf, by the Company under its General Conditions of Service available on request and accessible at http://www.sgs.com/en/Terms-and-Conditions/General-Conditions-of-Services-English.aspx . The Client's attention is drawn to the limitation of liability, indemnification and jurisdiction issues defined therein. Any other holder of this document is advised that information contained hereon reflects the Company's findings at the time of its intervention only and within the limits of Client's instructions, if any. The Company's sole responsibility is to its Client and this document does not exonerate parties to a transaction from exercising all their rights and obligations under the transaction documents. This test report shall not be reproduced, except in full.

26/08/2014

Page 3 of 3






SE130614

SAMPLE RECEIPT ADVICE

CLIENT DETAILS

LABORATORY DETAILS

Contact

An Nguyen

Manager

Huong Crawford

Client

Geotechnique

Laboratory

SGS Alexandria Environmental

Address

P.O. Box 880 NSW 2751

Address

Unit 16, 33 Maddox St Alexandria NSW 2015

Telephone

02 4722 2700

Telephone

+61 2 8594 0400

Facsimile

02 4722 6161

Facsimile

+61 2 8594 0499

Email

anguyen@geotech.com.au

Email

au.environmental.sydney@sgs.com

Project

13188-2 - Concord

Samples Received

Mon 18/8/2014

Order Number

(Not specified)

Report Due

Mon 25/8/2014

Samples

28

SGS Reference

SE130614

SUBMISSION DETAILS

This is to confirm that 28 samples were received on Monday 18/8/2014. Results are expected to be ready by Monday 25/8/2014. Please quote SGS reference SE130614 when making enquiries. Refer below for details relating to sample integrity upon receipt. Sample counts by matrix Date documentation received Samples received without headspace Sample container provider Samples received in correct containers Sample cooling method Complete documentation received

21 Soils, 5 Waters 18/08/2014@02:31pm Yes SGS Yes Ice Bricks Yes

Type of documentation received Samples received in good order Sample temperature upon receipt Turnaround time requested Sufficient sample for analysis Samples clearly labelled

COC Yes 4.5°C Standard Yes Yes

Samples will be held for one month for water samples and two months for soil samples from date of report, unless otherwise instructed. COMMENTS

A separate homogenised portion (~100g) was not supplied for Asbestos analysis on sample "BH5 0.6-0.7". SGS will proceed by sub-sampling a portion from the glass jar supplied, on the provision that a comment will be reflected on the final report regarding this sub-sampling. 12 soil samples, which were not marked for analyses on the COC, have been placed on hold. These samples will not be processed.

To the extent not inconsistent with the other provisions of this document and unless specifically agreed otherwise in writing by SGS, all SGS services are rendered in accordance with the applicable SGS General Conditions of Service accessible at http://www.sgs.com/en/Terms-and-Conditions/General-Conditions-of-Services-English.aspx as at the date of this document. Attention is drawn to the limitations of liability and to the clauses of indemnification.

SGS Australia Pty Ltd ABN 44 000 964 278

Environmental Services

Unit 16 33 Maddox St PO Box 6432 Bourke Rd BC

Alexandria NSW 2015 Alexandria NSW 2015

Australia Australia

t +61 2 8594 0400

f +61 2 8594 0499

www.au.sgs.com

Member of the SGS Group


SE130614

SAMPLE RECEIPT ADVICE

CLIENT DETAILS

Client

Geotechnique

Project

13188-2 - Concord

Volatile Petroleum Hydrocarbons in Soil

VOC’s in Soil

TRH (Total Recoverable Hydrocarbons) in Soil

Total Phenolics in Soil

Total Cyanide in soil by Discrete Analyser

PCBs in Soil

OC Pesticides in Soil

PAH (Polynuclear Aromatic Hydrocarbons) in

SUMMARY OF ANALYSIS

No.

Sample ID

001

BH1 1.5-1.8

28

26

-

-

-

-

-

-

002

BH1 3.15-3.25

28

26

-

-

-

-

-

-

003

BH2 0-0.15

28

26

-

-

-

-

-

-

004

BH2 0.5-0.8

28

26

11

1

1

10

12

8

005

BH2 4.5-4.8

28

26

11

1

1

10

12

8

006

BH2 5.1-5.25

28

26

11

1

1

10

12

8

007

BH3 0-0.1

28

26

-

-

-

-

-

-

008

BH3 1.5-1.8

28

26

11

1

1

10

12

8

009

BH4 0-0.15

28

26

-

-

-

-

-

-

010

BH5 0.1-0.4

28

26

11

1

1

10

12

8

011

BH5 0.6-0.7

28

26

11

1

1

10

12

8

012

BH6 0.6-0.7

28

26

-

-

-

-

-

-

013

BH7 0.15-0.45

28

26

-

-

-

-

-

-

014

BH7 1.4-1.7

28

26

-

-

-

-

-

-

015

BH8 0.2-0.4

28

26

-

-

-

-

-

-

016

BH9 0.2-0.5

28

26

11

1

1

10

12

8

017

BH9 2.0-2.3

28

26

11

1

1

10

12

8

018

BH9 2.55-2.65

28

26

11

1

1

10

12

8

019

BH10 0.23-0.5

28

26

11

1

1

10

12

8

020

BH10 0.55-0.65

28

26

11

1

1

10

12

8

021

Duplicate D2

28

26

11

1

1

10

12

8

022

Trip Spike TS1

-

-

-

-

-

-

12

-

023

Trip Spike TS2

-

-

-

-

-

-

12

-

CONTINUED OVERLEAF The above table represents SGS Environmental Services' interpretation of the client-supplied Chain Of Custody document. The numbers shown in the table indicate the number of results requested in each package. Please indicate as soon as possible should your request differ from these details. Testing as per this table shall commence immediately unless the client intervenes with a correction. 19/08/2014

Page 2 of 6


SE130614

SAMPLE RECEIPT ADVICE

CLIENT DETAILS

Client

Geotechnique

Project

13188-2 - Concord

13

2

1

-

1

1

1

7

002

BH1 3.15-3.25

13

-

1

-

1

1

1

7

003

BH2 0-0.15

13

2

1

-

1

1

1

7

004

BH2 0.5-0.8

13

2

1

-

1

1

1

7

005

BH2 4.5-4.8

13

2

1

-

1

1

1

7

006

BH2 5.1-5.25

13

-

1

-

1

1

1

7

007

BH3 0-0.1

13

2

1

-

1

1

1

7

008

BH3 1.5-1.8

13

2

1

-

1

1

1

7

009

BH4 0-0.15

13

2

1

-

1

1

1

7

010

BH5 0.1-0.4

13

2

1

-

1

1

1

7

011

BH5 0.6-0.7

13

2

1

-

1

1

1

7

012

BH6 0.6-0.7

13

-

1

-

1

1

1

7

013

BH7 0.15-0.45

13

2

1

-

1

1

1

7

014

BH7 1.4-1.7

13

2

1

-

1

1

1

7

015

BH8 0.2-0.4

-

-

1

-

1

1

-

7

016

BH9 0.2-0.5

13

2

1

-

1

1

1

7

017

BH9 2.0-2.3

13

2

1

-

1

1

1

7

018

BH9 2.55-2.65

13

-

1

-

1

1

1

7

019

BH10 0.23-0.5

13

2

1

-

1

1

1

7

020

BH10 0.55-0.65

13

-

1

-

1

1

1

7

021

Duplicate D2

-

-

1

-

1

1

-

7

024

Rinsate R1

-

-

-

7

-

-

-

-

TOC in Soil

pH in soil (1:5)

Mercury in Soil

Total Recoverable Metals in Soil by ICPOES from

BH1 1.5-1.8

Moisture Content

001

Metals in Water (Dissolved) by ICPOES

Sample ID

Fibre Identification in soil

No.

Exchangeable Cations and Cation Exchange Capacity

SUMMARY OF ANALYSIS

CONTINUED OVERLEAF The above table represents SGS Environmental Services' interpretation of the client-supplied Chain Of Custody document. The numbers shown in the table indicate the number of results requested in each package. Please indicate as soon as possible should your request differ from these details. Testing as per this table shall commence immediately unless the client intervenes with a correction. 19/08/2014

Page 3 of 6


SAMPLE RECEIPT ADVICE

SE130614

CLIENT DETAILS

Client

Geotechnique

Project

13188-2 - Concord

No.

Sample ID

Metals in Water (Dissolved) by ICPOES

SUMMARY OF ANALYSIS

025

Rinsate R2

7

026

Rinsate R3

7

027

Rinsate R4

7

028

Rinsate R5

7

CONTINUED OVERLEAF The above table represents SGS Environmental Services' interpretation of the client-supplied Chain Of Custody document. The numbers shown in the table indicate the number of results requested in each package. Please indicate as soon as possible should your request differ from these details. Testing as per this table shall commence immediately unless the client intervenes with a correction. 19/08/2014

Page 4 of 6


SAMPLE RECEIPT ADVICE

SE130614

CLIENT DETAILS

Client

Geotechnique

Project

13188-2 - Concord

No.

Sample ID

Mercury (dissolved) in Water

SUMMARY OF ANALYSIS

024

Rinsate R1

1

CONTINUED OVERLEAF The above table represents SGS Environmental Services' interpretation of the client-supplied Chain Of Custody document. The numbers shown in the table indicate the number of results requested in each package. Please indicate as soon as possible should your request differ from these details. Testing as per this table shall commence immediately unless the client intervenes with a correction. 19/08/2014

Page 5 of 6


SAMPLE RECEIPT ADVICE

SE130614

CLIENT DETAILS

Client

Geotechnique

Project

13188-2 - Concord

No.

Sample ID

Mercury (dissolved) in Water

SUMMARY OF ANALYSIS

025

Rinsate R2

1

026

Rinsate R3

1

027

Rinsate R4

1

028

Rinsate R5

1

The above table represents SGS Environmental Services' interpretation of the client-supplied Chain Of Custody document. The numbers shown in the table indicate the number of results requested in each package. Please indicate as soon as possible should your request differ from these details. Testing as per this table shall commence immediately unless the client intervenes with a correction. 19/08/2014

Page 6 of 6


APPENDIX D

ENVIRONMENTAL NOTES


G EOTECHNIQUE PTY LTD

IMPORTANT INFORMATION REGARDING YOUR ENVIRONMENTAL SITE ASSESSMENT

These notes have been prepared by Geotechnique Pty Ltd, using guidelines prepared by the ASFE (Associated Soil and Foundation Engineers). The notes are offered to assist in the interpretation of your environmental site assessment report. REASONS FOR AN ENVIRONMENTAL ASSESSMENT

Environmental site assessments are typically, though not exclusively, performed in the following circumstances: As a pre-acquisition assessment on behalf of a purchaser or a vendor, when a property is to be sold As a pre-development assessment, when a property or area of land is to be redeveloped, or the land use has changed, e.g. from a factory to a residential subdivision As a pre-development assessment of greenfield sites, to establish baseline conditions and assess environmental, geological and hydrological constraints to the development of e.g. a landfill As an audit of the environmental effects of previous and present site usage Each circumstance requires a specific approach to assessment of soil and groundwater contamination. In all cases the objective is to identify and if possible quantify the risks that unrecognised contamination poses to the ongoing proposed activity. Such risks may be financial (clean-up costs or limitations in site use) and physical (health risks to site users or the public). ENVIRONMENTAL SITE ASSESSMENT LIMITATIONS

Although information provided by an environmental site assessment can reduce exposure to the risk of the presence of contamination, no environmental site assessment can eliminate the risk. Even a rigorous professional assessment might not detect all contamination within a site. Contaminants could be present in areas that were not surveyed or sampled, or migrate to areas that did not show signs of contamination when sampled. Contaminant analysis cannot possibly cover every type of contaminant that may occur; only the most likely contaminants are screened. AN ENVIRONMENTAL SITE ASSESSMENT REPORT IS BASED ON A UNIQUE SET OF PROJECT SPECIFIC FACTORS

In the following events and in order to avoid cost problems, you should ask your consultant to assess any changes in the conclusion and recommendations made in the assessment: When the nature of the proposed development is changed e.g. if a residential development is proposed, rather than a commercial development When the size or configuration of the proposed development is altered e.g. if a basement is added When the location or orientation of the proposed structure is modified When there is a change of land ownership, or For application to an adjacent site ENVIRONMENTAL SITE ASSESSMENT FINDINGS ARE PROFESSIONAL ESTIMATES

Site assessment identifies actual sub-surface conditions only at those points where samples are taken, when they are taken. Data obtained from the sampling and subsequent laboratory analyses are interpreted by geologists, engineers or scientists and opinions are drawn about the overall sub-surface conditions, the nature and extent of contamination, the likely impact on any proposed development and appropriate remediation measures. Actual conditions may differ from those inferred, because no professional, no matter how qualified and no sub-surface exploration program, no matter how comprehensive, can reveal what is hidden by earth, rock and time. The actual interface between materials may be far more gradual or abrupt than an assessment indicates. Actual conditions in areas not sampled may differ from predictions. Nothing can be done to prevent the unanticipated, however, steps can be taken to help minimise the impact. For this reason site owners should retain the services of their consultants throughout the development stages of the project in order to identify variances, conduct additional tests that may be necessary and to recommend solutions to problems encountered on site. Soil and groundwater contamination is a field in which legislation and interpretation of legislation by government departments is changing rapidly. Whilst every attempt is made by Geotechnique Pty Ltd to be familiar with current policy, our interpretation of the investigation findings should not be taken to be that of the relevant authority. When approval from a statutory authority is required for a project, approval should be directly sought. Environotes-Ed3-04/06


G EOTECHNIQUE

PTY LTD ii

Environmental Notes continued

STABILITY OF SUB-SURFACE CONDITIONS

Sub-surface conditions can change by natural processes and site activities. As an environmental site assessment is based on conditions existing at the time of the investigation, project decisions should not be based on environmental site assessment data that may have been affected by time. The consultant should be requested to advise if additional tests are required. ENVIRONMENTAL SITE ASSESSMENTS ARE PERFORMED FOR SPECIFIC PURPOSES AND CLIENTS

Environmental site assessments are prepared in response to a specific scope of work required to meet the specific needs of specific individuals e.g. an assessment prepared for a consulting civil engineer may not be adequate to a construction contractor or another consulting civil engineer. An assessment should not be used by other persons for any purpose or by the client for a different purpose. No individual, other than the client, should apply an assessment, even for its intended purpose, without first conferring with the consultant. No person should apply an assessment for any purpose other than that originally contemplated, without first conferring with the consultant. MISINTERPRETATION OF ENVIRONMENTAL SITE ASSESSMENTS

Costly problems can occur when design professionals develop plans based on misinterpretation of an environmental site assessment. In order to minimise problems, the environmental consultant should be retained to work with appropriate design professionals, to explain relevant findings and to review the adequacy of plans and specifications relative to contamination issues. LOGS SHOULD NOT BE SEPARATED FROM THE REPORT

Borehole and test pit logs are prepared by environmental scientists, engineers or geologists, based upon interpretation of field conditions and laboratory evaluation of field samples. Logs are normally provided in our reports and these would not be redrawn for inclusion in site remediation or other design drawings, as subtle but significant drafting errors or omissions may occur in the transfer process. Photographic reproduction can eliminate this problem, however, contractors can still misinterpret the logs during bid preparation if separated from the text of the assessment. Should this occur, delays and disputes, or unanticipated costs may result. To reduce the likelihood of borehole and test pit log misinterpretation, the complete assessment should be available to persons or organisations involved in the project, such as contractors, for their use. Denial of such access and disclaiming responsibility for the accuracy of sub-surface information does not insulate an owner from the attendant liability. It is critical that the site owner provides all available site information to persons and organisations, such as contractors. READ RESPONSIBILITY CLAUSES CLOSELY

An environmental site assessment is based extensively on judgement and opinion; therefore, it is necessarily less exact than other disciplines. This situation has resulted in wholly unwarranted claims being lodged against consultants. In order to aid in prevention of this problem, model clauses have been developed for use in written transmittals. These are definitive clauses, designed to indicate consultant responsibility. Their use helps all parties involved recognise individual responsibilities and formulate appropriate action. Some of these definitive clauses are likely to appear in the environmental site assessment and you are encouraged to read them closely. Your consultant will be happy to give full and frank answers to any questions you may have.

Environotes-Ed3-04/06


APPENDIX G

2015 REPORT 13188/4-AA


G

EOTECHNIQUE

Job No: 13188/4 Our Ref: 13188/4-AA 3 August 2015

®

PTY LTD ABN 64 002 841 063

Nix Anderson Pty Ltd 17 Chuter Street MCMAHONS POINT NSW 2060 Email: robert.mcguinness@nxa.com.au

Attention: Mr R McGuinness Dear Sir re:

Proposed Redevelopment 160 Burwood Road, Concord Additional Contamination Assessment

Further to the contamination assessment report (Report 13188/1-AA dated 12 September 2014); this letter report presents the results of an additional contamination assessment (ACA) at locations (BH11 to BH16) as indicated on the Drawing No 13188/3-AA1. Field sampling was carried out in conjunction with additional geotechnical investigation. The additional geotechnical investigation report is being submitted separately. The investigation was commissioned by Mr R Ewing of Propertylink Holdings Pty Ltd through a subcontract agreement and was carried out in general accordance with Geotechnique Pty Ltd proposal Q6614-AC dated 12 June 2015. Proposed Development

We understand that Nix Anderson has been retained by Propertylink to assist in carrying out feasibility review of the above site to assess the development potential on behalf of the site owners – Freshfood Australia Holdings Pty Ltd. It is also understood that the existing Robert Timms Factory (Bushell’s) will be relocated prior to development and the site will be developed as an Urban Regeneration Project – an integrated Residential Community. As requested, assessment of soils in the area between the pathway and the seawall was conducted with recovery and analysis of soil samples from additional boreholes (BH11 to BH16) as nominated by the client. The objective of the assessment was to ascertain whether the soils being assessed are likely to present a risk of harm to human health and the environment under the conditions for the proposed residential development. SCOPE OF WORK

In order to achieve the objective of this report, the following scope of work was carried out: 

Site inspection.

Additional soil sampling by a Geotechnical/Environmental Engineer from Geotechnique in conjunction with geotechnical investigation.

Lemko Place, Penrith NSW 2750 PO Box 880, Penrith NSW 2751 Telephone (02) 4722 2700 Facsimile (02) 4722 2777 e-mail: info@geotech.com.au www.geotech.com.au


G EOTECHNIQUE PTY LTD

2 13188/4-AA 160 Burwood Road, Concord

Chemical analysis by laboratories accredited by the National Association of Testing Authorities (NATA), in accordance with Chains of Custody (COC) prepared by Geotechnique.

Assessment of field and laboratory Quality Assurance (QA) and Quality Control (QC).

Assessment of the laboratory analytical results.

Assessment of soil at the sampled borehole locations.

Regional Geology and Landscape

Reference to the Geological Map of Sydney (Herbert 1983) indicates that the bedrock at the site is likely to be Hawkesbury Sandstone, comprising medium grained quartz sandstone. Reference to the Soil Landscape Map of Sydney (Chapman et al., 2004) indicates that the landscape at the site belongs to the Gymea Group, which is characterised by undulating to rolling rises and low hills on Hawkesbury Sandstone. However, the site is likely to have been filled in the past to raise levels for development. FIELD SAMPLING AND LABORATORY TESTING

An Environmental Engineer from Geotechnique was responsible for sampling and logging the sub-surface profile encountered during the field work on 9, 10 and 13 July 2015. Reference should be made to the engineering borehole logs in Attachment A for detailed descriptions of the soil profile encountered during the field work. Generally, the samples did not have obvious asbestos sheets/pieces, odour, staining or discolouration that would indicate the potential for contamination. The sampled borehole locations are indicated on the attached Drawing No 13188/3-AA1. To prevent the potential loss of any volatile compounds, the recovered soil sample for laboratory analysis was immediately transferred into a labelled, laboratory supplied, 250ml glass jar and sealed with an airtight, Teflon screw top lid. The fully filled jar was then placed in a chilled container. Samples were recovered using one-off nitrile gloves in order to avoid cross contamination between the sampling locations. In order to ensure the analytical performance of the primary laboratory, duplicate and split samples were prepared and kept in labelled, laboratory supplied, glass jars (acid-washed and solvent-rinsed) sealed with airtight, Teflon screw top lids. The fully filled jars were placed in a chilled container. The recovered fill sample for asbestos analysis was transferred into a small labelled, plastic bags. The small plastic bags were placed inside a large plastic bag. At completion of field sampling the chilled container was transported to our Penrith office. All the jars and bottle were then transferred to a refrigerator where the temperature was maintained below 4°C. The chilled container with recovered samples was forwarded under Chain of Custody (COC) conditions to the primary laboratory SGS Environmental Services (SGS) and the secondary laboratory, Envirolab Services Pty Ltd (Envirolab), both NATA accredited. On receipt of the samples the laboratories returned the Sample Receipt Advice verifying the integrity of all samples received.

Nix Anderson Pty Ltd DS.sf/03.08.2015


G EOTECHNIQUE PTY LTD

3 13188/4-AA 160 Burwood Road, Concord

Within the holding times detailed in Schedule B(3) of The National Environment Protection (Assessment of Site Contamination) Measure (NEPM) 1999 (April 2013) by the National Environment Protection Council (NEPC), the recovered soil samples were analysed for the following potential contaminants of concern: 

Metals, including, arsenic (As), cadmium (Cd), chromium (Cr), copper (Cu), lead (Pb), mercury (Hg), nickel (Ni) and zinc (Zn).

Total Recoverable Hydrocarbons (TRH).

Benzene, Toluene, Ethyl Benzene and Xylenes (BTEX).

Organochlorine Pesticides (OCP).

Polycyclic Aromatic Hydrocarbons (PAH).

Polychlorinated Biphenyls (PCB).

Cyanides.

Phenols.

Asbestos.

FIELD QUALITY ASSURANCE & QUALITY CONTROL (QA & QC)

The following QA/QC procedures were implemented for the sampling and analytical program. Trip Spike Sample Trip spike samples are obtained from the laboratory on a regular basis, prior to conducting field sampling where volatile substances are suspected. The samples are held at Geotechnique in the Penrith office, at less than 4 degrees Celsius, for a period of not more than seven days. During the fieldwork, the trip spike samples are kept in the chilled container with soil samples recovered from the site. The trip spike sample is then forwarded to the primary laboratory together with the soil samples recovered from the site. The trip spike is prepared by the laboratory by adding a known amount of a pure petrol standard to a clean sand sample. The sample is mixed thoroughly to ensure a relatively homogenous distribution of the spike throughout the sample. When the sample is submitted for analysis, the same procedure is adopted for testing as the soil samples being analysed from the site. The purpose of the trip spike is to detect any loss or potential loss of volatiles from the soil samples, during field work, transportation, sample extraction or testing. A trip spike sample (TS1) was forwarded to the primary analytical laboratory with the samples collected from the site and tested for BTEX. The test results for the trip spike sample, reported as a percentage recovery of the applied and known spike concentrations, are shown in Table A. As indicated in Table A, the results show a generally good recovery (ranging from 99% to 107%) of the spike concentrations. Based on the above, it is considered that any loss of volatiles from the recovered samples that might have occurred would not affect the outcome / conclusions of this report.

Nix Anderson Pty Ltd DS.sf/03.08.2015


G EOTECHNIQUE PTY LTD

4 13188/4-AA 160 Burwood Road, Concord

Duplicate Sample

In order to ensure reliable analytical results from the laboratory, one duplicate soil sample was prepared from an original sample and submitted blind to the primary laboratory (SGS Environmental Services) for analysis. The test results for the duplicate sample were compared with the test results of the corresponding original sample and are summarised in the attached Table B. The duplicate frequency adopted complies with the NEPM, which recommends a duplicate frequency of at least 5% (achieved with 1 duplicate sample analysed from 20 samples analysed, i.e. 5%). A comparison was made and the Relative Percentage Differences (RPD) was computed to assess the difference between the original and duplicate. RPD within 30% are generally considered acceptable. As indicated in Table B, the comparisons between the duplicate and corresponding original sample indicated generally acceptable RPD with the exceptions of higher RPDs for Chromium, lead, nickel and zinc, which were considered due to the heterogeneity of the samples recovered. The concentration of arsenic, copper, lead and nickel of the pairs of samples analysed were also well below the assessment criteria adopted, therefore, the variations are not considered significant and the test results provided by the primary laboratory are deemed reliable for this assessment. Split Sample

Split samples provide a check on the analytical performance of the primary laboratory. One split sample was submitted for analysis to a secondary laboratory (Envirolab Services Pty Ltd). The split sample frequency adopted complies with the NEPM, which recommends a frequency of 5% (achieved with 1 split sample analysed from 20 samples analysed, i.e. 5%). Based on Schedule B (3) of the NEPM, the difference in the results between the split samples should in general be within 30% of the mean concentration determined by both laboratories, i.e., RPD should be within 30%. However, this variation can be higher for organic analysis than for inorganics and for low concentrations of analytes. The test results are summarised in the attached Table C. As indicated in Table C, the comparisons between the split and corresponding original samples indicated generally acceptable RPD with the exception for arsenic, copper, lead and nickel. Higher RPDs calculated for arsenic, copper, lead and nickel were considered due to heterogeneity of the samples analysed. The concentrations of arsenic, copper, lead and nickel for the pairs of samples analysed were also well below the assessment criteria adopted, therefore the variations are not considered significant and the test results provided by the primary laboratory are deemed reliable for this assessment. LABORATORY QA & QC

Geotechnique uses only NATA accredited laboratories for chemical analyses. The laboratory must also incorporate quality laboratory management systems to ensure trained analysts using validated methods and suitably calibrated equipment in order to produce reliable results. In addition to the quality control samples, the laboratory must also ensure that all analysts receive certification as to their competence in carrying out the analysis and participate in national and international proficiency studies. SGS and Envirolab are both accredited by NATA. The two laboratories also operate Quality Systems that are designed to comply with ISO/IEC 17025. All reported laboratory limits of reporting (LOR) / practical quantitation limits (PQL) were less than the assessment criteria. Nix Anderson Pty Ltd DS.sf/03.08.2015


G EOTECHNIQUE PTY LTD

5 13188/4-AA 160 Burwood Road, Concord

As part of the analytical run for the project, the laboratories included laboratory blanks, duplicate samples, laboratory control samples, matrix spikes and surrogate spikes. We have checked the QA/QC procedures and results adopted by the laboratories against the appropriate guidelines. The quality control sample numbers adopted by SGS and Envirolab are considered adequate for the analyses undertaken and generally conform to recommendations provided in the National Environment Protection Measure (NEPM) 1999 (April 2013) “Guideline on Laboratory Analysis of Potentially Contaminated Soils”. Overall, the quality control elements adopted by SGS and Envirolab indicate the analytical data to fall within acceptable levels of accuracy and precision for the analysis of soils. The analytical data provided, is therefore considered to be reliable and useable for this assessment. ASSESSMENT CRITERIA

Investigation levels and screening levels developed in the NEPM 2013 were used in this assessment, as follows: 

Risk-based Health Investigation Levels (HIL) for a broad range of metals and organic substances. The HIL are applicable for assessing human health risk via all relevant pathways of exposure. The HIL as listed in Table 1A (1) of Schedule B1 “Guideline on Investigation Levels for Soil and Groundwater” are provided for different land uses. The site is located within a parcel of industrial land, which will be developed into high density residential community. As such, with regard to human health, analytical results will be assessed against risk based HIL for residential with minimal opportunities for soil access; including dwellings with fully and permanently paved yard space such as high-rise buildings and apartments (HIL B).

Health Screening Levels (HSL) for selected petroleum compounds, fractions and Naphthalene are applicable for assessing human health risk via inhalation and direct contact pathways. The HSL depend on specific soil physicochemical properties, land use scenarios and the characteristics of building structures. The HSL listed in Table 1A(3) of Schedule B1 “Guideline on Investigation Levels for Soil and Groundwater” apply to different soil types and depths below surface to >4 m. For this assessment, the analytical result was assessed against the available HSL for with minimal opportunities for soil access; including dwellings with fully and permanently paved yard space such as high-rise buildings and apartments (HSL B) for clay to depth of 0m to <1m and for sand to depth of 0m to <1m.

Ecological Screening Levels (ESL) for selected petroleum hydrocarbon compounds, TPH fractions and Benzo(a)Pyrene are applicable for assessing the risk to terrestrial ecosystems. ESL listed in Table 1B(6) of Schedule B1 “Guideline on Investigation Levels for Soil and Groundwater” broadly apply to coarse and fine-grained soils and various land uses and are generally applicable to the top 2m of soil. The analytical results were assessed against the available ESL for urban residential for coarse and fine-grained soils.

Nix Anderson Pty Ltd DS.sf/03.08.2015


G EOTECHNIQUE PTY LTD

6 13188/4-AA 160 Burwood Road, Concord

Ecological Investigation Levels (EIL), a specific type of Soil Quality Guidelines (SQG) for selected metals are applicable for assessing the risk to terrestrial ecosystems. EIL listed in Table 1B(1-5) of Schedule B1 “Guideline on Investigation Levels for Soil and Groundwater” depend on specific soil physicochemical properties and land use scenarios and generally apply to the top 2m of soil. The EIL are calculated using 30% effect concentration (EC30) or lowest observed effect concentrations (LOEC) toxicity data. For arsenic and lead generic EIL for urban residential land use for aged contamination are adopted. For other metals, where available, EIL are calculated directly by using EIL calculator developed by CSIRO for NEPC. For this assessment the analytical results were assessed against the available SQG / EIL for urban residential land use for aged contamination in soil for low traffic volume.

With regard to protection of the environment and impact on plant growth the available Provisional Phytotoxicity Based Investigation Levels (PIL) published in the Guidelines for the NSW Site Auditor Scheme (NSW EPA / DEC, 2006) and EIL published in the NEPM 1999 for cadmium and mercury are used.

For discrete soil samples, the individual concentrations of analytes, except Cd and Hg, were assessed against the HIL B / HSL B / ESL / EIL. The individual concentrations of Cd and Hg were assessed against the PIL and HIL B. For asbestos, the assessed soil must not contain bonded ACM in excess of 0.01%w/w and surface soil within the site should be free of visible ACM, and friable asbestos in the soil should not exceed 0.001% w/w. The soil will be deemed contaminated or containing contamination “hot spots” if the above criteria are unfulfilled. Further investigation, remediation and/or management will be recommended if the area of concern is found to be contaminated or contain contamination “hot spots”. LABORATORY TEST RESULTS, ASSESSMENT & DISCUSSION

Copies of the actual laboratory test results certificates from SGS are kept in the offices of Geotechnique and will be provided upon request. The test results are also presented in Tables D to H together with the available assessment criteria adopted. A discussion of the test data is presented in the following subsections. Metals

The Metals test results for discrete selected soil samples are presented in Tables D1 and D2 and as shown, all concentrations of Metals were below the available relevant EIL, HIL B. All Cd and Hg concentrations were also below the relevant PIL. TRH and BTEX

The TRH and BTEX test results for the discrete selected soil samples are presented in Table E. As shown in Table F the concentrations of F1 (TRH C6-C10 less BTEX), F2 (TRH >C10-C16 less Naphthalene), F3 (TRH >C16-C34), F4 (TRH >C34-C40) and BTEX were below the relevant HSL B and / or ESL adopted. PAH

The PAH test results for the selected discrete soil samples are presented in Table F and as shown, all BaP, BaP TEQ, Naphthalene and Total PAH were below the relevant HIL B or ESL or HSL B or EIL adopted. Nix Anderson Pty Ltd DS.sf/03.08.2015


G EOTECHNIQUE PTY LTD

7 13188/4-AA 160 Burwood Road, Concord

OCP

The OCP test results for selected discrete soil samples are presented in Table G and as indicated, OCP were well below the relevant HIL B. The concentrations of DDT were also below the EIL. PCB

The PCB test results for the selected discrete soil samples are presented in Table G and as shown, the PCB concentrations were below the relevant HIL B adopted. Phenols

The Phenols test results for the selected discrete soil samples are presented in Table G and as shown, the Phenols concentrations were well below the relevant HIL B adopted. Cyanides

The Cyanides test results for the selected discrete soil samples are presented in Table G and as shown, the Cyanides concentrations were well below the relevant HIL B adopted. Asbestos

The asbestos results for the selected discrete soil samples are presented in Table H and as shown, no friable asbestos was detected at the laboratory detection limit of 0.001%. CONCLUSION AND RECOMMENDATIONS

Based on this assessment, it is considered that soil samples, recovered from boreholes BH11 to BH16 in conjunction with geotechnical investigation, are unlikely to pose a risk of harm to human health and the terrestrial environment and are environmentally suitable for the proposed development. If suspect materials (identified by unusual staining, odour, discolouration or inclusions such as building rubble, asbestos sheets / pieces, ash material, etc) are encountered during the construction stage, we recommend that this office is contacted for assessment and necessary action. LIMITATIONS

Within the stated scope of work, the services performed by Geotechnique in preparation of this report were conducted in a manner consistent with the level of quality and skill generally exercised by members of the profession and consulting practice. This report has been prepared for Nix Anderson Pty Ltd for the purpose stated within. Any reliance on this report by other parties shall be at such parties' sole risk as the report might not contain sufficient information for other purposes. This report shall only be presented in full and may not be used to support any other objective than those set out in the report, except where written approval is provided by Geotechnique. The information in this report is considered accurate at completion of field sampling (13 July 2015) and in accordance with current site conditions. Any variations to the site form or use beyond this date might nullify the conclusions stated. No contamination assessment can eliminate all risk; even a rigorous professional assessment might not detect all contamination within the investigated locations. Nix Anderson Pty Ltd DS.sf/03.08.2015


G EOTECHNIQUE PTY LTD

8 13188/4-AA 160 Burwood Road, Concord

Reference should be made to the attached "Environmental Notes" for details of the limitations of this assessment. If you have any questions regarding this report, please do not hesitate to contact the undersigned. Yours faithfully GEOTECHNIQUE PTY LTD

DANDA SAPKOTA Senior Environmental Engineer Attached

Attachment A Attachment B Attachment C Attachment D

Drawing No 13188/3-AA1 (Borehole Locations) Engineering Borehole Logs Laboratory Analytical Results Summary Tables (Tables A to H) Environmental Notes

LIST OF REFERENCES Chapman et al. 2004, Soil Landscape Series Sheet 9030, Scale 1:100,000 (Sydney), Soil Conservation Service of NSW, Sydney. Contaminated Land Management Act Herbert C 1983, Geological Series Sheet 9130, Scale 1:100,000 (Sydney), Department of Minerals and Energy, NSW, Sydney. NEPM 1999 (April 2013), National Environment Protection (Assessment of Site Contamination) Measure (NEPM), National Environmental Protection Council (NEPC), Australia.

Nix Anderson Pty Ltd DS.sf/03.08.2015


ATTACHMENT A


BH14 BH13

BH15 BH2

BH3

BH16

BH11 BH12

BH5 BH1 BH4 BH9

BH7

DUK E

BH8

U AVEN E

BH6

BH10

W OO BU R

AD D RO

LEGEND Borehole (August 2014)

0

Imagery ©2014 NearMap.com

Borehole (July 2015)

EOTECHNIQUE

40

60

80

100m

Scale 1:2000 NOTES

G

20

®

PTY LTD

PO Box 880 Penrith NSW 2750 Tel: 02 4722 2700 Fax: 02 4722 2777 e-mail:info@geotech.com.au www.geotech.com.au

1. Site features are indicative and are not to scale. 2. This drawing has been produced using a base plan provided by others to which additional information e.g test pits, borehole locations or notes have been added. Some or all of the plan may not be relevant at the time of producing this drawing

Nix Management Pty Ltd Proposed Development Robert Timms Factory Site (Bushell’s) 160 Burwood Road, Concord Borehole Locations

Drawing No: 13188/3-AA1 Job No: 13188/3 Drawn By: MH Date: 30 July 2015 Checked By: ZA File No: 13188-3 Layers: 0, AA1


ATTACHMENT B


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

deg.

datum :

AHD

classification symbol

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

W

D

hand penetrometer kPa

R.L. surface : 3.5

Remarks and additional observations

ASPHALT PAVEMENT FILL: Sandy Gravel, course grained, brown FILL: Sandy Gravel, coarse grained, yellow

N=12 9,7,5

1

GP

deg.

consistency density index

GP

slope : bearing :

0

GP

Logged/Checked by: MT

Utility Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/3 Borehole No. : 11 Date : 09/07/2015

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

FILL: Silty Sandy Clay, medium plasticity, red brown

N=5 3,2,3

2

GP 3 N=5 3,2,3

GP 4

G

Silty SAND, fine to medium grained, brown to red, with some ironstone SANDSTONE, grey-brown, low to medium strength, extremely weathered

N=40 11,20,20

5

6

7

form no. 002 version 04 - 05/11

SM

8

9

Refer to Cored Borehole

Groundwater at 4.0m

Bedrock


G EOTECHNIQUE PTY LTD

engineering log cored borehole

Coring Commenced at 5.0m 5

SANDSTONE, fine to coarse grained, grey to red-brown

DW- L-M SW

SANDSTONE, fine to coarse grained, greybrown

DW- M-H SW

6

7

8

9

10

Borehole No. 11 terminated at 10.2m

11

form no. 003 version 03 - 09/10

12

13

14

deg.

R.L. surface :

bearing :

deg.

datum :

L

M

H

VH

50

VL

100

EL

3.5 AHD

DEFECT DETAILS DESCRIPTION

defect spacing (mm) 300

point load index strength lS(50)

500

strength

rock type, grain characteristics, colour, structure, minor components.

weathering

CORE DESCRIPTION

MT

slope :

Utility Mounted NMLC

graphic log

depth of R.L. in meters

water loss/level

core size:

Logged/Checked by :

1000

drill model and mounting :

barrel lift

Job No. : 13188/3 Borehole No. : 11 Date : 09/07/2015

Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

2000

Client : Project : Location :

type, inclination, thickness, planarity, roughness, coating. Specific General


G EOTECHNIQUE

PTY LTD

GEOTECHNIQUE PTY LTD Job No 13188/3 BH11 Started Coring at 5m 5.0m 6.0m 7.0m 8.0m 9.0m 10.0m

BH11 terminated at 10.2m

Nix Anderson Pty Ltd MT.mh/04.09.2014


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

deg.

datum :

AHD

classification symbol

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

hand penetrometer kPa

R.L. surface : 3.4

consistency density index

deg.

Remarks and additional observations

TOPSOIL: Sandy Silt, low plasticity, dark brown, with some roots FILL: Silty Clayey Sand, fine to coarse grained, with some gravel FILL: Silty Clay, medium plasticity, grey, with some gravel

N=7 3,3,4

GP 1

GP

slope : bearing :

0

GP

Logged/Checked by: MT

Utility Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/3 Borehole No. : 12 Date : 09/07/2015

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

N=8 4,3,5

Groundwater at 1.8m 2

GP 3 N=5 1,2,3

GP 4

G

SC-SM Silty Clayey SAND, fine to medium grained,

W

black to dark brown, with some shell fragments CI

N=2 1,1,1

Silty Sandy CLAY, medium plasticity, red to brown

M>PL

L

5

6 N=10 3,5,5

Becoming harder to drill

7

form no. 002 version 04 - 05/11

N=R 12,16/ 100

SC-SM Silty Clayey SAND, fine to coarse grained, 8

9

grey-brown to red SANDSTONE, grey to red-brown, extremely weathered, low strength

W

MD Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

10

11

12

13

14

15

16

form no. 002 version 04 - 05/11

17

18

19

Logged/Checked by: MT

deg.

R.L. surface : 3.4

deg.

datum :

AHD

classification symbol

bearing : MATERIAL DESCRIPTION

soil type, plasticity or particle characteristic, colour, secondary and minor components.

Borehole No. 12 terminated at 9.7m due to TCBit refusal

hand penetrometer kPa

slope :

consistency density index

Utility Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/3 Borehole No. : 12 Date : 09/07/2015

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

R.L. surface : 3.4

deg.

datum :

AHD

classification symbol

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

W

MD

W

D

hand penetrometer kPa

deg.

consistency density index

GP

slope : bearing :

0

GP

Logged/Checked by: MT

Utility Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/3 Borehole No. : 13 Date : 10/07/2015

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations

TOPSOIL: Silty Sand, fine to medium grained, dark brown, with some grass roots FILL: Silty Clay, medium plasticity, brownorange, with some gravel

N=12 4,7,5

1

GP

FILL: Silty Clay, medium plasticity, brown-grey

N=6 3,3,3

2

GP

SC-SM Silty Clayey SAND, fine to medium grained,

Groundwater at 2.5m

yellow, with some sandstone gravel 3 N=8 3,4,4

SM

Silty SAND, fine to coarse grained, grey

4

N=R 5,8,20/50

5

6

form no. 002 version 04 - 05/11

7

8

9

SANDSTONE, fine to coarse grained, greybrown to yellow, extremely weathered, low strength

Refer to Cored Borehole

Bedrock


G EOTECHNIQUE PTY LTD

engineering log cored borehole

deg.

R.L. surface :

bearing :

deg.

datum :

L

M

H

VH

50

VL

100

EL

SANDSTONE, fine to coarse grained, brown to DW L-M red-grey

SANDSTONE, fine to coarse grained, grey to red-brown

DW L-M

7

8

CORE LOSS: 7.4-7.5m SANDSTONE, fine to coarse grained, grey to DW M red-brown DW- M-H SANDSTONE, fine to coarse grained, brown to SW grey

9

10

11

12

form no. 003 version 03 - 09/10

13

14

15

Borehole No. 13 terminated at 10.0m

AHD

type, inclination, thickness, planarity, roughness, coating. Specific General

Coring Commenced at 5.8m 6

3.4

DEFECT DETAILS DESCRIPTION

defect spacing (mm) 300

point load index strength lS(50)

500

strength

rock type, grain characteristics, colour, structure, minor components.

weathering

CORE DESCRIPTION

MT

slope :

Utility Mounted NMLC

graphic log

depth of R.L. in meters

water loss/level

core size:

Logged/Checked by :

1000

drill model and mounting :

barrel lift

Job No. : 13188/3 Borehole No. : 13 Date : 10/07/2015

Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

2000

Client : Project : Location :

Core loss 100mm


G EOTECHNIQUE

PTY LTD

GEOTECHNIQUE PTY LTD Job No 13188/3 BH13 Started Coring at 5.8m 5.8m

5.0m 6.0m 7.0m 8.0m 9.0m BH13 terminated at 10.0m

Nix Anderson Pty Ltd MT.mh/04.09.2014


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord Utility Mounted

deg.

R.L. surface : 3.2

deg.

datum :

AHD

moisture condition

consistency density index

classification symbol

Silty SAND, fine to coarse grained, grey-brown

W

MD

Silty SAND, fine to medium grained, grey

W

MD

W

MD

W

MD

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

Remarks and additional observations

TOPSOIL: Silty Sand, fine to medium grained, brown, with some grass roots FILL: Silty Clay, medium plasticity, grey-brown

N=6 1,2,4

1

GP

slope : bearing :

0

GP

Logged/Checked by: MT

mm depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/3 Borehole No. : 14 Date : 10/07/2015

hand penetrometer kPa

drill model and mounting :

graphic log

Client : Project : Location :

FILL: Silty Sand, fine to medium grained, brown, with trace of iron shards

N=20 11,15,5

2

GP

3 N=9 10,5,4

Silty SAND, fine to medium grained, greybrown

SM

Groundwater at 3.0m

4

SC-SM Silty Clayey SAND, fine to coarse grained, red-

brown

N=13 3,5,8

5

6 N=23 5,11,12

7

form no. 002 version 04 - 05/11

N=R 25/50

SM

Silty SAND, fine to coarse grained, red- brown, with some sandstone fragments

SANDSTONE, red-brown to grey, extremely weathered, low strength SANDSTONE, grey to red, distinctly weathered, low to medium strength

8

9

Bedrock


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

10

11

12

13

14

15

16

form no. 002 version 04 - 05/11

17

18

19

Logged/Checked by: MT

deg.

R.L. surface : 3.2

deg.

datum :

AHD

classification symbol

bearing : MATERIAL DESCRIPTION

soil type, plasticity or particle characteristic, colour, secondary and minor components.

Borehole No. 14 terminated at 10.0m

hand penetrometer kPa

slope :

consistency density index

Utility Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/3 Borehole No. : 14 Date : 10/07/2015

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

0

GP

GP

N=R 3,5,25/50

Logged/Checked by: MT

deg.

R.L. surface : 3.2

deg.

datum :

AHD

classification symbol

bearing : MATERIAL DESCRIPTION

soil type, plasticity or particle characteristic, colour, secondary and minor components.

TOPSOIL: Silty Sand, fine to medium grained, brown, with some grass FILL: Silty Sandy Clay, medium plasticity, brown

1

Borehole No. 15 terminated at 1.3m due to refusal in possible sandstone boulder 2

3

4

5

6

form no. 002 version 04 - 05/11

7

8

9

hand penetrometer kPa

slope :

consistency density index

Utility Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/3 Borehole No. : 15 Date : 13/07/2015

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations


G EOTECHNIQUE PTY LTD

engineering log - borehole Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

GP

deg.

datum :

AHD

classification symbol

MATERIAL DESCRIPTION soil type, plasticity or particle characteristic, colour, secondary and minor components.

N=10 3,6,4

FILL: Silty Sand, fine to coarse grained, brown, with some gravel

N=12 3,4,8

2

N=R 25/50

3

FILL: Silty Sand, fine grained, brown, with some boulders

4

5

6

SM

Silty SAND, fine to medium grained, dark brown, with some shell fragments

7

form no. 002 version 04 - 05/11

Refer to Cored Borehole 8

9

W

hand penetrometer kPa

R.L. surface : 3.2

consistency density index

deg.

TOPSOIL: Silty Sand, fine to medium grained, brown, with grass roots FILL: Silty Clay, medium plasticity, grey-brown

1

GP

slope : bearing :

0

GP

Logged/Checked by: MT

Utility Mounted mm

depth or R.L. in meters

field test

geo samples

PID reading (ppm)

env samples

groundwater

method

hole diameter : 125

Job No. : 13188/3 Borehole No. : 16 Date : 13/07/2015

moisture condition

drill model and mounting :

graphic log

Client : Project : Location :

Remarks and additional observations


G EOTECHNIQUE PTY LTD

engineering log cored borehole

deg.

R.L. surface :

bearing :

deg.

datum :

L

M

H

VH

50

VL

100

EL

8

Core loss 250mm

SANDSTONE, fine to coarse grained, redbrown, grey

DWSW

M

SANDSTONE, fine to coarse grained, redbrown

DW- M-H SW

SANDSTONE, fine to coarse grained, grey

SW- HFR VH

9

10

11

12

Borehole No. 16 terminated at 12.2m

13

14

form no. 003 version 03 - 09/10

15

16

17

AHD

type, inclination, thickness, planarity, roughness, coating. Specific General

Coring Commenced at 7.6m CORE LOSS: 7.6-7.85m

3.2

DEFECT DETAILS DESCRIPTION

defect spacing (mm) 300

point load index strength lS(50)

500

strength

rock type, grain characteristics, colour, structure, minor components.

weathering

CORE DESCRIPTION

MT

slope :

Utility Mounted NMLC

graphic log

depth of R.L. in meters

water loss/level

core size:

Logged/Checked by :

1000

drill model and mounting :

barrel lift

Job No. : 13188/3 Borehole No. : 16 Date : 13/07/2015

Nix Anderson Pty Ltd Proposed Development 160 Burwood Road, Concord

2000

Client : Project : Location :


G EOTECHNIQUE

PTY LTD

GEOTECHNIQUE PTY LTD Job No 13188/3 BH16 Started Coring at 7.6m 7.6m

7.0m 8.0m 9.0m 10.0m 11.0m 12.0m

BH16 terminated at 12.2m

Nix Anderson Pty Ltd MT.mh/04.09.2014


KEY TO SYMBOLS Symbol

Description

Strata symbols Pavement (Bitumen, Concrete Slab, etc) Fill Silty Sand Sandstone Topsoil Silty Clayey Sand Silty Sandy Clay medium plasticity Misc. Symbols Groundwater Descriptions of various line types (solid, dotted, etc.) Profile change Gradual profile change

Notes: 1. Exploratory borings were drilled between 13/07/2015 and 13/07/2015 using a 50, 100 and 125mm diameter continuous flight power auger. 2. These logs are subject to the limitations, conclusions and recommendations in this report. 3. Results of tests conducted on samples recovered are reported on the logs.


KEY TO SYMBOLS Symbol

Description

Strata symbols Sandstone Core Loss Misc. Symbols Point Load Strength Descriptions of various line types (solid, dotted, etc.) Profile change Gradual profile change

Notes: 1. Exploratory borings were drilled between 13/07/2015 and 13/07/2015 using a 50, 100 and 125mm diameter continuous flight power auger. 2. These logs are subject to the limitations, conclusions and recommendations in this report. 3. Results of tests conducted on samples recovered are reported on the logs.


G EOTECHNIQUE

PTY LTD

Log Symbols & Abbreviations (Non-cored Borehole Log) Log Column

Symbol/Value

Description

Drilling Method

V-bit TC-bit RR DB BB Dry

Hardened steel ‘V’ shaped bit attached to auger Tungsten Carbide bit attached to auger Tricone (Rock Roller) bit Drag bit Blade bit Groundwater not encountered to the drilled or auger refusal depth

Groundwater

Groundwater level at depths shown on log Environment Sample PID Reading Geotechnical Sample Field Test

GP G P 100

Groundwater seepage at depths shown on log Glass bottle and plastic bag sample over depths shown on log Glass bottle sample over depths shown on log Plastic bag sample over depths shown on log PID reading in ppm

DS DB U50 N=10 3,5,5

Disturbed Small bag sample over depths shown on log Disturbed Bulk sample over depths shown on log Undisturbed 50mm tube sample over depths shown on log Standard Penetration Test (SPT) ‘N’ value. Individual numbers indicate blows per 150mm penetration.

N=R 10,15/100

‘R’ represents refusal to penetration in hard/very dense soils or in cobbles or boulders. The first number represents10 blows for 150mm penetration whereas the second number represents 15 blows for 100mm penetration where SPT met refusal

DCP/PSP

5 6 R/10

Classification

Moisture Condition Cohesive soils

Cohesionless soils Consistency Cohesive soils

Density Index Cohesionless soils

Hand Penetrometer

Dynamic Cone Penetration (DCP) or Perth Sand Penetrometer (PSP). Each number represents blows per 100mm penetration. ‘R/10’ represents refusal after 10mm penetration in hard/very dense soils or in gravels or boulders.

GP GW GM GC SP SW SM SC ML MI MH CL CI CH

Poorly Graded GRAVEL Well graded GRAVEL Silty GRAVEL Clayey GRAVEL Poorly graded SAND Well graded SAND Silty SAND Clayey SAND SILT / Sandy SILT / clayey SILT, low plasticity SILT / Sandy SILT / clayey SILT, medium plasticity SILT / Sandy SILT / clayey SILT, high plasticity CLAY / Silty CLAY / Sandy CLAY / Gravelly CLAY, low plasticity CLAY / Silty CLAY / Sandy CLAY / Gravelly CLAY, medium plasticity CLAY / Silty CLAY / Sandy CLAY / Gravelly CLAY, high plasticity

M<PL M=PL M>PL

Moisture content less than Plastic Limit Moisture content equal to Plastic Limit Moisture content to be greater than Plastic Limit

D M W

Dry Runs freely through hand Moist Tends to cohere Wet Tends to cohere Term Undrained shear strength, C u (kPa) Hand Penetrometer (Qu) Very Soft ≤12 <25 Soft >12 ≤25 25 – 50 Firm >25 ≤50 50 – 100 Stiff >50 ≤100 100 – 200 Very Stiff >100 ≤200 200 – 400 Hard >200 >400 Term Density Index, ID (%) SPT ‘N’ (blows/300mm) Very Loose ≤15 ≤5 Loose >15 ≤35 >5 ≤10 Medium Dense >35 ≤65 >10 ≤30 Dense >65 ≤85 >30 ≤50 Very Dense >85 >50 Unconfined compressive strength (qu) in kPa determined using pocket penetrometer, at depths shown on log Geological origin of soils Residual soils above bedrock River deposited Alluvial soils Gravity deposited Colluvial soils Wind deposited Aeolian soils Marine Soils

VS S F St VSt H VL L M D VD 100 200

Remarks Residual Alluvium Colluvial Aeolian Marine


G EOTECHNIQUE

PTY LTD

AS1726 – Unified Soil Classification System Major Divisions

Particle size (mm)

Group Symbol

Typical Names

Field Identifications Sand and Gravels

Laboratory classification

BOULDERS

% (2) < 0.075mm

Plasticity of Fine Fraction

Cu = D60/D10

Cc = (D30)2/(D10D60)

0-5

-

>4

between 1 and 3

0-5

-

200

Notes

Well-graded gravels, gravel-sand mixtures, little or no fines

Wide range in grain size and substantial amounts of all intermediate sizes, not enough fines to bind coarse grains, no dry strength

GP

Poorly graded gravels, gravelsand mixtures, little or no fines, uniform gravels

Predominantly one size or range of sizes with some intermediate sizes missing, not enough fines to bind coarse grains, no dry strength

GM

Silty gravels, gravel-sand-silt mixtures

‘Dirty’ materials with excess of non-plastic fines, zero to medium dry strength

GC

Clayey gravels, gravel-sand-clay mixtures

‘Dirty’ materials with excess of plastic fines, medium to high dry strength

SW

Well-graded sands, gravelly sands, little or no fines

Wide range in grain size and substantial amounts of all intermediate sizes, not enough fines to bind coarse grains, no dry strength

SP

Poorly graded sands and gravelly sands; little or no fines, uniform sands

Predominantly one size or range of sizes with some intermediate sizes missing, not enough fines to bind coarse grains, no dry strength

SM

Silty sands, sand-silt mixtures

‘Dirty’ materials with excess of non-plastic fines, zero to medium dry strength

SC

Clayey sand, sand-clay mixtures

‘Dirty’ materials with excess of plastic fines, medium to high dry strength

ML

Inorganic silts and very fine sands, rock flour, silty or clayey fine sands or clayey silts with slight plasticity Inorganic clays of low to medium plasticity, gravelly clays, sandy clays, silty clays, lean clays

Dry Strength

Dilatancy

Toughness

None to low

Quick to slow None to very slow

None

Organic silts and organic silty clays of low plasticity

Low to medium

Slow

Low

MH

Inorganic silts, micaceous or diatomaceous fine sandy or silty soils, elastic silts

Low to medium

Slow to none

Low to medium

CH

Inorganic clays of medium to high plasticity, fat clays

High to very high

None

High

Coarse 20

COARSE GRAINED SOILS (more than half of material less 63mm is larger than 0.075mm)

GRAVELS (more than half of coarse fraction is larger than 2.36mm) Medium 6

Fine 2.36

Coarse 0.6 SANDS (more than half of coarse fraction is smaller than 2.36mm)

Medium 0.2

Fine 0.075

CL, CI SILTS & CLAYS (liquid limit < 50%) OL FINE GRAINED SOILS (more than half of material less than 63mm is smaller than 0.075mm) SILTS & CLAYS (liquid limit > 50%)

Medium to high

None to very slow

Medium

OH

Organic clays of medium to high plasticity, organic silts

Medium to high

Low to medium

Pt

Peat and highly organic soils

Identified by colour, odour, spongy feel and generally by fibrous texture

12-50

Below ‘A’ line or Ip<4

-

-

12-50

Above ‘A’ line or Ip>7

-

-

>6

between 1 and 3

0-5

-

0-5

-

Below ‘A’ line or Ip<4

-

-

12-50

Above ‘A’ line of Ip>7

-

-

Below ‘A’ line Below ‘A’ line Above ‘A’ line

40

CH

30

CI

CL

20

OH or MH

10

Below ‘A’ line

OL or ML

CL-ML 0

HIGHLY ORGANIC SOILS

2. Borderline classifications occur when the percentage of fines (fraction smaller than 0.075mm size) is greater than 5% and less than 12%. Borderline classifications require the use of dual symbols e.g. SP-SM, GWGC

Fails to comply with above

12-50

Below ‘A’ line Above ‘A’ line

1. Identify lines by the method given for fine grained soils

Fails to comply with above

Plasticity Index (Ip), percent

GW

More than 50% passing 0.075mm

63

Use the gradation of material passing 63mm for classification of fractions according to the criteria given in ‘Major Divisions’

COBBLES

Effervesces with H 2O2

0

10

20

30

40

50

60

Liquid Limit (WL), percent

70

80


G EOTECHNIQUE

PTY LTD

Log Symbols & Abbreviations (Cored Borehole Log) Log Column

Symbol

Description

NQ NMLC HQ

Nominal Core Size (mm) 47 52 63 Complete water loss

Core Size

Water Loss Weathering

FR

Partial water loss Fresh

SW

Slightly Weathered

Rock is slightly discoloured but shows little or no change of strength from fresh rock

DW

Distinctly Weathered

Rock strength usually changed by weathering. The rock may be highly discoloured, usually by ironstaining. Porosity may be increased by leaching, or may be decreased by deposition of weathering products in pores

EW

Extremely Weathered

Rock is weathered to such an extent that it has ‘soil’ properties, i.e. it either disintegrate or can be remoulded, in water

RS

Residual Soil

Strength EL VL L M H VH EH Defect Spacing

Defect Description Type

Soil developed on extremely weathered rock; the mass structure and substance fabric are no longer evident; there is a large change in volume but soil has not been significantly transported Term Point Load Strength Index (Is50, MPa) Extremely Low ≤0.03 Very Low >0.03 ≤0.1 Low >0.1 ≤0.3 Medium >0.3 ≤1 High >1 ≤3 Very High >3 ≤10 Extremely High >10 Description Spacing (mm) Extremely closely spaced <20 Very closely spaced 20 to 60 Closely spaced 60 to 200 Medium spaced 200 to 600 Widely spaced 600 to 2000 Very widely spaced 2000 to 6000 Extremely widely spaced >6000

Bp Fp Jo Sh Cs Ds Is

Bedding parting Foliation parting Joint Sheared zone Crushed seam Decomposed seam Infilled seam

Macro-surface geometry

St Cu Un Ir Pl

Stepped Curved Undulating Irregular Planar

Micro-surface geometry

Ro Sm Sl

Rough Smooth Slickensided

cn sn vn cg

clean stained veneer coating

Coating or infilling

Rock shows no sign of decomposition or staining


G EOTECHNIQUE

PTY LTD

AS1726 – Identification of Sedimentary Rocks for Engineering Purposes Grain Size mm More than 20

Bedded rocks (mostly sedimentary) Grain Size Description

At least 50% of grains are of carbonate

20 CONGLOMERATE Rounded boulders, cobbles and gravel cemented in a finer matrix Breccia Irregular rock fragments in a finer matrix

0.6

0.2

ARENACEOUS

Coarse

Medium

Fine

0.06

0.002 Less than 0.002

SANDSTONE Angular or rounded grains, commonly cemented by clay, calcite or iron minerals Quartzite Quartz grains and siliceous cement Arkose Many feldspar grains Greywacke Many rock chips MUDSTONE

SILTSTONE Mostly silt

SHALE Fissile

CLAYSTONE Mostly clay

ARGILLACEOUS

Amorphous or crypto-crystalline

Rounded grains AGGLOMERATE Angular grains VOLCANIC BRECCIA Cemented volcanic ash

SALINE ROCKS Halite Anhydrite Gypsum

TUFF Calcarenite

Calcisiltite Calcareous Mudstone

2

Calcirudite

LIMESTONE and DOLOMITE (undifferentiated)

RUDACEOUS

Calcilutite

Fine-grained TUFF CHALK

6

At least 50% of grains are of fine-grained volcanic rock Fragments of volcanic ejecta in a finer matrix

Very fine-grained TUFF

Flint: occurs as hands of nodules in the chalk Chert: occurs as nodules and beds in limestone and calcareous sandstone

COAL LIGNITE

Granular cemented – except amorphous rocks

SILICEOUS

CALCAREOUS

SILICEOUS

CARBONACEOUS

SEDIMENTARY ROCKS Granular cemented rocks vary greatly in strength, some sandstones are stronger than many Igneous rocks. Bedding may not show in hand specimens and is best seen in outcrop. Only sedimentary rocks, and some metamorphic rocks derived from them, contain fossils Calcareous rocks contain calcite (calcium carbonate) which effervesces with dilute hydrochloric acid

AS1726 – Identification of Metamorphic and Igneous Rocks for Engineering Purposes Obviously foliated rocks (mostly metamorphic)

Grain size (mm) More than 20

Rocks with massive structure and crystalline texture (mostly igneous)

Grain size description

Grain size description

Pegmatite

Pyrosenite

MARBLE GNEISS Well developed but often widely spaced foliation sometimes with schistose bands

QUARTZITE

Migmatite Irregularly foliated: mixed schists and gneisses SCHIST Well developed undulose foliation; generally much mica MEDIUM

GRANITE

Diorite

GABBRO 6

Granulite

COARSE

20 Peridorite

COARSE

These rocks are sometimes phorphyritic and are then described, for example, as porphyritic granite

HORNFELS 2 Amphibolite

Micorgranite

Microdiorite 0.6

Serpentine

MEDIUM

These rocks are sometimes phorphyritic and are then described as porphyries

Dolerite 0.2

0.06

FINE

PHYLLITE Slightly undulose foliation; sometimes ‘spotted’

RHYOLITE FINE

SLATE Well developed plane cleavage (foliation) Mylonite Found in fault zones, mainly in igneous and metamorphic areas

ANDESITE

These rocks are sometimes phorphyritic and are then described as porphyries Obsidian

0.002

BASALT

Less than 0.002 Amorphous or cryptocrystallin e

Volcanic glass

CRYSTALLINE Pale<------------------------------------------------------------------->Dark SILICEOUS

Mainly SILICEOUS

METAMORPHIC ROCKS Most metamorphic rocks are distinguished by foliation which may impart fissility. Foliation in gneisses is best observed in outcrop. Nonfoliated metamorphics are difficult to recognize except by association. Any rock baked by contact metamorphism is described as ‘hornfels’ and is generally somewhat stronger than the parent rock Most fresh metamorphic rocks are strong although perhaps fissile

ACID Much quartz

INTERMEDIATE Some quartz

BASIC Little or no quartz

ULTRA BASIC

IGNEOUS ROCKS Composed of closely interlocking mineral grains. Strong when fresh; not porous Mode of occurrence : 1 Batholith; 2 Laccoliths; 3 Sills; 4 Dykes; 5 Lava Flows; 6 Veins


ATTACHMENT C


GEOTECHNIQUE PTY LTD

TABLE A TRIP SPIKE SAMPLE (Ref No: 13188/4-AA) ANALYTES

Trip Spike TS1

BTEX Benzene

100%

Toluene

107%

Ethyl Benzene

99%

Xylenes

100%

Note : results are reported as percentage recovery of know n spike concentrations

Nix Anderson Pty Ltd DS.sf/03.08.2015


GEOTECHNIQUE PTY LTD

TABLE B DUPLICATE SAMPLE (Ref No: 13188/4-AA) . ANALYTES

BH11

Duplicate

RELATIVE PERCENTAGE

0-0.15m

D1

DIFFERENCES (RPD)

m g/kg

m g/kg

% -

METALS Arsenic

<3

<3

Cadmium

0.4

<0.3

-

Chromium

37

18

69

Copper

29

29

0

Lead

10

6

50

Mercury

0.01

<0.01

-

Nickel

36

6.7

137

Zinc

49

27

58

F1 (C6-C10 less BTEX)

<25

<25

-

F2 (>C10-C16)

<25

<25

-

F3 (>C16-C34)

<90

<90

-

F4 (>C34-C40)

<120

<120

-

Benzene

<0.1

<0.1

-

Toluene

<0.1

<0.1

-

Ethyl Benzene

<0.1

<0.1

-

Xylenes

<0.3

<0.3

-

<0.3

<0.3

-

1

<0.8

-

Naphthalene

<0.1

<0.1

-

Benzo(a)Pyrene

<0.1

<0.1

-

Hexachlorobenzene (HCB)

<0.1

<0.1

-

Heptachlor

<0.1

<0.1

-

Aldrin+Dieldrin

<0.15

<0.15

-

Endrin

<0.2

<0.2

-

Methoxychlor

<0.1

<0.1

-

Mirex

<0.1

<0.1

-

Endosulfan (alpha, beta & sulphate)

<0.5

<0.5

-

DDD+DDE+DDT

<0.6

<0.6

-

Chlordane (alpha & gamma)

<0.2

<0.2

-

<1

<1

-

<0.5

<0.5

-

<5

<5

-

TOTAL PETROLEUM HYDROCARBONS (TPH)

BTEX

POLYCYCLIC AROMATIC HYDROCARBONS Benzo(a)Pyrene TEQ Total PAH

ORGANOCHLORINE PESTICIDES (OCP)

POLYCHLORINATED BIPHENYLS (PCB) Total PCB CYANIDES & PHENOLS Cyanides Phenols

Nix Anderson Pty Ltd DS.sf/03.08.2015


GEOTECHNIQUE PTY LTD

TABLE C SPLIT SAMPLE (Ref No: 13188/4-AA) ANALYTES

BH13

Split Sam ple

RELATIVE PERCENTAGE

0-0.15m

S1

DIFFERENCES (RPD)

m g/kg

m g/kg

(SGS)

(ENVIROLAB)

% 40

METALS Arsenic

6

4

Cadmium

0.5

<0.4

-

Chromium

16

15

6

Copper

20

35

55

Lead

24

15

46

Mercury

0.02

<0.1

-

Nickel

7.5

14

60

Zinc

32

32

0

F1 (C6-C10 less BTEX)

<25

<25

-

F2 (>C10-C16)

<25

<50

-

F3 (>C16-C34)

<90

<100

-

F4 (>C34-C40)

<120

<100

-

Benzene

<0.1

<0.2

-

Toluene

<0.1

<0.5

-

Ethyl Benzene

<0.1

<1

-

Xylenes

<0.3

<3

-

TOTAL PETROLEUM HYDROCARBONS (TPH)

BTEX

POLYCYCLIC AROMATIC HYDROCARBONS (PAH) Benzo(a)Pyrene TEQ

<0.3

<0.5

-

Total PAH

<0.8

<1.55

-

Naphthalene

<0.1

<0.1

-

Benzo(a)Pyrene

<0.1

<0.05

-

Hexachlorobenzene (HCB)

<0.1

<0.1

-

Heptachlor

<0.1

<0.1

-

Aldrin+Dieldrin

<0.15

<0.2

-

Endrin

<0.2

<0.1

-

Methoxychlor

<0.1

<0.1

-

Mirex

<0.1

-

-

Endosulfan (alpha (I), beta (II) & sulphate)

<0.5

<0.3

-

DDD+DDE+DDT

<0.6

<0.3

-

Chlordane (alpha & gamma)

<0.2

<0.2

-

<1

<0.7

-

<0.5

<0.5

-

<5

<5

-

ORGANOCHLORINE PESTICIDES (OCP)

POLYCHLORINATED BIPHENYLS (PCB) Total PCB CYANIDES & PHENOLS Cyanides Phenols

Nix Anderson Pty Ltd DS.sf/03.08.2015


GEOTECHNIQUE PTY LTD

TABLE D1 METALS, CATION EXCHANGE CAPACITY (CEC) & pH TEST RESULTS DISCRETE SAMPLES (Ref No: 13188/4-AA)

Sample Location

Depth (m)

ARSENIC

CADMIUM

CHROMIUM (Total)

COPPER

LEAD

MERCURY

NICKEL

ZINC

CEC (cmolc /kg)

pH

METALS (mg/kg)

BH11

2.5-2.8

5

0.3

13

5.1

16

0.01

0.6

4.4

3.5

4.9

BH12

0-0.15

4

<0.3

12

17

19

0.02

4.9

26

8.4

7

BH12

1.5-1.8

6

0.3

12

16

21

0.02

2.2

21

-

-

BH13

0-0.15

6

0.5

16

20

24

0.02

7.5

32

10

7.9

BH13

1.5-1.8

6

0.4

13

6.8

20

0.01

1.4

8.8

8.1

7.2

BH14

0-0.15

4

0.3

14

16

20

0.11

6.3

36

-

-

BH14

2.0-2.1

<3

<0.3

19

4

7

0.03

2.1

100

-

-

BH15

0-0.15

6

0.4

13

21

28

0.01

5.5

36

-

-

BH15

0.5-0.8

5

0.4

14

21

29

0.02

6.4

32

12

7.1

BH16

0.5-0.8

5

0.3

16

19

19

0.02

5.5

22

-

-

BH16

1.5-1.8

<3

<0.3

32

21

19

0.03

2.4

34

2.6

9

3

0.3

0.5

0.5

1

0.05

0.5

0.5

0.02

-

500

150

500

30000

1200

30

Limits of Reporting (LOR) NATIONAL ENVIRONMENT PROTECTION AMENDMENT MEASURE (2013) a

Health-based Investigation Levels (HIL) B - Residential B

e b

Ecological Investigation Levels (EIL) - Urban residential

100

c

400

1200 60000

g

f

-

d

95

1100

-

10

160

GUIDELINES FOR THE NSW SITE AUDITOR SCHEME (2006) Provisional Phytotoxity-Based Investigation Levels (PIL) Notes:

3

1

a: Residential w ith minimal opportunities for soil access; includes dw ellings w ith fully and permanently paved yard space such as high-rise buildings and apartments. b: EIL of aged chromium(III), nickel & zinc w ere derived from calculation spreadsheet developed by CSIRO for NEPC; old NSW suburb w ith low traffic volume; the low est CEC=2.6 cmolc/kg & pH=4.9; the assumed clay content=10 % w ere selected for derivation of EIL; a conservative approach. EIL of aged copper w as calculated based on the pH and the CEC of the sample analysed and the low est value of the ACL w as adopted. c: Chromium (VI) d: Methyl Mercury e: Generic EIL for aged arsenic f: Chromium (III) g: Generic added contaminant limit for aged lead + ambient background concentration; old NSW suburb w ith low traffic volume.

Nix Anderson Pty Ltd DS.sf/03.08.2015


GEOTECHNIQUE PTY LTD

TABLE D2 METALS, CATION EXCHANGE CAPACITY (CEC) & pH TEST RESULTS DISCRETE SAMPLE (Ref No: 13188/4-AA)

Sample Location

Depth (m)

ARSENIC

CADMIUM

CHROMIUM (Total)

COPPER

LEAD

MERCURY

NICKEL

ZINC

CEC (cmolc /kg)

pH

METALS (mg/kg)

BH11

0-0.15

<3

0.4

37

29

10

0.01

36

49

14

9.1

3

0.3

0.5

0.5

1

0.05

0.5

0.5

0.02

-

500

150

500

30000

1200

30

Limits of Reporting (LOR) NATIONAL ENVIRONMENT PROTECTION AMENDMENT MEASURE (2013) a

Health-based Investigation Levels (HIL) B - Residential B

e b

Ecological Investigation Levels (EIL) - Urban residential

100

c

410

1200 60000

g

f

-

d

190

1100

-

210

600

GUIDELINES FOR THE NSW SITE AUDITOR SCHEME (2006) Provisional Phytotoxity-Based Investigation Levels (PIL) Notes:

3

1

a: Residential w ith minimal opportunities for soil access; includes dw ellings w ith fully and permanently paved yard space such as high-rise buildings and apartments. b: EIL of aged chromium(III), nickel & zinc w ere derived from calculation spreadsheet developed by CSIRO for NEPC; old NSW suburb w ith low traffic volume; CEC=14 cmolc/kg & pH=9.1; the assumed clay content=10 % w ere selected for derivation of EIL; a conservative approach. EIL of aged copper w as calculated based on the pH and the CEC of the sample analysed and the low er value of the tw o ACL w as adopted. c: Chromium (VI) d: Methyl Mercury e: Generic EIL for aged arsenic f: Chromium (III) g: Generic added contaminant limit for aged lead + ambient background concentration; old NSW suburb w ith low traffic volume.

Nix Anderson Pty Ltd DS.sf/03.08.2015


GEOTECHNIQUE PTY LTD

TABLE E TOTAL RECOVERABLE HYDROCARBONS (TRH) AND BTEX TEST RESULTS DISCRETE SAMPLES (Ref No: 13188/4-AA) NATIONAL ENVIRONMENT PROTECTION AMENDMENT MEASURE (2013) Health Screening Levels (HSL) B High density residential

F4

BENZENE

TOLUENE

ETHYLBENZENE

XYLENES

TOLUENE

ETHYLBENZENE

XYLENES

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

-

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

BH12

0-0.15

sand

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

45

110 0.5 160

55

40

-

-

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

BH12

1.5-1.8

sand

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

70

240 0.5 220 NL

60

-

-

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

BH13

0-0.15

sand

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

45

110 0.5 160

55

40

-

-

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

BH13

1.5-1.8

sand

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

70

240 0.5 220 NL

60

-

-

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

BH14

0-0.15

sand

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

45

110 0.5 160

55

40

-

-

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

BH15

0-0.15

sand

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

45

110 0.5 160

55

40

-

-

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

BH15

0.5-0.8

sand

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

45

110 0.5 160

55

40

-

-

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

BH16

0.5-0.8

sand

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

45

110 0.5 160

55

40

-

-

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

BH16

1.5-1.8

sand

<25

<25

<25

<90 <120 <0.1 <0.1 <0.1 <0.3

70

240 0.5 220 NL

60

-

-

-

-

-

-

-

-

180 120 300 2800 50 85

70

105

90

120

0.1

0.1

0.1

F1

F2*

BENZENE

F3

-

-

F4

F2**

-

95

110 0.5 160

F3

F1

40

45

F2**

XYLENES

55

<90 <120 <0.1 <0.1 <0.1 <0.3 110 440 0.5 310 NL

F1

ETHYLBENZENE

<90 <120 <0.1 <0.1 <0.1 <0.3

<25

TOLUENE

<25

<25

BENZENE

<25

<25

XYLENES

<25

sand

Limits of Reporting (LOR) 25 25 25 Notes: F1: C6-C10 less BTEX F2*: >C10-C16 less Naphthalene F2**: >C10-C16 F3: >C16-C34 F4: >C34-C40

ETHYLBENZENE

sand

2.5-2.8

TOLUENE

F3

0-0.15

BH11

Soil type

BENZENE

F2**

BH11

Sample Depth Location (m)

F4

F2*

BTEX (mg/kg)

Ecological Screening Levels for coarsegrained soil Urban residential

F1

TRH (mg/kg)

Ecological Screening Levels for finegrained soil Urban residential

0.3

NL: Not Limiting

Nix Anderson Pty Ltd DS.sf/03.08.2015


GEOTECHNIQUE PTY LTD

TABLE F POLYCYCLIC AROMATIC HYDROCARBONS (PAH) TEST RESULTS DISCRETE SAMPLES (Ref No: 13188/4-AA) NATIONAL ENVIRONMENT PROTECTION AMENDMENT MEASURE (2013)

TOTAL PAHs

NAPHTHALENE

NAPHTHALENE

400

3

170

0.7

2.5-2.8 sand

<0.3 <0.8 <0.1 <0.1

4

400

NL

170

0.7

BH12

0-0.15

sand

<0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH12

1.5-1.8 sand

<0.3 <0.8 <0.1 <0.1

4

400

NL

170

0.7

BH13

0-0.15

<0.3

<0.1 <0.1

4

400

3

170

0.7

400

0-0.15

BH11

sand

sand

TOTAL PAHs

4

BH11

BaP TEQ

BaP TEQ

BENZO(a)PYRENE (BaP)

Generic Ecological Ecological Screening Investigation Level (EIL) - Level (ESL) - Urban Urban residential residential

<0.1 <0.1

Sample Depth Location (m) Soil type

<0.3

1

1

NAPHTHALENE

PAH (mg/kg)

BENZO(a)PYRENE (BaP)

Health-based Investigation Health Screening Level Levels (HIL) B a(HSL) B - High density Residential B residential

BH13

1.5-1.8 sand

<0.3 <0.8 <0.1 <0.1

4

NL

170

0.7

BH14

0-0.15

sand

<0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH15

0-0.15

sand

<0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH15

0.5-0.8 sand

<0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH16

0.5-0.8 sand

<0.3 <0.8 <0.1 <0.1

4

400

3

170

0.7

BH16

1.5-1.8 sand

1.4

4

400

NL

170

0.7

11

<0.1 1

Limits of Reporting (LOR) 0.3 0.8 0.1 0.1 Notes: a: Residential w ith minimal opportunities for soil access; includes dw ellings w ith fully and permanently paved yard space such as highrise buildings and apartments. NL: Not Limimting

Nix Anderson Pty Ltd DS.sf/03.08.2015


GEOTECHNIQUE PTY LTD

(mg/kg)

(mg/kg)

Cyanides

Phenols

(mg/kg) PCB

TABLE G ORGANOCHLORINE PESTICIDES (OCP), POLYCHLORINATED BIPHENYLS (PCB), CYANIDES & PHENOLS TEST DISCRETE SAMPLES (Ref No: 13188/4-AA)

BH11

0-0.15

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.5

<5

BH11

2.5-2.8

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

-

-

BH12

0-0.15

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.5

<5

BH12

1.5-1.8

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

-

-

BH13

0-0.15

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.5

<5

BH13

1.5-1.8

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

-

-

BH14

0-0.15

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.5

<5

BH15

0-0.15

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.5

<5

BH15

0.5-0.8

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

-

-

BH16

0.5-0.8

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

<0.5

<5

BH16

1.5-1.8

<0.1 <0.1 <0.15 <0.2 <0.1 <0.1 <0.5 <0.6 <0.2 <0.2

<1

-

-

0.1

0.1

0.15

0.2

0.1

0.1

0.5

0.6

0.2

1

0.1

0.1

15

10

10

20

500

20

400

600

90

1

300

45000

Limits of Reporting (LOR)

CHLORDANE (alpha & gamma)

DDT

DDD+DDE+DDT

ENDOSULFAN (alpha, beta & sulphate)

MIREX

METHOXYCHLOR

ENDRIN

ALDRIN+DIELDRIN

Depth (m)

HEPTACHLOR

Sample Location

HEXACHLOROBENZENE (HCB)

OCP (mg/kg)

0.2

NATIONAL ENVIRONMENT PROTECTION AMENDMENT MEASURE (2013) a

Health-based Investigation Levels (HIL) B - Residential B Ecological Investigation Levels (EIL) - Urban residential Notes:

180

b

a: Residential w ith minimal opportunities for soil access; includes dw ellings w ith fully and permanently paved yard space such as high-rise buildings and apartments. b: Generic EIL for DDT

Nix Anderson Pty Ltd DS.sf/03.08.2015


GEOTECHNIQUE PTY LTD

TABLE H ASBESTOS TEST RESULTS DISCRETE SAMPLES (Ref No: 13188/4-AA) Sample Location

Depth (m)

ASBESTOS

BH11

0-0.15

No Friable Asbestos exceeded the laboratory limit of reporting of 0.001%w /w

BH11

2.5-2.8

No Friable Asbestos exceeded the laboratory limit of reporting of 0.001%w /w

BH12

0-0.15

No Friable Asbestos exceeded the laboratory limit of reporting of 0.001%w /w

BH13

0-0.15

No Friable Asbestos exceeded the laboratory limit of reporting of 0.001%w /w

BH14

0-0.15

No Friable Asbestos exceeded the laboratory limit of reporting of 0.001%w /w

BH15

0-0.15

No Friable Asbestos exceeded the laboratory limit of reporting of 0.001%w /w

BH16

0.5-0.8

No Friable Asbestos exceeded the laboratory limit of reporting of 0.001%w /w

Nix Anderson Pty Ltd DS.sf/03.08.2015


ATTACHMENT D


G EOTECHNIQUE PTY LTD

IMPORTANT INFORMATION REGARDING YOUR ENVIRONMENTAL SITE ASSESSMENT

These notes have been prepared by Geotechnique Pty Ltd, using guidelines prepared by the ASFE (Associated Soil and Foundation Engineers). The notes are offered to assist in the interpretation of your environmental site assessment report. REASONS FOR AN ENVIRONMENTAL ASSESSMENT

Environmental site assessments are typically, though not exclusively, performed in the following circumstances: As a pre-acquisition assessment on behalf of a purchaser or a vendor, when a property is to be sold As a pre-development assessment, when a property or area of land is to be redeveloped, or the land use has changed, e.g. from a factory to a residential subdivision As a pre-development assessment of greenfield sites, to establish baseline conditions and assess environmental, geological and hydrological constraints to the development of e.g. a landfill As an audit of the environmental effects of previous and present site usage Each circumstance requires a specific approach to assessment of soil and groundwater contamination. In all cases the objective is to identify and if possible quantify the risks that unrecognised contamination poses to the ongoing proposed activity. Such risks may be financial (clean-up costs or limitations in site use) and physical (health risks to site users or the public). ENVIRONMENTAL SITE ASSESSMENT LIMITATIONS

Although information provided by an environmental site assessment can reduce exposure to the risk of the presence of contamination, no environmental site assessment can eliminate the risk. Even a rigorous professional assessment might not detect all contamination within a site. Contaminants could be present in areas that were not surveyed or sampled, or migrate to areas that did not show signs of contamination when sampled. Contaminant analysis cannot possibly cover every type of contaminant that may occur; only the most likely contaminants are screened. AN ENVIRONMENTAL SITE ASSESSMENT REPORT IS BASED ON A UNIQUE SET OF PROJECT SPECIFIC FACTORS

In the following events and in order to avoid cost problems, you should ask your consultant to assess any changes in the conclusion and recommendations made in the assessment: When the nature of the proposed development is changed e.g. if a residential development is proposed, rather than a commercial development When the size or configuration of the proposed development is altered e.g. if a basement is added When the location or orientation of the proposed structure is modified When there is a change of land ownership, or For application to an adjacent site ENVIRONMENTAL SITE ASSESSMENT FINDINGS ARE PROFESSIONAL ESTIMATES

Site assessment identifies actual sub-surface conditions only at those points where samples are taken, when they are taken. Data obtained from the sampling and subsequent laboratory analyses are interpreted by geologists, engineers or scientists and opinions are drawn about the overall sub-surface conditions, the nature and extent of contamination, the likely impact on any proposed development and appropriate remediation measures. Actual conditions may differ from those inferred, because no professional, no matter how qualified and no sub-surface exploration program, no matter how comprehensive, can reveal what is hidden by earth, rock and time. The actual interface between materials may be far more gradual or abrupt than an assessment indicates. Actual conditions in areas not sampled may differ from predictions. Nothing can be done to prevent the unanticipated, however, steps can be taken to help minimise the impact. For this reason site owners should retain the services of their consultants throughout the development stages of the project in order to identify variances, conduct additional tests that may be necessary and to recommend solutions to problems encountered on site. Soil and groundwater contamination is a field in which legislation and interpretation of legislation by government departments is changing rapidly. Whilst every attempt is made by Geotechnique Pty Ltd to be familiar with current policy, our interpretation of the investigation findings should not be taken to be that of the relevant authority. When approval from a statutory authority is required for a project, approval should be directly sought. Environotes-Ed3-04/06


G EOTECHNIQUE

PTY LTD ii

Environmental Notes continued

STABILITY OF SUB-SURFACE CONDITIONS

Sub-surface conditions can change by natural processes and site activities. As an environmental site assessment is based on conditions existing at the time of the investigation, project decisions should not be based on environmental site assessment data that may have been affected by time. The consultant should be requested to advise if additional tests are required. ENVIRONMENTAL SITE ASSESSMENTS ARE PERFORMED FOR SPECIFIC PURPOSES AND CLIENTS

Environmental site assessments are prepared in response to a specific scope of work required to meet the specific needs of specific individuals e.g. an assessment prepared for a consulting civil engineer may not be adequate to a construction contractor or another consulting civil engineer. An assessment should not be used by other persons for any purpose or by the client for a different purpose. No individual, other than the client, should apply an assessment, even for its intended purpose, without first conferring with the consultant. No person should apply an assessment for any purpose other than that originally contemplated, without first conferring with the consultant. MISINTERPRETATION OF ENVIRONMENTAL SITE ASSESSMENTS

Costly problems can occur when design professionals develop plans based on misinterpretation of an environmental site assessment. In order to minimise problems, the environmental consultant should be retained to work with appropriate design professionals, to explain relevant findings and to review the adequacy of plans and specifications relative to contamination issues. LOGS SHOULD NOT BE SEPARATED FROM THE REPORT

Borehole and test pit logs are prepared by environmental scientists, engineers or geologists, based upon interpretation of field conditions and laboratory evaluation of field samples. Logs are normally provided in our reports and these would not be redrawn for inclusion in site remediation or other design drawings, as subtle but significant drafting errors or omissions may occur in the transfer process. Photographic reproduction can eliminate this problem, however, contractors can still misinterpret the logs during bid preparation if separated from the text of the assessment. Should this occur, delays and disputes, or unanticipated costs may result. To reduce the likelihood of borehole and test pit log misinterpretation, the complete assessment should be available to persons or organisations involved in the project, such as contractors, for their use. Denial of such access and disclaiming responsibility for the accuracy of sub-surface information does not insulate an owner from the attendant liability. It is critical that the site owner provides all available site information to persons and organisations, such as contractors. READ RESPONSIBILITY CLAUSES CLOSELY

An environmental site assessment is based extensively on judgement and opinion; therefore, it is necessarily less exact than other disciplines. This situation has resulted in wholly unwarranted claims being lodged against consultants. In order to aid in prevention of this problem, model clauses have been developed for use in written transmittals. These are definitive clauses, designed to indicate consultant responsibility. Their use helps all parties involved recognise individual responsibilities and formulate appropriate action. Some of these definitive clauses are likely to appear in the environmental site assessment and you are encouraged to read them closely. Your consultant will be happy to give full and frank answers to any questions you may have.

Environotes-Ed3-04/06


APPENDIX H

WATERNSW RECORDS



APPENDIX I

ENVIRONMENTAL NOTES


G EOTEC HNI QUE PTY LTD

IMPORTANT INFORMATION REGARDING YOUR ENVIRONMENTAL SITE ASSESSMENT

These notes have been prepared by Geotechnique Pty Ltd, using guidelines prepared by the ASFE (Associated Soil and Foundation Engineers). The notes are offered to assist in the interpretation of your environmental site assessment report. REASONS FOR AN ENVIRONMENTAL ASSESSMENT

Environmental site assessments are typically, though not exclusively, performed in the following circumstances:

As a pre-acquisition assessment on behalf of either a purchaser or a vendor, when a property is to be sold

As a pre-development assessment, when a property or area of land is to be redeveloped, or the land use has changed e.g. from a factory to a residential subdivision

As a pre-development assessment of greenfield sites, to establish baseline conditions and assess environmental, geological and hydrological constraints to the development of e.g. a landfill

As an audit of the environmental effects of previous and present site usage

Each circumstance requires a specific approach to the assessment of soil and groundwater contamination. In all cases the objective is to identify and if possible quantify the risks that unrecognised contamination poses to the ongoing proposed activity. Such risks may be both financial (clean-up costs or limitations in site use) and physical (health risks to site users or the public). ENVIRONMENTAL SITE ASSESSMENT LIMITATIONS

Although information provided by an environmental site assessment can reduce exposure to the risk of the presence of contamination, no environmental site assessment can eliminate the risk. Even a rigorous professional assessment may not detect all contamination within a site. Contaminants may be present in areas that were not surveyed or sampled, or may migrate to areas which did not show signs of contamination when sampled. Contaminant analysis cannot possibly cover every type of contaminant that may occur; only the most likely contaminants are screened. AN ENVIRONMENTAL SITE ASSESSMENT REPORT IS BASED ON A UNIQUE SET OF PROJECT SPECIFIC FACTORS

In the following events and in order to avoid cost problems, you should ask your consultant to assess any changes in the conclusion and recommendations made in the assessment:

When the nature of the proposed development is changed e.g. if a residential development is proposed, rather than a commercial development

When the size or configuration of the proposed development is altered e.g. if a basement is added

When the location or orientation of the proposed structure is modified

When there is a change of land ownership, or

For application to an adjacent site

ENVIRONMENTAL SITE ASSESSMENT FINDINGS ARE PROFESSIONAL ESTIMATES

Site assessment identifies actual sub-surface conditions only at those points where samples are taken, when they are taken. Data obtained from the sampling and subsequent laboratory analyses are interpreted by geologists, engineers or scientists and opinions are drawn about the overall sub-surface conditions, the nature and extent of contamination, the likely impact on any proposed development and appropriate remediation measures. Actual conditions may differ from those inferred, because no professional, no matter how qualified and no sub-surface exploration program, no matter how comprehensive, can reveal what is hidden by earth, rock and time. The actual interface between materials may be far more gradual or abrupt than an assessment indicates. Actual conditions in areas not sampled may differ from predictions. Nothing can be done to prevent the unanticipated, however, steps can be taken to help minimise the impact. For this reason site owners should retain the services of their consultants throughout the development stages of the project in order to identify variances, conduct additional tests that may be necessary and to recommend solutions to problems encountered on site. Soil and groundwater contamination is a field in which legislation and interpretation of legislation by government departments is changing rapidly. Whilst every attempt is made by Geotechnique Pty Ltd to be familiar with current policy, our interpretation of the investigation findings should not be taken to be that of the relevant authority. When approval from a statutory authority is required for a project, approval should be directly sought. Environotes-Ed3-04/06


G EOTECHNIQUE PTY LTD

ii Environmental Notes continued

STABILITY OF SUB-SURFACE CONDITIONS

Sub-surface conditions can change by natural processes and site activities. As an environmental site assessment is based on conditions existing at the time of the investigation, project decisions should not be based on environmental site assessment data that may have been affected by time. The consultant should be requested to advise if additional tests are required. ENVIRONMENTAL SITE ASSESSMENTS ARE PERFORMED FOR SPECIFIC PURPOSES AND CLIENTS

Environmental site assessments are prepared in response to a specific scope of work required to meet the specific needs of specific individuals e.g. an assessment prepared for a consulting civil engineer may not be adequate to a construction contractor or another consulting civil engineer. An assessment should not be used by other persons for any purpose or by the client for a different purpose. No individual, other than the client, should apply an assessment, even for its intended purpose, without first conferring with the consultant. No person should apply an assessment for any purpose other than that originally contemplated, without first conferring with the consultant. MISINTERPRETATION OF ENVIRONMENTAL SITE ASSESSMENTS

Costly problems can occur when design professionals develop plans based on misinterpretation of an environmental site assessment. In order to minimise problems, the environmental consultant should be retained to work with appropriate design professionals, to explain relevant findings and to review the adequacy of plans and specifications relative to contamination issues. LOGS SHOULD NOT BE SEPARATED FROM THE REPORT

Borehole and test pit logs are prepared by environmental scientists, engineers or geologists, based upon interpretation of field conditions and laboratory evaluation of field samples. Logs are normally provided in our reports and these would not be redrawn for inclusion in site remediation or other design drawings, as subtle but significant drafting errors or omissions may occur in the transfer process. Photographic reproduction can eliminate this problem, however, contractors can still misinterpret the logs during bid preparation if separated from the text of the assessment. Should this occur, delays and disputes, or unanticipated costs may result. To reduce the likelihood of borehole and test pit log misinterpretation, the complete assessment should be available to persons or organisations involved in the project, such as contractors, for their use. Denial of such access and disclaiming responsibility for the accuracy of sub-surface information does not insulate an owner from the attendant liability. It is critical that the site owner provides all available site information to persons and organisations, such as contractors. READ RESPONSIBILITY CLAUSES CLOSELY

An environmental site assessment is based extensively on judgement and opinion; therefore, it is necessarily less exact than other disciplines. This situation has resulted in wholly unwarranted claims being lodged against consultants. In order to aid in prevention of this problem, model clauses have been developed for use in written transmittals. These are definitive clauses, designed to indicate consultant responsibility. Their use helps all parties involved recognise individual responsibilities and formulate appropriate action. Some of these definitive clauses are likely to appear in the environmental site assessment and you are encouraged to read them closely. Your consultant will be happy to give full and frank answers to any questions you may have.

Environotes-Ed3-04/06


Issuu converts static files into: digital portfolios, online yearbooks, online catalogs, digital photo albums and more. Sign up and create your flipbook.