Biofouling Management Plans (BFMP) by Alpha Marine Consulting Ltd.

M/T “VSLNAME” IMO No: 9999999

BIOFOULING MANAGEMENT PLAN

ALPHA MARINE CONSULTING P.C. MARINE CONSULTANTS & SURVEYORS T: +30 211 8881000, F: +30 211 8881039 mail@alphamrn.com | www.alphamrn.com

PLAN HISTORY DESCRIPTION Issued as Final Drawing

DATE 01/01/2019

REV. 0

TOTAL THIRTY (30) SHEETS WITH COVER, EXCL. APPENDICES

CAUTION

THIS DRAWING OR DOCUMENT IS THE PROPERTY OF ALPHA MARINE CONSULTING AND IT MUST NOT BE PARTIALLY OR WHOLLY COPIED OR USED FOR ANY OTHER PURPOSE WITHOUT PRIOR WRITTEN PERMISSION OF AMC.

TITLE:

BIOFOULING MANAGEMENT PLAN

SHIP TYPE:

150,000 DWT SUEZMAX TANKER

SHIP NAME: CHECKED BY: DRAWN BY:

IMO NO.:

VSLNAME DF KA

DWG NO.: REV. NO.:

xxxx-BMP-0 0

ALPHA MARINE CONSULTING P.C.

HULL NO.:

DATE: SIZE:

8184 9999999 01/01/2019 A4

MARINE CONSULTANTS & SURVEYORS T: +30 211 8881000, F: +30 211 8881039 mail@alphamrn.com | www.alphamrn.com

M/T “VSLNAME” BIOFOULING MANAGEMENT PLAN

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AMENDMENT RECORD

Amendment Date

Description

Approved by

Amendment Number

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TABLE OF CONTENTS

PAGE INTRODUCTION ......................................................................................................5

1.1.

SCOPE .....................................................................................................................5

1.2.

GENERAL ................................................................................................................5

1.3.

DEFINITIONS...........................................................................................................6

VESSEL PARTICULARS ......................................................................................11

2.1.

GENERAL PARTICULARS ....................................................................................11

2.2.

PRINCIPAL DIMENSIONS.....................................................................................11

DESCRIPTION OF VESSEL’S ANTI-FOULING SYSTEMS .................................12

DESCRIPTION OF VESSEL’S OPERATING PROFILE .......................................13

DESCRIPTION OF VESSEL’S AREAS SUSCEPTIBLE TO BIOFOULING .........15

OPERATION & MAINTENANCE OF VESSEL’S ANTI-FOULING SYSTEM ........20

6.1.

TIMING OF OPERATIONAL AND MAINTENANCE ACTIVITIES ..........................20

6.2.

MAINTENANCE PROCEDURES DURING DRY-DOCKING .................................21

6.3.

IN-WATER CLEANING AND MAINTENANCE PROCEDURES ............................22

6.4.

OPERATION OF ONBOARD TREATMENT PROCESSES ...................................26

SAFETY PROCEDURES FOR SHIP AND CREW ................................................27

DISPOSAL OF BIOLOGICAL WASTE .................................................................28

RECORDING REQUIREMENTS ...........................................................................29

10.

CREW TRAINING AND FAMILIARIZATION .........................................................30

APPENDIX I –

DESCRIPTION OF VESSEL’S ANTI-FOULING SYSTEMS

APPENDIX II – BIOFOULING RECORD BOOK FORM APPENDIX III – DECISION SUPPORT TOOL FOR IN-WATER CLEANING APPENDIX IV – TYPES OF ANTI-FOULING COATINGS APPENDIX V – INFORMATION ON CURRENTLY AVAILABLE IN-WATER CLEANING TECHNOLOGY

APPENDIX VI – SPECIFIC CALIFORNIA STATE REQUIREMENTS APPENDIX VII – SPECIFIC NEW ZEALAND REQUIREMENTS APPENDIX VIII – RELEVANT INFORMATION

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2. INTRODUCTION

2.1.

SCOPE

This Plan has been developed pursuant to the 2011 Guidelines for the Control and Management of Ships’ Biofouling to Minimize the Transfer of Invasive Aquatic Species, Resolution MEPC.207(62), adopted on 15 July 2011, and the US Ballast Water Management Rule, 33 CFR 151.2050(g), adopted on 21 June 2012.

The latest specific requirements of California State and New Zealand have been also taken into account (refer to Appendices VI and VII respectively) when developing this Plan. The aim of this Plan is to provide effective procedures and practical guidance to the vessel’s master, operator and owner and any other interested parties, on biofouling management measures in order to minimize the risk of transferring invasive aquatic species from ships' biofouling. It is important that these biofouling management procedures be effective as well as environmentally safe, practical and designed to minimize costs and delays to the vessel.

The management measures outlined herein are intended to complement current maintenance practices carried out within the Company.

2.2.

This Plan is to be available for viewing on request by a Port State Authority and is written in the English language which is the working language of the crew. GENERAL

Studies have shown that biofouling can be a significant factor for the transfer of invasive aquatic species. Biofouling on ships may result in the establishment of invasive aquatic species which may pose threats to human, animal and plant life, economic and cultural activities and the aquatic environment.

While the International Convention on the Control of Harmful Anti-Fouling Systems on Ships, 2001 (AFS Convention) addresses anti-fouling systems on ships, its focus is on the prevention of adverse impacts from the use of anti-fouling systems and the biocides they may contain, rather than preventing the transfer of invasive aquatic species. The potential for invasive aquatic species transferred through biofouling to cause harm has been recognized by the IMO, the Convention on Biological Diversity (CBD), several UNEP Regional Seas Conventions (e.g., Barcelona Convention for the Protection of the Mediterranean Sea Against Pollution), the Asia Pacific Economic Cooperation forum (APEC), and the Secretariat of the Pacific Region Environmental Program (SPREP). All ships have some degree of biofouling, even those which may have been recently cleaned or had a new application of an anti-fouling coating system. Studies have shown that the biofouling process begins within the first few hours of a ship's immersion in water.

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The biofouling that may be found on a ship is influenced by a range of factors, such as: .1 .2 .3 .4

design and construction, particularly the number, location & design of niche areas; specific operating profile, including factors such as operating speeds, ratio of time underway compared with time alongside, moored or at anchor, and where the ship is located when not in use (e.g., open anchorage or estuarine port); places visited and trading routes; and maintenance history, including: the type, age and condition of any anti-fouling coating system, installation and operation of anti-fouling systems and drydocking/slipping and hull cleaning practices.

Implementing practices to control and manage biofouling can greatly assist in reducing the risk of the transfer of invasive aquatic species. Such management practices can also improve a ship's hydrodynamic performance and can be effective tools in enhancing energy efficiency and reducing air emissions from ships. The procedures contained herein are intended to provide useful recommendations to the ship’s crew and Company personnel on general measures to minimize the risks associated with biofouling for this particular ship.

2.3.

To minimize the transfer of invasive aquatic species, the ship should implement biofouling management practices, including the use of anti-fouling systems and other operational management practices to reduce the development of biofouling. The intent of such practices is to keep the ship's submerged surfaces, and internal seawater cooling systems, as free of biofouling as practical. Following this Plan and minimizing macrofouling would have a reduced potential for transferring invasive aquatic species via biofouling. DEFINITIONS

Adequate documentation means records of the recent history of anti-fouling installation and hull maintenance undertaken on a ship or movable structure. AFS Convention means the International Convention on the Control of Harmful AntiFouling Systems on Ships, 2001.

Anti-fouling coating means a coating used on a vessel to prevent or reduce the accumulation of biofouling. Common types of anti-fouling coating are described in Appendix IV.

Anti-fouling coating system means the combination of all component coatings, surface treatments (including primer, sealer, binder, anti-corrosive and anti-fouling coatings) or other surface treatments, used on a vessel to control or prevent attachment of unwanted aquatic organisms. Anti-fouling system means a coating, paint, surface treatment, surface, or device that is used on a vessel to control or prevent attachment or association of unwanted organisms and / or biofouling.

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Anti-fouling System (AFS) Certificate means the International Anti-fouling System Certificate that ships greater than 400 gross tonnes and registered to a Flag State that is a Party to the AFS Convention, 2001 are required to carry. This certificate indicates that the ship’s anti-fouling system complies with the Convention. Biocide means a chemical substance that is incorporated into anti-fouling coatings to prevent the settlement or survival of aquatic organisms. Biofouling, also referred to as hull fouling or marine growth, means the accumulation of aquatic organisms such as micro-organisms, plants, and animals on surfaces and structures immersed in or exposed to the aquatic environment, including, but not limited to, sea chests, propellers, anchors and associated chains, and other niche areas. Biofouling can include microfouling and macrofouling (see below).

Biosecurity means the exclusion, eradication or effective management of pests and diseases that threaten the economy, environment, human health, social and cultural values. Biosecurity risk means the potential harm to the economy, environment, human health and social and cultural values posed by pests and diseases entering, emerging, establishing or spreading.

Contaminant means any undesirable substance occurring in the environment as a result of human activities, without adverse effects being observed.

Contamination means the presence of a contaminant in the environment, or the process whereby a contaminant is introduced into the environment. Controlled waste means material or liquid waste that is regulated because of its toxicity or imminent hazardous nature.

Declaration on Anti-fouling System means the declaration required to be carried by vessels of less than 400 gross tonnes but greater than 24m, and registered to a Flag State that is Party to the AFS Convention, 2001. This declaration ensures that their anti-fouling coating system complies with the Convention.

Exclusive Economic Zone (EEZ) means those waters beyond the limits of the Territorial Sea out to 200 nautical miles. In-water cleaning means the physical removal of biofouling and / or anti-fouling coating surface deposits from a ship while in the water. In-water inspection means underwater survey or inspection by divers (including inspections conducted with remotely operated vehicles). Inspections for purposes other than surveying biofouling may be considered opportunities for evaluating biofouling extent. In-water treatment means any method or process that is aimed at sterilizing biofouling from the wetted portions of a vessel while the vessel remains in the water. Invasive aquatic species means a species which may pose threats to human, animal and plant life, economic and cultural activities and the aquatic environment.

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Local water quality standards means the concentrations or discharge of contaminants (such as those arising from hull maintenance operations) that are regarded as acceptable by the relevant authority. Maintenance facility refers to any location or facility where on-shore maintenance of ships is carried out. This includes the maintenance, removal and application of anti-fouling coatings and the removal of biofouling organisms. Marine Growth Prevention System (MGPS) means an anti-fouling system used for the prevention of biofouling accumulation in internal seawater cooling systems and sea chests and can include the use of anodes, injection systems and electrolysis. Member States means States that are Members of the International Maritime Organization.

Macrofouling means large, distinct multicellular organisms visible to the human eye such as barnacles, tubeworms, or fronds of algae and other large attached or mobile organisms.

Microfouling means microscopic organisms including bacteria and diatoms and the slimy substances that they produce. Biofouling comprised of only microfouling is commonly referred to as a slime layer and can be usually removed by gently passing a finger over the surface.

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Niche areas mean areas on a vessel that may be more susceptible to biofouling due to different hydrodynamic forces, susceptibility to coating system wear or damage, or being inadequately, or not, painted, e.g., sea chests, bow thrusters, propeller shafts, inlet gratings, dry-dock support strips, etc. Organization means the International Maritime Organization. Out-of-water maintenance means removal of the vessel from the water and into a dry-dock or slipway for inspection or maintenance.

Out-of-water support strips means sections of the hull that rested on support blocks while the vessel was out of water in a dry-dock or slipway. These areas are typically not cleaned or treated with fresh anti-fouling systems, resulting in reduced antifouling protection. Percentage cover means the percentage of the total surface area under examination that is occupied by biofouling.

Planned in-service period means the intended interval (decided at the time of antifouling coating application) until the next scheduled application of anti-fouling coating on a vessel.

Port State authority means any official or organization authorized by the Government of a port State to verify the compliance and enforcement of standards and regulations relevant to the implementation of national and international shipping control measures. Relevant authority means the authority that has responsibility for managing the environmental effects of activities.

Service life means the period of time an anti-fouling coating system is expected to protect a treated surface from biofouling and/or corrosion if the coatings are applied in accordance with the manufacturer’s specifications.

Ship means a vessel of any type whatsoever operating in the aquatic environment and includes hydrofoil boats, air-cushion vehicles, submersibles, floating craft, fixed or floating platforms, floating storage units (FSUs) and floating production storage and off-loading units (FPSOs). Statement of Compliance means a document (and associated evidence) issued by a Classification Society to ships greater than 400 gross tonnes that are registered in Flag States not Party to the AFS Convention, 2001. States means coastal, port or Member States as appropriate. Treatment means a process which may use a mechanical, physical, chemical or biological method to remove or render sterile, invasive or potentially invasive aquatic species fouling a ship.

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Waterline means the area along the external hull of a vessel where the surface of the water interfaces with the air. The waterline is not a fixed location; its placement is dependent on loading and ballasting operations.

Wetted portion of a vessel means all parts of a vessel’s hull and structures that are either submerged in water when the vessel is loaded to the deepest permissible legal draft or associated with internal piping structures in contact with water taken onboard.

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3. VESSEL PARTICULARS

3.1.

GENERAL PARTICULARS

Ship’s Name:

VSLNAME

Ship’s Type: Flag: Port of Registry:

Call Sign: MMSI: IMO Number: Gross Tonnage: Net Tonnage: Built by:

3.2.

Year Built: PRINCIPAL DIMENSIONS

Length O.A.: Length B.P.:

Breadth (mld.):

Depth to Main Deck (mld.):

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9999999

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4. DESCRIPTION OF VESSEL’S ANTI-FOULING SYSTEMS

Anti-fouling systems and operational practices are the primary means of biofouling prevention and control for existing vessels' submerged surfaces, including the hull and niche areas. An anti-fouling system can be a coating system applied to exposed surfaces, biofouling resistant materials used for piping and other unpainted components, marine growth prevention systems (MGPSs) for sea chests and internal seawater cooling systems, or other innovative measures to control biofouling.

  

type(s) of anti-fouling coating systems applied; details of where anti-fouling systems are and are not applied or installed; manufacturer and product names of all coatings or products used in the anti-fouling coating systems; and anti-fouling system specifications (including dry film thickness for coatings, dosing and frequency for MGPSs, etc.) together with the expected effective life, operating conditions required for coatings to be effective, cleaning requirements and any other specifications relevant for paint performance



Details for the anti-fouling systems in place for different parts of the vessel, including as follows:

are set out / referred to in Appendix I.

Previous reports on the performance of the vessel's anti-fouling systems, the AFS certificate or statement of compliance or other documentation are included in Appendix VI or in the vessel’s Certificates File. It is noted that the anti-fouling system used complies with the AFS Convention.

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5. DESCRIPTION OF VESSEL’S OPERATING PROFILE

The vessel's operating profile that has determined the performance specifications of the vessel's anti-fouling systems and operational practices is described below:

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6. DESCRIPTION OF VESSEL’S AREAS SUSCEPTIBLE TO BIOFOULING

The hull areas, niche areas and seawater cooling systems on the vessel that are particularly susceptible to biofouling (including access points in the internal seawater cooling systems) are identified in the diagram below.

Rudder Propeller

SW Cool. System

Drydocking support strips

Sea Chest

Bow Thruster

Drydocking support strips

Bilge Keel

SW Cool. System

Sea Chest Propeller Rudder

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Bow Thruster

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The management actions required for each area and the actions to be taken if the vessel is operating outside of the desired operating profile, or if excessive unexpected biofouling is observed, and any other actions that can be taken to minimize the accumulation of biofouling on the vessel are described in the action plan provided below: Biofouling Management Action Plan Areas of the vessel which are particularly susceptible to biofouling

Management actions to be undertaken if vessel operates outside its usual operating profile

External hull surfaces: - Vertical sides - Flats - Boottop - Bow dome - Transom

Management actions required for each area (e.g., inspections, cleaning, repairs and maintenance)

Plans / diagrams of the vessel identifying relevant locations: Hull appendages and fittings: - Bilge keels - Echo sounder probes - A-brackets - Stabilizer fins - CP anodes Plans / diagrams of the vessel identifying relevant locations: Steering and propulsion: - Propeller

Plans / diagrams of the vessel identifying relevant locations:

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Areas of the vessel which are particularly susceptible to biofouling

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Management actions required for each area (e.g., inspections, cleaning, repairs and maintenance)

Management actions to be undertaken if vessel operates outside its usual operating profile

Plans / diagrams of the vessel identifying relevant locations: - Anchor chain

- Stern tube seal

Plans / diagrams of the vessel identifying relevant locations: - Chain locker

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Areas of the vessel which are particularly susceptible to biofouling

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Management actions required for each area (e.g., inspections, cleaning, repairs and maintenance)

Management actions to be undertaken if vessel operates outside its usual operating profile

- Rope guard

- Rudder

Plans / diagrams of the vessel identifying relevant locations: - Bow / Stern thrusters - Propeller - Thruster body - Tunnel - Tunnel grates

Plans / diagrams of the vessel identifying relevant locations: ALPHA MARINE CONSULTING

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Seawater intakes and internal seawater cooling systems: - Engine cooling system - Sea chests (identify number and position) - Sea chest grate - Internal pipework and heat exchanger - Fire-fighting system - Ballast uptake system - Auxiliary services system

Management actions required for each area (e.g., inspections, cleaning, repairs and maintenance)

Plans / diagrams of the vessel identifying relevant locations:

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Management actions to be undertaken if vessel operates outside its usual operating profile

Areas of the vessel which are particularly susceptible to biofouling

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7. OPERATION & MAINTENANCE OF VESSEL’S ANTI-FOULING SYSTEM

This Section contains a detailed description of the operation and maintenance of the antifouling system(s) used, including schedule(s) of activities and step-by-step operational procedures. 7.1.

TIMING OF OPERATIONAL AND MAINTENANCE ACTIVITIES

This Section stipulates the schedule of planned inspections, repairs, maintenance and renewal of the anti-fouling systems.

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7.2.

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MAINTENANCE PROCEDURES DURING DRY-DOCKING

When re-installing or repairing the anti-fouling system, care should be taken in surface preparation to ensure all biofouling residues, flaking paint, or other surface contamination is completely removed, particularly in niche areas, to facilitate good adhesion and durability of the anti-fouling system

For sea chests the following should be considered when re-installing or repairing their antifouling systems:

Other niche areas can also be particularly susceptible to biofouling growth. Management measures for niche areas are outlined below.

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7.3.

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IN-WATER CLEANING AND MAINTENANCE PROCEDURES

Despite the use of effective anti-fouling systems and operational practices, undesirable amounts of biofouling may still accumulate during the intended lifetime of the anti-fouling system. To maintain the vessel as free of biofouling as practical, it may be advisable for the vessel to undertake in-water inspection, cleaning and maintenance.

6.3.1. In-water inspection

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6.3.2. In-water cleaning and maintenance

Hull cleaning should be carried out based on a condition assessment basis and if there is significant growth on the hull (see below note), an immediate decision to clean the hull should be made taking into account the inspection report / notification by the Master.

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6.3.3. In-water inspection / cleaning reports

Divers’ reports (including photographic / video material) should be kept both in the Company and onboard.

6.3.4. Extended stay at port or anchorage

When waiting at a port or anchorage for long periods (i.e. for ninety (90) days or longer), the vessel should - at least every two weeks - sail at normal speed for a couple of hours to reduce biofouling accumulation.

6.3.5. Procedures for Sediment Removal

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Sediment control and removal methods Tank

Bottom Flush

Water Jet

De-Mucking

Fore Peak SBT Double Bottom

After Peak

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OPERATION OF ONBOARD TREATMENT PROCESSES

7.4.

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8. SAFETY PROCEDURES FOR SHIP AND CREW

The following table provides a non-exhaustive list of possible areas with associated risks and the precautions to be taken by the ship’s crew.

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9. DISPOSAL OF BIOLOGICAL WASTE

The disposal of biological waste generated by the cleaning process when the cleaning is conducted by or under the direct supervision of the shipowner, Master or crew should be consistent with applicable national and local laws and regulations, so that viable (able to take root and grow / likely to survive) biofouling or chemical and physical pollutants are not released into the local aquatic environment where they may cause harm.

The Master and the crew should make every effort to minimize the release of organisms into the local environment and ensure that adequate measures are adopted when cleaning immersed areas coated with biocidal anti-fouling coatings, so as to prevent the premature depletion of the anti-fouling coating system and the creation of a pulse of biocides that can harm the local environment.

In general the Master and crew should adhere to the following measures:

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10. RECORDING REQUIREMENTS

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11. CREW TRAINING AND FAMILIARIZATION

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APPENDIX I – DESCRIPTION OF VESSEL’S ANTI-FOULING SYSTEMS

APPENDIX II â&#x20AC;&#x201C; BIOFOULING RECORD BOOK FORM

BIOFOULING RECORD BOOK Page 1 of ____ Ship’s Name:

VSLNAME

Ship’s Type: Flag: Port of Registry: Registry Number: Call Sign: IMO Number:

9999999

Gross Tonnage: Net Tonnage:

The ship is provided with a Biofouling Management Plan

Diagram of ship indicating underwater hull form and recognized biofouling niches: Rudder

Propeller

P Bow Thruster

SW Cool. System

Sea Chest

Bilge Keel Bilge Keel

SW Cool. System

Sea Chest Propeller Rudder

Bow Thruster

BIOFOULING RECORD BOOK Page 2 of ____ Guidelines for completing the Biofouling Record Book 1.

Introduction

The IMO â&#x20AC;&#x153;Guidelines for the control and management of ships' biofouling to minimize the transfer of invasive aquatic speciesâ&#x20AC;? adopted by Res. MEPC.207(62) on 15 July 2011 recommend that a Biofouling Record Book is maintained for each ship, in which should be recorded the details of all inspections and biofouling management measures undertaken on the ship. 2.

Entries in the Biofouling Record Book

The following information should be recorded in the Biofouling Record Book:

After each dry-docking: a. Date and location that the ship was dry-docked. b. Date that ship was re-floated. c. Any hull cleaning that was performed while dry-docked, including areas cleaned, method used for cleaning and the location of dry-dock support blocks. d. Any anti-fouling coating system, including patch repairs, that was applied while drydocked. Detail the type of anti-fouling coating system, the area and locations it was applied to, the coating thickness achieved and any surface preparation work undertaken (e.g., complete removal of underlying anti-fouling coating system or application of new anti-fouling coating system over the top of existing anti-fouling coating system). e. Name, position and signature of the person in charge of the activity for the ship.

2.2

When the hull area, fittings, niches and voids below the waterline have been inspected by divers: a. Date and location of ship when dive surveyed and reason for survey. b. Area or side of the ship surveyed. c. General observations with regard to biofouling (i.e. extent of biofouling and predominant biofouling types, e.g., mussels, barnacles, tubeworms, algae and slime). d. What action was taken, if any, to remove or otherwise treat biofouling. e. Any supporting evidence of the actions taken (e.g., report from the classification society or contractor, photographs and receipts). f. Name, position, signature of the person in charge of the activity.

2.1

2.3

When the hull area, fittings, niches and voids below the waterline have been cleaned by divers: a. Date and location of ship when cleaning / treatment occurred. b. Hull areas, fittings, niches and voids cleaned/treated. c. Methods of cleaning or treatment used. d. General observations with regard to biofouling (i.e. extent of biofouling and predominant biofouling types, e.g., mussels, barnacles, tubeworms, algae and slime). e. Any supporting evidence of the actions taken (e.g., report from the classification society or contractor, photographs and receipts). f. Records of permits required to undertake in-water cleaning if applicable. g. Name, position and signature of the person in charge of the activity.

BIOFOULING RECORD BOOK Page 3 of ____ Guidelines for completing the Biofouling Record Book (contâ&#x20AC;&#x2122;d) When the internal seawater cooling systems have been inspected and cleaned or treated: a. Date and location of ship when inspection and/or cleaning occurred. b. General observations with regard to biofouling of internal seawater cooling systems (i.e. extent of biofouling and predominant biofouling types, e.g., mussels, barnacles, tubeworms, algae, slime). c. Any cleaning or treatment undertaken. d. Methods of cleaning or treatment used. e. Any supporting evidence of the actions taken (e.g., report from the classification society or contractor, photographs and receipts). f. Name, position and signature of the person in charge of the activity.

2.5

For ships with a MGPS fitted: a. Records of operation and maintenance (such as regularly monitoring the electrical and mechanical functions of the systems). b. Any instances when the system was not operating in accordance with the biofouling management plan.

2.6

Periods of time when the ship was laid up / inactive for an extended period of time: a. Date and location where ship was laid up. b. Date when ship returned to normal operations. c. Maintenance action taken prior to and following the period laid up. d. Precautions taken to prevent biofouling accumulation (e.g., sea chests blanked off).

2.7

Periods of time when ship operating outside its normal operating profile: a. Duration and dates when ship not operating in accordance with its normal operating profile. b. Reason for departure from normal operating profile (e.g., unexpected maintenance required).

2.4

Details of official inspection or review of ship biofouling risk (for ships arriving internationally, if applicable): a. Date and location of ship when inspection or review occurred. b. Port State authority conducting the inspection/review and details of procedures followed or protocol adhered to and inspector/s involved. c. Result of inspection / review. d. Name, position, signature of the person in charge of the activity for the ship.

2.8

2.9

Any additional observations and general remarks: a. Since the ship was last cleaned, has the ship spent periods of time in locations that may significantly affect biofouling accumulation (e.g., fresh water, high latitude (Arctic and Antarctic) or tropical ports).

BIOFOULING RECORD BOOK Page 4 of ____ EXAMPLES OF BIOFOULING RECORD BOOK ENTRIES HULL INSPECTION Date 20 Feb 2012

Item (number) 2.2.a

Record of management actions

2.2.b 2.2.c 2.2.d 2.2.e 2.2.f PROPELLER CLEANING

20 Apr 2012

Item (number) 2.3.a

Signature of officers in charge

2.3.b 2.3.c 2.3.d 2.3.e 2.3.f 2.3.g

Record of management actions

Date

Signature of officers in charge

WEEKLY MGPS INSPECTION Date

20 Jun 2012

Item (number) 2.5.a

Record of management actions

Signature of officers in charge

BIOFOULING RECORD BOOK Page 5 of ____ Item (number)

Record of management actions

Signature of officers in charge

Date

Signature of Master

________________________________

APPENDIX III – DECISION SUPPORT TOOL FOR IN-WATER CLEANING

This Decision Support Tool for in-water cleaning is designed to assist relevant authorities with making decisions about in-water cleaning practices in their jurisdictions. The Decision Support Tool also helps owners or operators of ships and other movable structures to determine the types of information and documentation that relevant authorities may require of them to make decisions on in-water cleaning. Relevant authorities may require additional information for their risk-assessment and decision making processes. Persons who wish to in-water clean ships or movable structures must contact the relevant authority.

(a) (b) (c)

If the type of a coating (e.g. biocidal; biocide-free) cannot be reliably determined, then it should be assumed that the coating contains biocides. If the age of a coating cannot be reliably determined, then it should be assumed that the coating has reached the end of its service life. Where the type of biofouling on a ship or structure is unknown, it should be assumed that macrofouling is present. If the origin of the biofouling on a ship or movable structure is unknown, then it should be assumed that it is of international origin. If the biofouling is likely to be from more than one origin category (e.g. regional and international) then decisions on in-water cleaning should be based on the furthest likely origin (i.e. international).

(d)

When information and/or documentation required for making decisions on in-water cleaning is not available, the following default assumptions apply:

The Decision Support Tool should be used in conjunction with the following recommendations: Microfouling, regardless of origin, may be removed without the need for full containment of biofouling waste, provided the cleaning method is consistent with the coating manufacturer’s recommendations. Where microfouling is removed using a gentle, nonabrasive cleaning technique, the contamination risk is likely to be acceptable.

Macrofouling of regional origin (as defined by relevant authority) may be removed without the need for full containment of biofouling waste provided the cleaning method is consistent with the coating manufacturer’s recommendations and contaminant discharges meet local water quality standards. Macrofouling of domestic origin may be removed without the need for full containment of biofouling waste following risk assessment by the relevant authority. If the relevant authority determines containment of biofouling waste is required, then methods should be used to ensure that unacceptable amounts of biological material are not released into the water column. In-water cleaning technologies should aim to, at least, capture debris greater than 50 µm in diameter which will minimise the release of viable adult, juvenile and larval stages of macrofouling organisms. Any cleaning debris collected must be disposed of on land and in compliance with the waste disposal requirements of the relevant authority. In either case, the cleaning method must be consistent with the coating manufacturer’s recommendations and contaminant discharges must meet local water quality standards.

Macrofouling derived from international locations should only be removed using cleaning methods that are able to minimise the release of all organisms, or parts of organisms, and antifouling coating debris, using the guidance described above. The cleaning method must be consistent with the coating manufacturer’s recommendations and contaminant discharges must meet local water quality standards.

S A

APPENDIX IV – TYPES OF ANTI-FOULING COATINGS

Biocidal coatings are coatings that release chemicals such as copper compounds or other pesticides that aim to deter biofouling organisms. There are four general types of biocidal coatings: Soluble matrix, Controlled depletion polymer or Ablative anti-fouling coatings contain a binder that is slightly soluble in seawater. Hydration causes the coating surface to slowly dissolve, releasing the freely associated biocide.

Insoluble matrix, Contact leaching, Longlife or Diffusion anti-fouling coatings use an insoluble binder that contains a high concentration of biocide that is released from the coating through a diffusion process.

Self-polishing copolymer anti-fouling coatings release biocides as a result of hydrolysis causing the coating to “erode” when a vessel is moving.

Metallic anti-fouling coatings use copper or copper nickel alloy as either metal sheathing or metal particles mixed into a coating.

Biocide-free coatings are coatings that do not depend on chemicals or pesticides for their anti-fouling properties, instead relying on their physical nature. They are further split into two sub-categories: Fouling release coatings rely on non-stick, low surface energy compounds such as silicone or fluoropolymers to impair the adhesive attachment of biofouling.

Mechanically resistant coatings (epoxy, ceramic/epoxy, and epoxy/glass) are tough and highly durable coatings. They do not have any anti-fouling properties. They allow biofouling organisms to accumulate and are designed to withstand regular in-water cleaning (including abrasive methods).

APPENDIX V – INFORMATION ON CURRENTLY AVAILABLE IN-WATER CLEANING TECHNOLOGY

The most commonly available in-water cleaning technologies are currently brushing/scraping, use of soft cleaning tools, and water or air jet systems. These methods vary in their effectiveness in removing and containing biofouling organisms, and in their suitability for use on different anti-fouling coating types. Brief descriptions of their use and limitations are provided below: Brush systems - Brushes are a widely used method for in-water hull cleaning because of their ability to remove surface deposits and low levels of biofouling from biocidal coatings. They can have a rejuvenating effect on the performance of some coating types. Existing brush systems are not able to remove all biofouling from a surface or contain all of the removed material. The use of abrasive brushes can also result in the exacerbated release of biocidal coating material. Use of brushes on fouling-release coatings can damage the coating surface and is not recommended unless the brushes are sufficiently soft and will not harm the integrity of the coating. Advice should be sought from the coating manufacturer or supplier prior to using any brush system on an anti-fouling coating.

•

Soft tools - Fouling release coatings prevent firm attachment of biofouling organisms. Soft cleaning tools, such as cloths, squeegees and wiping tools can be used to remove micro and macrofouling effectively from surfaces coated in fouling release coatings without harming the integrity of the coating. These coatings are delicate and scratching of the surface should be avoided. If cloths are used for cleaning, it is necessary to ensure that no shell fragments or other hard objects are trapped beneath the cloths that could scratch and damage the coatings.

•

Water jet and air jet (blast) systems - Water and air jet cleaning systems are versatile tools because their operating pressure (and jet pattern) can be varied according to coating type and biofouling extent. The effects of water jet technology on biocidal coatings are not fully understood. Currently available water jet systems are not able to contain all of the removed biofouling or coating material. Water pressures should be used that do not harm the integrity of the anti-fouling coating.

•

Other technologies:

•

Technologies that kill, but not necessarily remove biofouling - Several types of biofouling treatment are available that kill biofouling organisms but do not actively remove them from a surface. These include the use of heat (in the form of steam or heated water) or enveloping technologies (wrapping of a vessel or movable structure in plastic sheets or canvas sleeves to suffocate biofouling). These are generally developing technologies and their effectiveness and effects on anti-fouling coatings have not been evaluated.

•

Developing technologies - A number of technologies that collect biofouling and coating material are under development.

APPENDIX VI – SPECIFIC CALIFORNIA STATE REQUIREMENTS This Appendix contains the additional requirements related to Biofouling Management according to the California State Regulations “Biofouling Management to Minimize the Transfer of Nonindigenous Species from Vessels Arriving at California Ports” (California Code of Regulations Title 2, Division 3, Chapter 1, Article 4.8). 1.

Application

The provisions described in this Appendix apply to newly constructed vessels delivered on or after 1 January 2018, and to existing vessels beginning with completion of the first regularly scheduled out-of-water maintenance on or after 1 January 2018. The Marine Invasive Species Program Annual Vessel Reporting Form (see Section 8. below) became effective from 1 October 2017. Definitions

An anti-fouling coating containing one or more chemical substances that are toxic or act as a deterrent to the settlement of living organisms.

CCR:

California Code of Regulations.

Commission staff:

Staff of the California State Lands Commission.

Division Chief:

The Chief of the Marine Environmental Protection Division of the California State Lands Commission or any employee of the Marine Environmental Protection Division authorized by the Division Chief to act on her or his behalf.

Effective coating lifespan:

The expected age of an anti-fouling coating, as determined by the manufacturer and based on the vessel-specific application scheme (e.g. coating thickness) at the time of application, at which the coating is no longer expected to satisfactorily prevent or deter biofouling.

Biocidal anti-fouling coating:

Remaining in one port consecutively for forty-five days or longer.

Foul-release coating:

A non-biocidal anti-fouling coating with surface properties that minimize the adhesion of biofouling organisms, resulting in organism detachment by vessel movement.

Geographic location:

A port, anchorage, city and country, or latitude and longitude coordinates.

Non-biocidal anti-fouling coating:

An anti-fouling coating that does not rely on one or more chemical substances intended to be toxic or act as a deterrent to organism settlement in order to achieve its anti-fouling properties. Nonbiocidal anti-fouling coatings may include foul-release coatings.

Extended residency period:

Obviously excessive biofouling:

Macrofouling percentage cover significantly in excess of fifteen percent of the wetted surface under investigation, as determined using the biofouling compliance assessment protocols. Filamentous or turf algae on the bulbous bow and at the waterline, including one meter above and one meter below the waterline, shall be excluded from this calculation.

Out-of-water support blocks:

Support blocks placed underneath the vessel while the vessel is undergoing out-of-water maintenance in a dry dock or slipway.

Port:

Any port or place in which a vessel was, is, or will be anchored or moored, or where a vessel will transfer cargo.

Vessel:

A vessel of 300 gross registered tons (GRT) or more.

Application of Biofouling Management

3.1. Biofouling Management shall apply to the following niche areas, if present:  Sea chests  Sea chest gratings  Bow and stern thrusters  Bow and stern thruster gratings  Fins stabilizers and recesses  Out-of-water support strips  Propellers and propeller shafts  Rudders

All niche area management practices to be employed as part of the overall biofouling management strategy shall be listed in the Biofouling Management Plan, as required by 2 CCR § 2298.3(b)(2).

(a)

3.2. Biofouling in niche areas must be managed using one or more biofouling management practices that are appropriate for the vessel and its operational profile, as determined by the master, owner, operator, or person in charge of a vessel, and subject to the following conditions:

All completed niche area management practices shall be documented in the Biofouling Record Book, as required by 2 CCR 2298.4(b)(2).

(c)

If any of the niche area management practices listed in the Biofouling Management Plan are not conducted as planned, the reason(s) why the practice(s) were not conducted shall be documented in the Biofouling Record Book.

(b)

Biofouling Management Plan – Additional California Requirements

4.1. The master, owner, operator, or person in charge of the vessel (carrying, or capable of carrying, ballast water) calling at a California port shall maintain a ship-specific Biofouling Management Plan onboard. Upon request, the plan shall be made available to Commission staff for inspection and review. This plan shall provide a description of the biofouling management strategy for the vessel that is sufficiently detailed to allow a master or other appropriate ship's officer or crew member serving on that vessel to understand and follow the biofouling management strategy. The plan to be regularly reviewed and revised to be current as of the last day of the most recent out-of-water maintenance or delivery if the vessel has never undergone out-of-water maintenance.

4.2. If a vessel does not have a Biofouling Management Plan, and is arriving at a California port for the first time since the most recent regularly scheduled out-of-water maintenance or since delivery as a newly constructed vessel if no out-of-water maintenance has yet occurred, there shall be a 60-day grace period commencing on the date of arrival to enable the development of the required documents.

Biofouling Record Book – Additional California Requirements

5.1. The master, owner, operator, or person in charge of the vessel that arrives at a California port shall maintain a Biofouling Record Book to be retained onboard the vessel. The Biofouling Record Book must contain details of all inspections and biofouling management measures undertaken on the vessel since the beginning of the most recent scheduled out-of-water maintenance or since delivery into service as a newly constructed vessel if no out-of-water maintenance has yet occurred.

5.2. If a vessel does not have a Biofouling Record Book consistent with the requirements of subdivisions (a) and (b) of this section and is arriving at a California port for the first time since the most recent regularly scheduled out-of-water maintenance or since delivery as a newly constructed vessel if no out-of-water maintenance has yet occurred, there shall be a 60-day grace period commencing on the date of arrival to enable the development of the required documents. During the 60-day grace period, the master, owner, operator, or person in charge of a vessel subject to this subdivision shall: (a) Maintain records containing details of all inspections and biofouling management measures undertaken on the vessel since the beginning of the most recent regularly scheduled out-of-water maintenance or since delivery into service as a newly constructed vessel if no out-of-water maintenance has yet occurred; and

(b) Make the records described in 2 CCR § 2298.4(c)(1) available to Commission staff upon request. Marine Invasive Species Program Annual Vessel Reporting Form

All vessels of 300 gross tons or more (carrying, or capable of carrying, ballast water) calling at a California Port, should submit a completed “Marine Invasive Species Program Annual Vessel Reporting Form”, starting from 1 October 2017. This form should be submitted to the below address of Commission, in written or electronic form, at least twenty-four hours in advance of the first arrival of each calendar year at a California port of call: California State Lands Commission Marine Environmental Protection Division 200 Oceangate, Suite 900 Long Beach, CA 90802 or fax: 562-499-6444 or e-mail: bwform@slc.ca.gov

MARINE INVASIVE SPECIES PROGRAM ANNUAL VESSEL REPORTING FORM

Vessel Name: Official / IMO Number: Responsible Officer’s Name and Title: Date Submitted (Day/Month/Year): Does the vessel have a ballast water treatment system installed?

Yes No

If “YES” Complete sections 1 and 2 If “NO” Complete section 1 only

Section 1: 2.

Hull Husbandry Maintenance and Operational Information

Since delivery, has this vessel ever been removed from the water for maintenance?

Yes a)

If Yes, enter the date and location of the most recent out-of-water maintenance:

Last date out of water (Day/Month/Year): Port or Position:

If No, enter the delivery date and location where the vessel was built:

Delivery date (Day/Month/Year): Port or Position:

Country:

Were the submerged portions of the vessel coated with an anti-fouling treatment or coating during the out-of-water maintenance or shipbuilding process listed above?

Country:

Date last full coat applied (Day/Month/Year) Date last full coat applied (Day/Month/Year)

Yes, partial coat No coat applied

Official / IMO Number:

For the most recent full coat application of anti-fouling treatment, what type of anti-fouling treatment was applied and to which specific sections of the submerged portion of the vessel was it applied?

Manufacturer/Company: Product Name: Applied on (Check all that apply):

Sea Chests Rope Guard/ Propeller Shaft Rudder

Hull Sides Hull Bottom Sea Chest Propeller Gratings Thrusters Bilge Keels Previous Docking Blocks

Were the sea chests inspected and/or cleaned during the out-of-water maintenance listed above? If no out-of-water maintenance was performed since delivery, select Not Applicable.

Check all that apply Yes, sea chests inspected No, sea chests not inspected or cleaned 6.

Sea Chests Rope Guard/ Propeller Shaft Rudder

Hull Bottom Hull Sides Sea Chest Propeller Gratings Bilge Keels Thrusters Previous Docking Blocks

Manufacturer/Company: Product Name: Applied on (Check all that apply):

Sea Chests Rope Guard/ Propeller Shaft Rudder

Hull Bottom Hull Sides Sea Chest Propeller Gratings Thrusters Bilge Keels Previous Docking Blocks

Yes, sea chests cleaned Not Applicable

Are Marine Growth Protection Systems (MGPS) installed in the sea chest(s) or sea strainer(s)?

Yes Manufacturer: If Yes, MGPS installed in (check all that apply): No

Model: Sea Chest(s)

Sea strainer(s)

Official / IMO Number:

Has the vessel undergone in-water cleaning to the submerged portions of the vessel since the last out-of-water maintenance Yes period? No

a) If Yes, when and where did the vessel most recently undergo in-water cleaning? (Do not include cleaning performed during out-of-water maintenance period)

Propeller

Sea Chest

Bilge Keels

Docking Blocks

Thrusters

Robotic

Both

Has the propeller been polished since the last out-of-water maintenance (including shipbuilding process) or in-water cleaning?

Yes No 9.

Hull Bottom

Date last full coat applied (Day/Month/Year)

Country:

Date (Day/Month/Year): Port or Position: Vendor providing cleaning service Section(s) cleaned Hull Sides (Check all that apply): Sea Chest Grating Rudder Unknown Cleaning method Divers

Are the anchor and anchor chains rinsed during retrieval?

Yes

10. List the following information for this vessel averaged over the last four months

a. Average Voyage Speed (knots): b. Average Port Residency Time (hours or days):

Hours or

11. Since the hull was last cleaned (out-of-water or in-water), has the vessel visited:

a. Fresh water ports (Specific gravity of less than 1.005)? Yes How many times? No

b. Tropical ports (between 23.5oS and 23.5oN latitude)? Yes How many times? No c. Panama Canal? Yes How many times? No

Official / IMO Number:

Days

12. List the previous 10 ports visited by this vessel in the order they were visited (start with most recent). You do not have to use all 10 spaces if the vessel has a regular route that involves less than 10 ports. Check here

if the vessel visits the same ports on a regular route.

List dates as (Day/Month/Year). Country: Departure date:

Port or Position: Arrival date:

Country: Departure date:

Port or Position: Arrival date:

Country: Departure date:

Port or Position: Arrival date:

Country: Departure date:

Port or Position: Arrival date:

Country: Departure date:

Port or Position: Arrival date:

Country: Departure date: Country: Departure date:

Port or Position: Arrival date:

Country: Departure date:

Port or Position: Arrival date:

Country: Departure date:

Port or Position: Arrival date:

Country: Departure date:

Port or Position: Arrival date:

Official / IMO Number:

13. Since the most recent hull cleaning (out-of-water or in-water) or delivery, has the vessel spent 10 or more consecutive days in any single location? (Do not include time out-ofwater or during in-water cleaning.) No

Indicate the longest amount of time spent in a single location since the last hull cleaning Date of Arrival: Country:

Number of Days: Port or Position: Yes

List all of the occurrences where the vessel spent 10 or more consecutive days in any single location since the last hull cleaning. List dates as (Day/Month/Year): Date of Arrival: Country:

Number of Days: Port or Position:

Date of Arrival: Country:

Number of Days: Port or Position:

Date of Arrival: Country:

Number of Days: Port or Position:

Date of Arrival: Country:

Number of Days: Port or Position:

Date of Arrival: Country: Date of Arrival: Country: Date of Arrival: Country:

Number of Days: Port or Position:

Date of Arrival: Country:

Number of Days: Port or Position:

Date of Arrival: Country:

Number of Days: Port or Position:

Date of Arrival: Country:

Number of Days: Port or Position:

Official / IMO Number:

Section 2:

Ballast Water Treatment System Information

COMPLETE ONLY IF VESSEL HAS A BALLAST WATER TREATMENT SYSTEM INSTALLED Note: Complete a separate Section 2 for each installed ballast water treatment system 14. Provide the following information about the vessel’s installed ballast water treatment system:

Manufacturer/Company: Product Name: Model Number: Date System Commissioned (Day/Month/Year): 15. Has the installed ballast water treatment system been used to treat ballast water in the last 12 months? Yes Number of times the system was used in the last 12 months: No

16. Has the installed ballast water treatment system malfunctioned in the last 12 months?

Date of Most Recent Malfunction (Day/Month/Year): Yes Describe all malfunctions during the previous 12 months:

Describe all repairs for all malfunctions during the previous 12 months:

17. Has an onboard test for biological performance of the vessel’s installed ballast water treatment system been completed since the system was commissioned? Yes

If “YES”, List the dates of the tests (Day/Month/Year):

Official / IMO Number:

INSTRUCTIONS As used in this form, “vessel” has the sa me meaning as defined in California Code of Regulations, Title 2, section 2298.2. Applicability of this reporting requirement is defined in California Code of Regulations, Title 2, section 2298.5. SUBMIT THE COMPLETED FORM AT LEAST TWENTY-FOUR HOURS IN ADVANCE OF THE FIRST ARRIVAL OF THE CALENDAR YEAR AT A CALIFORNIA PORT TO:

California State Lands Commission Marine Environmental Protection Division 200 Oceangate, Suite 900 Long Beach, CA 90802 or fax: 562-499-6444 or e-mail: bwform@slc.ca.gov Report information using the following instructions:

Question 1: Check the appropriate box to indicate whether the vessel has an onboard ballast water treatment system installed.  If Yes was selected, complete both Section 1 and Section 2  If No was selected, complete only Section 1 Section 1: Hull Husbandry Maintenance and Operational Information

Question 2: Check the appropriate box to indicate whether, since delivery, the vessel has ever been removed from the water for maintenance.  If “Yes” was selected, enter the date (Day/Month/Year) and location for the most recent out-of- water maintenance period (for example, if vessel was out of water for dry-dock from 1 January 2016 through 10 January 2016, list 10 January 2016 as the last date out of water)  If “No” was selected, enter the vessel’s delivery date (Day/Month/Year) and the location where the vessel was built

Question 3: Check the appropriate box to indicate whether the vessel’s hull was coated with an anti- fouling treatment/coating during the out-of-water maintenance period or shipbuilding process described in Question 2.

  

If “Yes, full coat applied” was selected, move on to Question 4 If “Yes, partial coat” was selected, list completion date (Day/Month/Year) of most recent full coat application of an anti-fouling treatment/coating If “No coat applied” was selected, list completion date (Day/Month/Year) of most recent full coat application of an anti-fouling treatment/coating

Question 4: For the most recent full coat application of anti-fouling treatment/coating, list the manufacturer(s)/company(ies) and product names of the treatment(s)/coating(s) and check the box next to the specific section(s) of the submerged portions of the vessel where each treatment was applied (check all sections that apply). List information for each anti-fouling treatment/coating if more than one was applied. Attach additional pages if necessary. Question 5: Check the appropriate box to indicate whether the sea chest(s) were inspected and/or cleaned during the most recent out-of-water maintenance period described in Question 2. If no out-of- water maintenance since delivery, check Not Applicable.

Question 6: Marine Growth Protection Systems (MGPS) are systems installed in the sea chests or sea strainers to prevent the accumulation of fouling organisms within the sea chests and associated seawater circulation networks. Check the appropriate box to indicate if a Marine Growth Protection System is installed in the sea chest(s).   

If “Yes” was selected, list the Manufacturer and Model If “Yes” was selected, indicate whether MGPS is installed in sea chests or strainers (or both) If “No” was selected, move on to Question 7

 

Question 7: Check the appropriate box to indicate if the vessel has undergone in-water cleaning on the submerged portions of the vessel since the last out-of-water maintenance period. In-water cleaning does not include cleaning carried out during out-of-water maintenance but does include cleaning carried out during the Underwater Inspection In lieu of Dry-Docking (UWILD). For this question, out-of-water maintenance includes the shipbuilding process. If “Yes” was selected, answer Question 7a If “No” was selected, move on to Question 8

Question 7a: Provide date (Day/Month/Year) and location of most recent in-water cleaning (do not include cleaning performed during out-of-water maintenance period) as well as the vendor that conducted the in-water cleaning. Check the box next to the appropriate sections to indicate those sections of the vessel that were cleaned during the in-water cleaning described in Question 7. Indicate whether in-water cleaning was conducted by divers, a robotic system, or both.

 

Question 8: Check the appropriate box to indicate whether the propeller has been polished since the most recent out-of-water maintenance or in-water cleaning. For this question, out-ofwater maintenance includes the shipbuilding process. If “Yes” was selected, list the date of the most recent propeller polishing If “No” was selected, move on to Question 9

Question 9: Check the appropriate box to indicate whether the anchor and anchor chains are rinsed during retrieval.

Question 10a: Over the past four months, list the average speed (knots) at which this vessel has travelled. Question 10b: Over the past four months, list the average length of time (either hours or days) that this vessel has spent in any given port. Question 11a: Check the appropriate box to indicate whether this vessel has visited any freshwater ports (specific gravity of less than 1.005) since the hull was last cleaned (either inwater or out-of- water) or since delivery if the hull has never been cleaned. 

If “Yes” was selected, list the number of times that this vessel visited freshwater ports since the hull was last cleaned or since delivery if the hull has never been cleaned

Question 11b: Check the appropriate box to indicate whether this vessel has visited any tropical ports between latitudes 23.5o S and 23.5o N since the hull was last cleaned (either inwater or out-of- water) or since delivery if the hull has never been cleaned. 

If “Yes” was selected, list the number of times that this vessel visited tropical ports since the hull was last cleaned or since delivery if the hull has never been cleaned.

Question 11c: Check the appropriate box to indicate whether this vessel has traversed the Panama Canal since the hull was last cleaned (either in-water or out-of-water) or since delivery if the hull has never been cleaned. 

If “Yes” was selected, list the number of times that this vessel has traversed the Panama Canal since the hull was last cleaned or since delivery if the hull has never been cleaned.

Question 12: Starting with the most recent port, list the last 10 ports visited by this vessel. Provide information on the port or place, country, and the dates of arrival and departure. If this vessel follows a regular route, visiting the same ports routinely, place a check in the box provided and list the information for the most recently completed route. You do not have to use all ten spaces if the regular route involves less than 10 ports. Add more lines if the regular route involves more than ten ports.



If “No” was selected, enter the information for the single longest amount of time this vessel has spent in a single location since the last hull cleaning or since delivery if the hull has never been cleaned. If “Yes” was selected, list all of the occurrences where the vessel spent 10 or more consecutive days in any single location since the last hull cleaning or since delivery if the hull has never been cleaned.



Question 13: Check the appropriate box to indicate whether this vessel has spent 10 or more consecutive days in any single location since the last time the hull was cleaned (either in-water or out of water) or since delivery if the hull has never been cleaned. Do not include time spent out-of-water or time spent during in-water cleaning.

Section 2: Ballast Water Treatment System Information COMPLETE ONLY IF VESSEL HAS A BALLAST WATER TREATMENT SYSTEM INSTALLED If more than one treatment system is installed on board the vessel, Section 2 must be filled out separately for each system. Question 14: Provide the following information for each ballast water treatment installed on the vessel:   



System manufacturer or company (For example - Acme Incorporated) Product name, if applicable (For example - Acme Ballast Water Treatment System) Model number, if applicable (For example - Acme Model # 5454). Do not provide the serial number. Date (Day/Month/Year) the ballast water treatment system was commissioned. This is the date that the system was determined to be ready for active service including: (1) Functionally ready for use, and (2) Has received all applicable use approvals.

Question 15: Provide the number of times the vessel’s installed ballast water treatment system was used during the previous 12 months.



If “Yes” was selected: o List the date of the most recent malfunction o Describe the malfunction including the type of malfunction (for example software, chemical, operational, plumbing, etc.) o Describe all repairs that were completed as a result of each malfunction If “No” was selected, move on to Question 17



Question 16: Check the appropriate box to indicate whether the installed ballast water treatment system has malfunctioned during operation in the previous 12-month period. Attach additional pages as necessary.

If “Yes” was selected, list the dates (Day/Month/Year) for all tests of biological efficacy since the system was installed. If “No” was selected, this is the end of the form.



Question 17: Check the appropriate box next to indicate whether an onboard test for biological efficacy has been completed since the system was installed. Biological efficacy is the ability of the ballast water treatment system to reduce the number of viable organisms in water.



Biofouling Management for Wetted Surfaces

7.1. The master, owner, or operator of the vessel arriving at a California port or place shall manage biofouling on the wetted surfaces of the vessel, except those niche areas described in the section 3, in any of the following ways:

(a) If vessel is using an anti-fouling coating, the coating shall not be aged beyond its effective coating lifespan. If vessel is using an anti-fouling coating and the coating is aged beyond its effective coating lifespan, as documented in 2 CCR Â§2298.3(b)(2)(C), the master, owner, operator, or person in charge of the vessel shall document in the Biofouling Management Plan how biofouling on the wetted surfaces of the vessel (except those niche areas listed in the section 3.1) shall be managed after the effective coating lifespan is exceeded. All biofouling management actions undertaken, and reports resulting from such actions, shall be documented in the Biofouling Record Book. (b) If a vessel is not using an anti-fouling coating, the master, owner, operator, or person in charge of a vessel shall document in the Biofouling Management Plan how biofouling on the wetted surfaces of the vessel (except those niche areas listed in the section 3.1) shall be managed in the absence of an anti-fouling coating. All biofouling management actions undertaken and reports resulting from such actions shall be documented in the Biofouling Record Book.

7.2. The vesselâ&#x20AC;&#x2122;s master, owner, operator prior arriving at a California port shall manage biofouling on the niche areas (as listed in the section 3.1), if present, with practices appropriate for the vessel and its operational profile, as determined by the master, owner, operator, or person in charge of a vessel, and in a manner consistent with the requirements of section 3.2. Any other niche areas should also be managed in a manner consistent with section 3.2. Requirements for Vessels with Extended Residency Periods

The master, owner, operator, or person in charge of a vessel that has had an extended residency period since its most recent out-of-water maintenance, in-water treatment, or inwater cleaning must ensure that the vessel is compliant with the following requirements upon arrival to a California port: Manage biofouling in the niche areas listed in section 3.1, if present, in a manner that is consistent with the niche area management practices listed in the Biofouling Management Plan. All activities employed to manage biofouling in the niche areas described in section 3.1, if present, that accumulates as a result of the extended residency period shall be documented in the Biofouling Record Book.

(a)

(b)

Any activities, including in-water inspection, in-water cleaning, in-water treatment, or outof-water maintenance, to manage biofouling on the wetted surfaces of the vessel, except those niche areas listed in section 3.1, that accumulates as a result of the extended residency period shall be documented in the Biofouling Record Book.

Propeller Cleaning in California Waters

Propeller cleaning in California waters is not prohibited.

10. Emergency Exemptions A vessel will be exempt from the requirements contained within Article 4.8 if all of the following conditions are satisfied: (a)

The vessel makes an unscheduled arrival to a California port because of an emergency, where the safety of the vessel or crew is compromised; Arrival for the sole purpose of scheduled bunkering is not an emergency under this clause; The master, owner, operator, agent, or person in charge of the vessel notifies the Division Chief, in written or electronic form, of the emergency, and provides details on the nature of the emergency, no later than twenty-four hours after the arrival and cessation of the emergency;

(c)

The vessel has not arrived to another California port since the most recent of the:

(b)

(1) Previous out-of-water maintenance; (2) Vesselâ&#x20AC;&#x2122;s delivery into service; or

(3) Date when the vessel owner commenced ownership of the vessel

The vessel will remain in California waters for 21 days or less. If the vessel remains in California waters for greater than 21 days, the Division Chief may require the master, owner, operator, or person in charge of a vessel to clean or treat the vessel to remove or inactivate macrofouling, using available in-water cleaning technologies, in-water treatment technologies, or out-of-water maintenance. The Division Chief will consider the biofouling extent, vessel port residency duration, and available in-water cleaning or treatment options when making this determination.

(d)

APPENDIX VII – SPECIFIC NEW ZEALAND REQUIREMENTS This Appendix contains the additional requirements related to Biofouling Management on Vessels arriving to New Zealand according to the “Craft Risk Management Standard (CRMS)”. 1.

Application

The provisions described in this Appendix apply to vessels arriving at New Zealand. The Craft Risk Management Standard (requirements provided in current Appendix) become effective from 15 May 2018. Abbreviations

Craft Risk Management Plan

CRMS:

Craft Risk Management Standard

MPI:

Ministry for Primary Industries

NZT:

New Zealand Territory

PoFA:

Approved Place of First Arrival

Requirements

CRMP:

Operators of any vessel, arrives at a Port in New Zealand Territory (NZT), should take all reasonable and practicable steps to make sure the vessel has a “clean hull”. To achieve the clean hull requirement, all vessels and marine-going craft must be treated, cleaned, or have a Record of ongoing Biofouling Maintenance, prior to arrival in NZT.

Even when no specific offshore cleaning or treatment activities are carried out, all vessels must be compliant with the CRMS and arrive into NZT free of biofouling. To comply with the requirements, operators must carry evidence that hull maintenance has been done, such as antifouling system details, diver reports and photos from inspections and cleaning, or evidence of a full hull clean (among others).

For areas not easily seen or accessible during inspections, such as internal areas of sea chests and pipework, actions taken for biofouling management should be properly kept. Such actions may include: a) The operation of Marine Growth Prevention Systems (MGPSs), b) The chemical dosing, and c) Inspection of strainers. Where a complete inspection of all submerged areas of the vessel is difficult, the vessel may need to be dry docked or managed using an MPI-approved treatment to ensure that the requirements are met. Vessels coming to work permanently within NZT should consider carrying out specific cleaning and/or treatment activities in dry dock before departing. If requirements are not met and risk management is required, MPI will determine if a suitable treatment can be carried out within NZT, or if other actions are required. There are limited

options for dry docking and cleaning for commercial vessels within NZT so if the vessel does not comply with the biofouling standard on arrival, it may be directed to leave NZT and required to be cleaned elsewhere. 4.

Actions to be carried out prior vessel’s departure for New Zealand

MPI requires the operator of any vessel arriving in NZT to send the pre-arrival information to MPI at least 48 hours prior to entry, including submitting information on what has been done to manage biofouling prior to arrival (as described in next section).

Actions to be carried out on route to NZT

The three below management options are provided by MPI to vessels’ operators in order the compliance with the relevant requirements to be achieved and enabling operators to tailor a solution that suits their vessel type, provided that the approach achieves a “clean hull”: a) Cleaning the hull within 30 days prior to arriving in NZT and providing MPI with documentation of that clean; or b) Conducting continual hull maintenance using best practice principles, such as IMO biofouling guidelines, and providing MPI with documentation of that management; or c) Conducting hull treatment using an MPI-approved provider within 24 hours of arriving into NZT and providing MPI with documentation of the scheduled treatment.

The operator must submit the following forms to MPI at least 48 hours prior to vessel’s entry into NZT: a) Advanced Notice of Arrival. b) Biofouling and Ballast Water Declaration. c) Master’s Declaration. d) Verifiable evidence that one of the three management options to meet the biofouling standard have been done.

These forms include information such as:  Details about the vessel’s antifouling coating (AFC), such as date of last renewal, certificate of treatment and service life.  Intended length of stay within NZT and the places the vessel intends to visit.  Whether a Biofouling Management Plan (BFMP) and Biofouling Record Book (BFRB) (or any other forms of records) are kept.  Whether the vessel has spent extensive time idle or extended periods mainly stationary in a single location. 6.

Record keeping

Record keeping is the key step in showing MPI that the vessel is not high risk. Acceptable evidences:  Antifouling Certificate, including information on AFC application date, type of antifouling applied and if it is applied to niche areas.  Reports from a recent hull and niche area inspection, with photos and/or video footage.  Reports from the most recent cleaning of the hull and niche areas, with photos and/or video footage.  Records of contingency planning if a vessel falls out of its operational profile.  Ship-specific Biofouling Management Plan (BFMP) and Biofouling Record Book (BFRB).

Upon arrival to PoFA

Upon arrival, all information provided to MPI will be verified. The risk profile of the vessel, and the quality of the documentation carried on board will determine what further actions are required, if any. Verification will take place through conversations with the operator of the vessel and by conducting verification inspections. This can include checking that the information provided in the Advance Notice of Arrival, and the Master's Declaration is correct, inspecting records of biofouling management, asking to inspect sea strainers and MGPSs, and studying the vessel's voyage history.

Becoming a long-stay vessel

Verification ranges from confirming information requirements (e.g. antifouling certificate, biofouling management plan) to a physical inspection of the vessel’s hull.

Where an operator or person in charge of vessel wishes to extend the vessel's stay past 20 days or visit places that are not PoFAs, they must contact MPI as soon as possible and make arrangements to meet the requirements of long-stay vessels. The biofouling thresholds for long-stay vessels, or vessels that wish to visit places not approved as PoFAs are stricter.

A vessel which changes its itinerary and falls into the long-stay category must meet these stricter requirements. Craft Risk Management Plan

In case that the biofouling requirements have not been met via the below options, the vessel’s operator can develop a Craft Risk Management Plan (CRMP) where the actions on how the risk will be managed must be outlined:  best practices and/or developing a BFMP,  cleaning prior to arrival, or  using an approved treatment. The CRMP may be submitted to MPI for approval. Failure to meet biosecurity requirements or non-compliance

10.

The vessel’s operator is responsible for ensuring that vessel arriving into NZT meet the requirements of the biofouling standard. If the requirements are not met, biosecurity compliance will not be given and the vessel will be directed for further action under the Act. Any vessel that can be managed by approved local treatment providers or haul out facilities may be directed for treatment (clean in-water or hauled out for cleaning). Any vessel that cannot be treated by approved treatment providers may be directed out of NZT for treatment before being allowed to come back into NZT. Any biofouling management or costs due to delays for non-compliant vessels will be at the vessel owner’s or operator’s expense. 11.

Random compliance inspections and audits

Any arriving vessel may be subject to random compliance inspections to verify compliance with the requirements of the biofouling standard. This is in addition to risk-based verification inspections. It is likely that random compliance inspections will generally be more intensive than risk-based verification.

Where a vessel has been selected for a compliance inspection, MPI will liaise with the agent, operator or person in charge of the vessel to ensure that any delays are minimised. Meeting of biofouling requirements of New Zealand



Prior departing, it must be ensured that the section(s) of the biofouling standard related to the vessel’s intended length of stay in NZT having been identified.



Identification of which measure will be used onboard the vessel in order the biofouling standard (for example, best practice maintenance of your vessel’s hull, clean before arrival, or MPI-approved treatment) to be complied.



Ensuring that verifiable evidence, that one of the three measures to meet the biofouling standards has been done, exists onboard the vessel.



If the vessel has been stationary or idle for any extended period of time, operator must check if any additional cleaning is required in order the biofouling standards to be complied. This will significantly reduce arrival delays and costs.



MPI should be contacted before departing for NZT. MPI assistance prior to departure can help in minimizing delays and costs on arrival.



The Advance Notice of Arrival and Master's Declaration Forms should be properly filled in and submitted to MPI at least 48 hours prior to entry into NZT. Relevant evidences of compliance with the biofouling standard should be also submitted.



Ensuring that the port of arrival is an approved Place of First Arrival (PoFA) that can receive your type of vessel and any associated cargo or risk goods on-board that you wish to discharge.



Any entry or arrival directions given by MPI must be followed.



No in-water cleaning of vessels hull should be carried out in the NZT, unless authorised by MPI or using an MPI-approved treatment provider.

12.

New Zealand (NZ) Biofouling and Ballast Water Declaration: Parts 1 and 2 TO BE COMPLETED FOR ALL VESSELS ARRIVING IN NEW ZEALAND Vessel Name:

IMO Number:

Voyage Number:

Arrival Date:

Arrival Port:

PART 1: BIOFOULING Do you have a biofouling management plan on board?

Yes or

No or

Unknown

Do you keep a biofouling record book?

Yes or

No or

Unknown

When was the vessel built?

When was the last renewal of anti-fouling coating to the hull?

Build Date:

A. Do you have a certificate of treatment?

Yes or

B. What date is the anti-fouling coat effective until? In the last year how many times was the vessel moored or laid up in one location for 10 days or more, 20 days or more, and 30 days or more? When is the next haul out/dry dock intended for this vessel and in what location?

PART 2: BALLAST WATER

Antifouling Date: No

Date:

≥10 days:

≥20 days:

Date:

Location:

Do you have a ballast water management plan on board?

Yes or

Is the vessel carrying any ballast water?

Yes or

Do you have a ballast water log?

What is your ballast status on arrival in NZ?

5 6

What is the maximum ballast capacity of this vessel? Are any ballast tanks intended for discharge, or possible discharge, in New Zealand ports or territorial waters?

S A

MASTER TO MAKE DECLARATION HERE I state the declaration (Part 1, Part 2, and Part 3 as relevant) is true in every particular. Master’s Name: Signature:

Yes or No Number of tanks in ballast:

Volume:

Total number of tanks: Maximum volume: m3 Yes: Complete ‘Part 3’ of this declaration and sign this form. OR No: Sign this form and no further detail is required. MPI Officer signature BW discharge permitted:

No ballast water discharge is permitted without written authority by MPI

MPI Officer Comments:

≥30 days:

Yes

New Zealand (NZ) Biofouling and Ballast Water Declaration: Part 3

Vessel Name: Voyage Number: All vessels intending to discharge ballast water or with contingency tanks for possible discharge in NZ territorial waters must complete this part. All ballast water tank volumes must be recorded in mPP3PP. (For more information see the NZ Import Health Standard for Ballast Water from all Countries). How will you comply with NZ’s ballast water requirements? Check the box(es) indicating the ballast water management option used. FW TS E/R or F/T Discharging Treating ballast water using an MPI-approved Exchanging the ballast water at mid-ocean (at least 200 NM from the nearest land and in water of over 200m in fresh water shipboard system depth) by Empty/Refill (E/R) (with an efficiency of 95% volumetric exchange) or Flow-Through (F/T) (at least three times the maximum tank capacity). Treatment system: Maximum combined pump capacity (all ballast water pumps): mPP3PP/hr Exemption applied for If you were unable to complete the mid-ocean exchange because it would have caused unacceptable risk to the crew or vessel due to adverse conditions you will need to complete details in the following table identifying the tanks and source of the ballast water for all tanks that the exemption is applied for. Specific details of why the exemption is required: F/T TANKS

S A

TANKS BW SOURCE MANAGE- E/R TANKS Use tank codes listed Prior to mid-ocean exchange or treatment OR source of MENT & REFILL below FW ballast OR “Empty tank”. METHOD of Empty “Empty Tank” or Volume in tank Residual Tank Max. tank Date FW, TS, Uptake port before exchange volume when Name capacity (d/mmm/yy) E/R or F/T or treatment empty Lat/Long 3 3 m m m3 ° ′N ° ′E m3 m3 m3 ° ′N ° ′E m3 m3 m3 ° ′N ° ′E m3 m3 m3 ° ′N ° ′E m3 m3 m3 ° ′N ° ′E m3 m3 m3 ° ′N ° ′E

Volume pumped through m3 m3 m3 m3 m3 m3

MID-OCEAN FLOW-THROUGH EXCHANGE (F/T) or REFILL (R) *For E/R or filling empty tanks, only record REFILL (R) detail* Details at start and end of refill (R) or F/T Final volume in tank on Lat / Long Date Time (degrees minutes) (d/mmm/yy) (24 HR) arrival in NZ

Start End Start End Start End Start End Start End Start End

° ° ° ° ° ° ° ° ° ° ° °

′N ′N ′N ′N ′N ′N ′N ′N ′N ′N ′N ′N

° ° ° ° ° ° ° ° ° ° ° °

′E ′E ′E ′E ′E ′E ′E ′E ′E ′E ′E ′E

m3 m3 m3 m3 m3 m3

Ballast tanks codes: Forepeak (FP), Afterpeak (AP), Double Bottom (DB), Deep Tank (DT), Wing Tank (WT), Topside Tank (TS). Starboard (S), Upper (U), Lower (L) BW Management Method codes: Freshwater (FW), Empty then Refill (E/R), Flow-Through (F/T), Treatment System (TS)

New Zealand (NZ) Biofouling and Ballast Water Declaration: Part 3

Tank Name

Max. tank capacity

BW SOURCE Prior to mid-ocean exchange or treatment OR source of FW ballast OR “Empty tank”.

Date (d/mmm/yy)

“Empty Tank” or Uptake port Lat/Long

m3 °

′N

′E

′N

′E

m3 m3 °

′N

′E

m3 ′N

′E

′N

′E

m3 m3

m3 m3 m3

Volume pumped through

′E

′N

′E

′N

′E

′N

′E

′N

′E

′N

′E

′N

′E

S A

′N

F/T TANKS

Residual volume when empty

° m3

Volume in FW, TS, tank before E/R or exchange F/T or treatment

° m3

MANAG E/R E-MENT TANKS METHO & REFILL D of Empty

′N

′E

′N

′E

MID-OCEAN FLOW-THROUGH EXCHANGE (F/T) or REFILL (R) *For E/R or filling empty tanks, only record REFILL (R) detail* Details at start and end of refill (R) or F/T Final volume in Lat / Long Time tank on Date (degrees (24 arrival in (d/mmm/yy) minutes) HR) NZ Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E Start ° ′N ° ′E m3 End ° ′N ° ′E

TANKS Use tank codes listed below

New Zealand (NZ) Biofouling and Ballast Water Declaration: Part 3

Tank Name

Max. tank capacity

BW SOURCE Prior to mid-ocean exchange or treatment OR source of FW ballast OR “Empty tank”.

Date (d/mmm/yy)

“Empty Tank” or Uptake port Lat/Long

m3 °

′N

′E

′N

′E

m3 m3 °

′N

′E

m3 ′N

′E

′N

′E

m3 m3

m3 m3 m3

Volume pumped through

′E

′N

′E

′N

′E

′N

′E

′N

′E

′N

′E

′N

′E

S A

′N

F/T TANKS

Residual volume when empty

° m3

Volume in FW, TS, tank before E/R or exchange F/T or treatment

° m3

MANAG E/R E-MENT TANKS METHO & REFILL D of Empty

′N

′E

′N

′E

TANKS Use tank codes listed below

MASTERâ&#x20AC;&#x2122;S DECLARATION I, (Given Name)

Family Name)

of the

hereby certify that: (Full Name of Craft)

1. The origin of all meat on board is (attach extra page if required): Country of origin Type of meat (including poultry and fresh-water fish)

2. The origin of all fresh produce including fruit and vegetables is (attach extra page if required): Country of origin Port and country of loading Type of fresh produce

3. Refuse: NO 3.1 The craft has a refuse/garbage management plan. YES 3.2 The refuse/garbage control on board is: Drums Holding room Holding tanks Galley chute Galley grinder Sea Holding tanks Not applicable 3.3 Galley chute/grinder discharges into:

4. The live animals on board are (list all dogs, cats, fish, birds and any other pets): Number of animals MPI permit or prior approval Type of animal (include identifying features) details

5. The following pest management programmes are adhered to on board (attach extra page if required): Control measures in place Pest management programme (e.g. baiting or treatment) (treatment type and application methods)

6. The following insects, pests and / or hitchhiker animals are on board (attach extra page if required): Location on craft Type/name of insect, pest or hitchhiker

To the best of my knowledge and belief the above statements are true and correct in every particular and I am fully aware of the provisions of the Biosecurity Act 1993 sections 18 and 19. Masterâ&#x20AC;&#x2122;s Signature: Dated this

day of

Time:

Port:

Biosecurity Act 1993 18 Arrival of craft in New Zealand  (1) The person in charge of any craft that arrives at a place in New Zealand: o (a) Shall, if:  (i) The person has not notified the Director-General under section 17 of this Act; or  (ii) The place is not the port or destination notified (or, as the case may be, last notified) under section 17 of this Act, give the Director-General notice of where and (approximately) when the craft arrived; and o (b) Shall prevent risk goods from leaving the craft without the permission of an inspector. (2) The person in charge of any such craft shall, if so required by an inspector, pay a bond for such amount not exceeding $10,000 as the inspector may require to secure due compliance with subsection (1)(b) of this section.

19 Persons in charge of certain craft to obey directions of inspector or authorised person  (1) This section applies to a craft, and place in New Zealand, if: o (a) The craft arrives in New Zealand there; or o (b) The craft is carrying risk goods that it was carrying when it arrived in New Zealand at some other place. (2) Where this section applies to a craft and place, the person in charge of the craft shall: (a) Obey every reasonable direction given by an inspector as to:  (i) The movement of the craft in the place; or  (ii) The unloading or discharge of risk goods or the disembarkation of crew or passengers from the craft; or  (iii) Measures (including any bond required under section 18(2) of this Act) to ensure that any risk goods not intended to be unloaded or discharged from the craft are maintained in a secure place under the control of that person; and o (b) Within the required time or times, deliver to an inspector a report, in such manner and form, and containing such particulars verified by declaration, and with such supporting documents, as may be required; and o (c) Answer all questions relating to the craft or its cargo, crew, passengers, stores, or voyage, asked by an inspector; and every person disembarking from the craft shall, on request by an inspector, make his or her baggage available for inspection by the inspector.

Privacy Statement

Information sought on the New Zealand Master’s Declaration and associated crew and passenger lists for arriving crafts is required to administer the Biosecurity Act 1993 (the Act). Collection of this information is authorised by s19 of the Biosecurity Act and failure to provide information may be an offence under the Act. The Ministry for Primary Industries (MPI) will not disclose any personal information unless it is in accordance with New Zealand law.

The Privacy Act 1993 provides rights of access to, and correction of, personal information held in readily retrievable form. Should you wish to exercise these rights please contact MPI on telephone number 0800 00 83 33.

APPENDIX VIII â&#x20AC;&#x201C; RELEVANT INFORMATION

The following information related to this plan is attached: No.

Title General Arrangement Plan

Docking Plan

AFS certificate or statement of compliance or other documentation

MGPS Manual

5. 6.

Dwg. / Cert. No.