Impact analysis of rainwater harvesting in Delhi India - FORCE

STUDY REPORT December 2010

For

Impact Assessment of Rainwater Harvesting (A case study of Alakananda, New Delhi)

Report by: FORCE

With Support from Sh Shubh Sharada: RWA Member, Mandakini Enclave

Under the guidance of: Mr. RC Sharma – Scientist, Central Groundwater Board (Retd) Jyoti Sharma – President, FORCE

FORCE

Forum for Organised Resource Conservation and Enhancement For more information on

FORCE visit our website:

www.force.org.in

FORCE–C-8/8035, Vasant Kunj, New Delhi–110070.T: 11 46018754 M: 9899812888 email force@force.org.in

PREFACE Rainwater Harvesting is now widely acknowledged as a simple, effective method of augmenting local water reserves. 10 states in India have already made rainwater harvesting mandatory for all new buildings. Many more are expected to follow suit. The central government has announced several schemes to support rainwater harvesting and has also included it in the list of approved activities for several existing schemes.

And yet, the skeptics continue to doubt its efficacy. Myths abound about its inefficiency, unsuitability to some terrain types and damage to buildings etc.

FORCE has been actively propagating the adoption of rainwater harvesting by communities because it is the cheapest, most effective method of increasing local water reserves. Through our awareness programs, we have tried to address all these doubts about Rainwater Harvesting, yet much more needs to be done.

We have been working with the Residents Welfare Associations of Alakananda to help them adopt / maintain rainwater harvesting for the past few years. In our interactions with them, both on formal public platforms and in informal meetings, they have been sharing very positive stories about the increase in the yield of their tubewells, dried up tubewells that have started yielding water, measured rise in water table etc.

This Study was done to check the validity of those claims. Also, we hoped that, if validated, these results would lay to rest some of the doubts raised about the efficacy of rainwater harvesting.

The study was conducted by FORCE with a team of students of reputed universities – TERI University and University of Pennsylvania (USA) under the guidance of a Scientist (Retd) from Central Groundwater Board and with support from the Residents Welfare Associations of Alakananda notably Mandakini Enclave RWA.

We are thankful to the students and advisors who helped give shape to this study. We hope that this study will prove what we have been observing all along – that rainwater harvesting is an effective, efficient way of recharge to groundwater.

TABLE OF CONTENTS S.NO.

TOPIC

PAGE

SECTION 1 1.1.

INTRODUCTION About Water Supply in Delhi The Role of Groundwater in Delhi’s Water Supply

1.2

BACKGROUND INFORMATION Groundwater Status and Trends in Delhi Typical contaminants in groundwater & their effect About Rainwater Harvesting

SECTION 2 2.1

OBJECTIVES OF THE STUDY

2.2

GEOGRAPHICAL SCOPE OF THE STUDY

2.3

METHODOLOGY Data Collection Limitations of the study

17

SECTION 3 3.1 3.2

DETAILS OF STUDY AREA Hydrometreological conditions Hydrological details

SECTION 4 4.1

FINDINGS & CONCLUSIONS Rainwater Harvesting status in Alakananda Groundwater draft as compared to RWH Groundwater status Community Observations of water level Pre & Post Monsoon 2010 Water Level Pre & Post Monsoon 2010 Water Quality Contribution of Aquifer Characteristics impact Financial Implications and benefits of rainwater harvesting Social Impact of RWH in Alakananda

SECTION 5 5.1

CASE STUDY – MANADKINI ENCLAVE, ALAKANANDA

SECTION 6 6.1

RECOMMENDATIONS

SECTION 1 1.1 INTRODUCTION About Water Supply in Delhi Present Water Demand and Supply In Delhi, the civic body responsible for the provision of water is Delhi Jal Board (DJB). The norms set by DJB call for the supply of a total of 225 LPCD. If these norms are applied to the dual water supply system, this would mean that the water would be supplied as follows: Potable or drinking water

75 LPCD

Domestic water

150 LPCD

Total

225 LPCD

As per the above requirements and accounting the population of Delhi, per capita per day, present total requirement for drinking and domestic purposes comes out as is 3675.5 MLD per day (810 MGD). Considering the irrigational and industrial requirements water, the total water requirement would be 3940 MLD (866 MGD). At present Delhi Jal Board is supplying about 630 MGD of water by treating the surface water through the conventional treatment plants.

The share of surface water allotted to NCT, Delhi from the Himalayan Rivers through different interstate agreements is as follows: 1. Yamuna

724 mcm

2. Ganga

178.8 mcm

3. Beas (Bhakra water)

246.4 mcm

The river Yamuna provides the major share of surface water in the territory i.e. 724 mcm.

The interim seasonal allocation of annual utilizable flow of the river Yamuna for the NCT of Delhi is as follows: Table-3.1: Interim seasonal allocation of annual utilizable flow of the river Yamuna for the NCT of Delhi July-Oct Nov-Feb (non- March to June Annual (monsoonseason) monsoonseason) (Summer) 580 mcm 68 mcm 76 mcm 724 mcm From the above table it is seen that the major part of the allotted water is in monsoon period which cannot be fully utilizable as the requirement during that period is low. As per the information available, nearly half of this flood water is not being utilized at present and

flows out of Delhi in these months. Already drained out and overexploited, except Yamuna, Delhi has no other surface source of water to rely upon.

Projected future Water Demand and Supply Table-3.2: Projected future requirement of water in NCT, Delhi.

Water demand in 2005 Water Population requireme nt (In Lakhs) MLD/ (MGD) Drinking and 3675.5 / domesti 163 (808) c water require ments Irrigational 200 / requirements (44) Farm house 21.5 / uses (4.7) Industrial 43 /* requirements (9.5) Total 3940 / (866)

Projected water demand 2011 2021 Popula Water Popul Water tion require ation requirement In ment In MLD/ Lakhs MLD/ Lakhs (MGD) (MGD)

205

4612.5 / (1014)

270

6075 / (1355)

200 / 200 / (44) (44) 21.5 */ 21.5 */ (4.7) (4.7) 43 /* 43 /* (9.5) (9.5) 4877 / 6323 / (1389) (1072) SOURCE: Delhi Groundwater year book 2007.

Population of Delhi has increased at a rate of 4.63% per annum during the decade 19912001. Considering the same growth rate for the present decade, it is estimated that the population of Delhi in 2005 is about 163 lakhs and it would be about 205 lakhs in 2011 and 270 lakhs by 2021. The future water requirements for drinking and domestic requirements are worked out based on the projected population figures multiplied by the per capita requirements of water. The requirement of water for irrigational purposes and industrial purposes has been worked out based on the present withdrawal pattern as given in the report of ground water estimation committee (The report has been approved by the committee consisting of the members from Central Ground Water Board, Delhi Jal Board, DDA, Delhi Cantt and Irrigation and Flood Control Dept.). * Considering that no more water intensive industries will be permitted in NCT, Delhi, the present draft from the ground water is taken as the water requirement for industrial use in Delhi. Supply of water for industries and farm houses is nil from DJB’s piped water supply system.

Considering the 15% transmission losses, the projected water requirement for 2011 and 2021 is about 4877 MLD (1072 MGD) and 6323 MLD (1389 MGD).

Considering the present treatment capacities of water treatment plants located in Delhi, the future water availability to fulfill the demands projected above are as follows: Table 3.3 The future availability of water from all sources.

Withdrawal of water (MGD) 210

Source of Water

Treatment Plant

Yamuna River

Wazirabad Water Treatment Plant Chandrawal Water Treatment Plant Hyderpur Water Treatment Plant

240

Bhakra Storage and Western Yamuna Canal

100 140

Upper Ganga Canal, U.P. from Tehri Dam

20

Surface water

125

Ground Water

825

Nangloi Water Treatment Plant Bhagirathi Water Treatment Plant Sonia Vihar Treatment plant Delhi parallel branch (lining of canal of 102 km stretch) From the tubewells present in different parts of NCT, Delhi and tubewells recommended in Yamuna Flood plain areas (Dewatering and refilling of shallow aquifers) Total

The Role Of Groundwater In Delhi’s Water Supply The case of Delhi is representative of the situation of many urban water systems in developing metropolises. The low level of service ensured by the public utility has led the upper and middle classes to develop coping strategies based on private groundwater abstraction. These might include direct use of groundwater from a private tube well, development of a private small supply network fed with untreated groundwater, or supply by tanker, groundwater remaining the primary source of raw water in most of those private supply chains. As a consequence, indiscriminate abstraction has led to a rapid fall in water tables across the city, which threatens the short term sustainability of the system.

As per Delhi Jal Board, the contribution of groundwater to the municipal supply is around 11% in terms of volume, which represents around 370 Million Liters a Day (MLD). This

figure is often used as an indicator of the relative importance of groundwater for the city's water supply.

However, these figures do not show the real role of groundwater in the city’s water supply.

In order to understand the hidden role of groundwater in Delhi’s water supply, one has to understand the current state of failure of the municipal supply system. Water supply from the network is intermittent and unreliable. Private connections and public standpoint get water only one to four hours a day, with a great uncertainty on the pressure. Zerah (2000) investigated the development of private strategies for coping with the unreliability of the public supply, and found that the total annual cost of those strategies represented twice the annual public expenditure in water in Delhi.

Image 1.2

War on water, a common scenario in Delhi.

Therefore, a large number private tube wells have been installed as a complement or a substitute to the public supply. Although the number of private tube wells legally registered to the authority in charge is around 100 000, different sources estimate the actual number of private tube wells between 2000001 and 3600002. Precise information on private groundwater use is difficult to obtain since this use is subject to public regulation. No precise estimation of the total volume of water abstracted through private tube wells exist.

However, some rough estimates for the year 1996 give a total abstraction around 1300 MLD. One can compare these estimates with the volume of municipal water actually reaching the final user. The total l capacity of the municipal system is of 2950 MLD, and recent estimates give a level of technical losses of 40%. The volume of municipal water reaching the final user is therefore around 1770 MLD. Assuming a growth in the private abstraction of groundwater between 1996 and 2004, we can consider that in terms of volume, private abstraction of groundwater represents around 50% of the total supply to the final users.

At present, there is a demand and supply gap of about 236 MGD. This gap may increase and reaches to 247 MGD during 2011 and 564 MGD by 2021. But the analysis of both

surface and ground water sources, the total availability of water is just 825 MGD fulfilling the just 50% of total water requirements. As per the data of NCRPB, the gap would be about 1900 MLD (417 MGD) as the total water requirement is worked out based on the population projection of 220 lakhs. But as per the figures projected based on the growth percentage of population in NCT, Delhi the demand –supply gap is about 564.

1.2 BACKGROUND INFORMATION Ground Water Status And Trends In Delhi Delhi is experiencing increasing pressure to meet demand for its water resources. Growing urbanization, improvements in living standards, exploding population are just some of the contributing factors. In Delhi too ground water contributes to substantial quantity of supply.

Especially in new development areas ground water is largely being utilized as a drinking water resource, mainly because of the insufficiency of the Yamuna water share for Delhi.

Ground water collects in the aquifers over thousands of years through infiltration and ground water flow recharge. Some amount of ground water is replenished regularly through rainwater infiltration. Sustainable use of ground water means withdrawal of ground water at a rate at which it is replenished through recharge. Faster withdrawal rates would lead to fall in water table and finally depletion of ground water.

The alarm bells are ringing right below our feet. Delhi extracts almost double the amount of groundwater than is recharged every year. A status report on groundwater by the NCR Planning Board (NCRPB) reveals that the water table in Delhi was dipping by 2 meters every year. The report says the city currently draws 0.47 billion cubic meters (bcm) of water from the ground every year while only 0.28 bcm gets recharged. That means Delhi loses a whopping 0.19 bcm of groundwater in a year.

Depth to Water Table A comparison of water levels from 1962 to 1977, 1977 to 1983 and 1983 to 1995 brings out a clear picture of water level declines in major parts of the territory. During 1977, the water table was by and large within 6m below ground level(bgl) in major parts of the territory deepest being 23m bgl at near Quatab minar in Mehrauli Block. In 1983 the depth to water level declined to 10 m bgl in major parts. In 1995 the extent of area with water levels in the range of 10 to 20 m bgl has substantially increased.

Fig. 2.2 Out of nine districts in city seven have been categorized as over exploited.

Source: CGWB

Ground Water Quality Chemical quality of groundwater in NCT Delhi varies with depth and space. In alluvial formations, the quality of groundwater deteriorates with depth, which is variable in different areas. Brackish groundwater mainly exists at shallow depths in northwest, west and southwest districts with minor patches in north and central districts. Groundwater is fresh at all depths in the areas around the ridge in the central, New Delhi, south and southwest districts. In the areas west of the ridge, in general, the thickness of fresh water aquifers decreases towards northwest.

Salinity of ground water in different districts is found in the decreasing order as Southwest > West >Northwest> Northeast and East districts. The salinity of ground water increases with depth. Occurrence of moderately to highly saline ground water and increase in salinity with depth suggests that at many places, mostly highly urbanized area, the ground water flushing is incomplete and amount of contemporary recharge to ground water is very limited or even absent at many places.

In over 30 percent of the area in NCT Delhi, the fluoride concentration in ground water is more than the WHO prescribed maximum permissible concentrations in drinking water i.e.

1.5mg/l. The areas spread mainly in the South-western and Western part of the city comprising Southwest, West and Northwest districts (Fig. 2.3).

The studies carried out by CGWB indicate that nitrate concentrations in ground water of Delhi have wide range (less than 1 mg/lt to 945 mg/lt). The higher nitrate concentration may be attributed due to combined effect of contamination from domestic sewage; livestock rearing, landfills and run off from fertilized fields, unlined drains and cattle sheds. These

wide ranges in concentrations suggest mainly point source of contamination. The high nitrate concentration in ground water is significant particularly in the parts of West, Southwest and some pockets in Northwest districts (Fig.2.3).

The most common water quality problem in rural and urban water supplies in Delhi is bacteriological contamination. Central Ground Water Board in collaboration with Central Pollution Control Board carried out water sampling in NCT Delhi for bacteriological contamination also. Out of total number of 269 ground water samples collected 58% water samples were found bacteriological contaminated in N.C.T. Delhi. The presence of total coliforms and fecal coli-forms was mostly from ground water samples collected from hand pumps. In the most of the hand pumps, the ground water is polluted due to bacteriological contamination, due to poor maintenance of hand pumps and unhygienic conditions around the structure. The areas affected with respect to fecal contamination are located in Southwest, Central and East Districts of NCT, Delhi.

Typical Contaminants In Groundwater And Their Effects Fluoride Fluoride is a chemical that occurs naturally within many types of rock. The Maximum Acceptable Concentration of fluoride in drinking water is 1.5 mg/L. Most of the fluoride found in groundwater is naturally occurring from the breakdown of rocks and soils or weathering and deposition of atmospheric volcanic particles. Fluoride can also come from: •

Runoff and infiltration of chemical fertilizers in agricultural areas

•

Septic and sewage treatment system discharges in communities with fluoridated water supplies

At low concentrations fluoride can reduce the risk of dental cavities. Exposure to somewhat higher amounts of fluoride can cause dental fluorosis. In its mildest form this results in discoloration of teeth, while severe dental fluorosis includes pitting and alteration of tooth enamel. Even higher intakes of fluoride taken over a long period of time can result in changes to bone, a condition known as skeletal fluorosis. This can cause joint pain, restriction of mobility, and possibly increase the risk of some bone fractures.

Hardness Water hardness is primarily the amount of calcium and magnesium, and to a lesser extent, iron in the water. Water hardness is measured by adding up the concentrations of calcium, magnesium and converting this value to an equivalent concentration of calcium carbonate (CaCO3) in milligrams per liter (mg/L) of water.

The optimum range of hardness in drinking water is from 80 to 100 mg/L. Water with hardness greater than 200 mg/L is considered poor in usage and water with hardness greater than 500 mg/L is normally considered unacceptable for domestic purposes.

Water hardness in most groundwater is naturally occurring from weathering of limestone, sedimentary rock and calcium bearing minerals. Hardness can also occur locally in

groundwater from chemical and household effluents. Hard water is mainly an aesthetic concern because of the unpleasant taste that a high concentration of calcium and other ions give to water. It also reduces the ability of soap to produce lather, and causes scale formation in pipes and on plumbing fixtures. Excessive hardness may indicate the presence of other chemicals such as nitrate.

Nitrate Nitrate is the most common form of nitrogen found in water. In water, nitrate has no taste or scent and can only be detected through a chemical test. The Maximum Acceptable Concentration (MAC) for nitrate in drinking water is 45 milligrams per liter (mg/L).

The presence of nitrate in groundwater in greater conc. usually reflects the impact of human activities on well water quality. Nitrate is usually introduced into groundwater through widespread or diffuse sources, commonly called non-point sources, which can be hard to detect. These sources can include: •

Groundwater pollution from septic and sewage discharges.

•

Leaching of animal manure

•

Leaching of chemical fertilizers

Though nitrate is considered relatively non-toxic, a high nitrate concentration in drinking water is an environmental health concern because it can harm infants by reducing the ability of blood to transport oxygen. In babies, especially those under six months old, methaemoglobinaemia, commonly called “blue-baby syndrome,” can result from oxygen deprivation caused by drinking water high in nitrate. Death can occur in extreme cases.

Phosphate A number of anthropogenic sources can be responsible for elevated P levels in groundwater.

These include: •

leaking mains water pipes (as orthophosphate is added to drinking water supplies)

•

Septic tank overflows.

•

manure heaps and unlined slurry storage facilities

Silica Silica released as a result of chemical breakdown of silicate minerals in rocks and sediments by chemical weathering, is acquired by circulating groundwater. Therefore the source of silica (SiO2) in groundwater is almost exclusively and unequivocally a result of water–rock interaction. Concentration of SiO2 in groundwater varies from 1 to 30 mg/l, the median value being 17 mg/l.

Studies demonstrates that silica content of groundwater is directly proportional to the residence time of water underground. Relatively high silica content in groundwater, therefore, implies more intense water–rock interaction, which, in turn, may be related to various aquifer-related parameters, such as permeability, residence time and litho logy. pH and TDS count pH value of 6.5-8.5 is considered as safe. Also this neutral pH is quite significant in maintaining numerous chemical dynamics among different chemicals in ground water. TDS (total dissolved solids) is also a parameter in the determination of water quality.

Table 7.1. Freshwater resources according to salinity Water Quality Water Quality Fresh Water Brackish Water Saline Water

Parameter TDS < 1000 ppm 1000 < TDS < 5000 ppm TDS > 5000 ppm

Microbiological – E.coli -analysis The presence of E. Coli in well water may indicate recent contamination of the groundwater by human sewage or animal droppings which could contain other bacteria, viruses, or disease causing organisms. This is why Coliform bacteria are considered “indicator organisms”; their presence warns of the potential presence of disease causing organisms and should alert the person responsible for the water to take precautionary action.

A basic laboratory test is the best way to tell if Coliform organisms are present, as they can be there with no appearance or taste difference. When water is tested for Fecal or Total Coliform, the results are usually given as the number of colony forming units per 100 millilitres (CFU/100ml) of water sampled. No sample should contain Fecal Coliform or E. coli, and ideally there should be no Total Coliform, however a single sample may contain up to 10 Total Coliform CFU/100 ml.

Sources of Total and Fecal Coli form in groundwater can include: •

Infiltration of domestic or wild animal fecal matter

•

Effluent from septic systems or sewage discharges

Poor well maintenance and construction (particularly shallow dug wells) can also increase the risk of bacteria and other harmful organisms getting into a well water supply. The presence of Fecal Coliform bacteria or E. coli indicates contamination of water with fecal waste that may contain other harmful or disease causing organisms, including bacteria, viruses, or parasites such as Giardia, the cause of beaver fever. Drinking water contaminated with these organisms can cause stomach and intestinal illness including diarrhea and nausea, and even lead to death. These effects may be more severe and

possibly life threatening for babies, children, the elderly or people with immune deficiencies or other illnesses.

About Rainwater Harvesting Rainwater harvesting has been done from the days of ancient civilizations in India using improvised methods with local materials. In scientific terms, water harvesting refers to collection and storage of rainwater and efficient utilization of the limited water endowment of physiographic unit such as a watershed.

There are two main techniques of rainwater harvesting: a) Storage of rainwater on surface in natural or man made storage systems for future use. b) Recharge to groundwater Rain â&#x20AC;&#x201C; a critical part of the Hydrological Cycle - is a primary source of water for all of us.

Fig. 4.1 Hydrological cycle With growing human impact over the natural self sustaining environment, various components of hydrological cycle are being disturbed. As all the components of this cycle are interlinked and interdependent, growing influence on one simultaneously degraded other components also. Rainwater harvesting also helps restore the hydrological cycle and to maintain fresh water balance on the land surfaces.

Rainwater Harvesting for Artificial Recharge to Ground Water RainWater harvesting is the deliberate collection and storage of rainwater that runs off on natural or manmade catchment areas. Catchment includes rooftops, compounds, rocky surface or hill slopes or artificially prepared impervious/ semi-pervious land surface. The

amount of water harvested depends on the frequency and intensity of rainfall, catchment characteristics, water demands and how much runoff occurs and how quickly or how easy it is for the water to infiltrate through the subsoil and percolate down to recharge the aquifers.

In urban areas, though adequate space for surface storage is not available, water levels are deep enough to provide unsaturated geophysical zones that can be used to store rainwater and recharge the aquifers. Hence rainwater harvesting is the ideal solution to solve the water supply problems of an urban area like Delhi

Fig.4.2

Schematic diagram of Artificial recharge of groundwater.

The type of artificial recharge system that can be developed at any specific site is controlled, to a large degree, by the geologic and hydrologic conditions that exist at that site. Site selection criteria, in addition to economic considerations should include at least the following: 路 Source of recharge water 路 Chemical and physical characteristics of the recharge water 路 Chemical characteristics of water in the aquifer

· Availability of an aquifer suitable for artificial recharge · Thickness and permeability of the material overlying the aquifer, if any. · Thickness and permeability of the aquifer. · Proximity of the potential recharge site to an appropriate well field cone of depression. · Water- level difference between the aquifer and the recharge site · Topography. · Availability of property (land) Capturing and storing rainwater for use is particularly important in dry land, hilly, urban and coastal areas. It not only provides an improvement in the groundwater both in terms of quantity and quality, but also prevents flash flooding, land subsidence in urban areas.

Additional services like increase well yields and storage of storm water for usage. In recent studies in alluvial areas, energy saving for 1m rise in ground water level was found around 0.40 kilo watt per hour.

Rain water recharge structures besides being sustainable drivers of aquifer recharge, serves many a role. Local water harvesting systems developed by local communities and households can reduce the pressure on the state to provide all the financial resources needed for water supply. In addition, involving people will give them a sense of ownership and reduce the burden on government funds.

Rainwater Harvesting in Delhi One of the Reports from regional authority says that though NCR receives 22.54 bcm of rainwater every year, approximately 16.9 bcm falls during the monsoon season alone. It is estimated that on an average, 6.27 bcm of water is lost due to surface run-off. The report points out that region's capacity to store as much as 183.82 bcm of groundwater remains highly unutilized NCR planning board has pointed out that the groundwater level in NCR is getting critical in the absence of a broad framework for rainwater harvesting and saving the disappearing ponds and lakes. It has also prepared a Master Plan for groundwater recharge in NCR. Building regulations have also been modified to make RWH mandatory, on new buildings, and in severely affected areas, users of tube wells are supposed to install such systems to compensate their abstraction.

SECTION 2 2.1 OBJECTIVES OF THE STUDY There are several myths surrounding rainwater harvesting, especially among laypersons with limited knowledge about the subject. They often question its efficacy in urban environments and discourage people from adopting it.

This Impact Analysis was conducted to establish that rainwater harvesting is effective and cost efficient even in highly built up environments such as in our study area.

With this study, we hope that we would be able to present concrete proof of the immediate localized impact of rain water harvesting. The sub-objectives of the study were: 1) To quantify the Rainwater harvesting that has been done in Alaknanda. Also to specify the dimensions and state of maintenance of these structures 2) Impact Assessment of rainwater harvesting on three parameters: a) Quantitative impact i.e. rise in water table of the area b) Qualitative impact i.e. improvement in the water quality c) Socio-economic impact of rainwater harvesting We hope that the results of this study will help to reduce cynicism of the people about urban rainwater harvesting and thereby encourage more adoption of the same.

2.2 GEOGRAPHICAL SCOPE OF THE STUDY About Alakananda Alaknanda, a DDA developed locality having several Apartment Complexes , in South Delhi, was one of the first to adopt Rainwater Harvesting. It has several well-known apartment complexes such as Mandakini Apartments, Narmada Apartments, NRI Complex, Aravli Apartment, Gangotri Apartments, Tara Apartments, Yamuna Apartments etc. All these complexes have well designed and maintained storm water drainage systems.

Majority of apartment complexes in Alaknanda have implemented rainwater harvesting.

These complexes are also making efforts to maintain their RWH structures and monitor their effect on the water table. The community leaders claim that the water table in their area has gone up and that the yield in their tube wells near the RWH structures has increased.

Of all the apartment complexes in Alakananda, the study was conducted in Mandakini Apartment - Aravali Apartment

-Narmada Apartment -NRI Complex - Rishi Apartment - Nilgiri Apartment - Yamuna Apartment

Image 5.1 Demarcated Study area Source: Google earth.

2.3 METHODOLOGY Data Collection Data for the analysis was collected both from primary and secondary sources.

Primary data sources included: 1) Identifying the rainwater harvesting structures and their catchment areas (artificial recharge to groundwater) present in the area. The total amount of recharge because of these structures was estimated individually assuming 80% efficiency of structures.

2) Field testing of Pre and Post Monsoon 2010 water levels at different points within the study area. Water depth level changes are used as indicators for the successful augmentation of runoff water in aquifer after the establishment of RWH. 2) Field testing of water quality samples for pre and post monsoon 2010 at various points in the study area.

3) Interviews with Residents Welfare Associations (RWA) of each housing complex in the study area and Administrative officials to get historical information about water issues in the

area. Also to obtain information about the number of hours for which tubewells run in the area (to calculate groundwater extraction in the area) The sources of Secondary Data and their use is as given below: •

All the reference materials in the field (Ministry manuals, guides on the estimation of recharge by CGWB and relevant research papers) were collected prior starting up the project and an approach was accomplished.

•

Formal data from the local RWA offices in the forms of documents. Also public authority offices (MCD, DJB) were visited for any relevant information.

•

Design Criteria of Recharge Structures was collected from the RWA offices and inspected whether they are laid accordingly with the CGWB designs or modified if any to suit local conditions and space availability.

•

As most of the rainwater recharge structure has been completed with the assistance of FORCE NGO, so all the documents regarding proposals of projects, layout plans, finance/sponsors details etc. was collected. In addition, periodic depth level records, as well as yearly status of maintenance of these structures was also taken

•

By a generalized survey the Runoff which was expected in the documentation of recharging structures was assessed by taking into account all the components contributing to recharge by following formula.

Runoff = Catchment area * Runoff Coefficient * Rainfall

•

Runoff Coefficients (the mathematical factor that accounts for runoff loss by evaporation and retention on the surface itself) as given by Central Groundwater Board were taken.

Table 5.3 Type of catchment Runoff coefficient •

•

Roof Catchments o Tiles o Corrugated Metal Sheets Ground surface coverings o Concrete o Brick Pavement

Untreated ground catchments o Soil on slopes less than 10 percent o Rocky natural catchments o Green area Water Sampling

0.9 0.7 - 0.9

0.6 - 0.8 0.5 – 0.6

•

0.0 - 0.3 0.2 – 0.5 0.05 - 0.10

Sampling of water was performed in pre-monsoon (July 16, 2010). Water samples were drawn from the bore well nearest to recharge structure using sterilized sampling devices by a team comprising of Expert from MINMEC CONSULTANCY, one RWA Personnel, three coordinators from FORCE NGO. In housing societies where bore wells are not present samples were collected directly from the Recharge well. The samples were placed in

polyethylene bottles for chemical analysis and microbiological analysis, put into ice-bag containers and transported to the MINMEC laboratory the same day.

A total of 9 samples were collected. Out of them, 2 were drawn from the Mandakini apartment, from the rest of apartments one individual sample was collected for the analysis.

The samples were tested for pH, Electrical conductivity, TDS, Fluoride, Total hardness, Phosphate, Nitrate, Silica, E.Coli, TDS Chemical analysis The collected samples were chemically analyzed according to the standard methods for the examination of water.

Limitations of the Study

The study faced several limitations which made it impossible to get all the data that was required for a thorough comprehensive study. The key limitations were: 1) Non-Availability of government data about exact groundwater status of the area. We were surprised to find that neither the Delhi Jal Board nor the Municipal Corporation of Delhi, keep any records about the depth to water levels in their tubewells or about water quality of their tubewells. The lithographs or survey details made prior to / during the digging of tubewells by these agencies in the area were also not available.

2) The only government data that was available for groundwater was from Central Groundwater Board. This data too was not specific to our study area â&#x20AC;&#x201C; Alakananda.

The nearest peizometers (observation wells) from which the data is collected by Central Groundwater Board were at a distance of 4-5 km from our study area and were substantially different in terms of land usage, population density, dependence on tubewells and other characteristics which impact water levels in an area. Hence that data could not be used for comparison with current observed data 3) Consistent, year wise community records for water levels / depths were not available for most localities. Even details of rainwater harvesting projects were not available in the Residents Welfare Association offices. Apart from a general lack of necessity to maintain these records, another contributory factor was the change in the members of the Residents Welfare Association. The members who had made the rainwater harvesting systems were no longer in the RWA and had not passed on all the information about the rainwater harvesting systems.

4) Inability to take water level readings / samples in many areas. Since there were no observation wells made along with the rainwater harvesting projects, we had to take readings from abandoned tubewells in the vicinity or those in the recharge structures themselves. In many places, it was not possible to even access any of these and so we tried taking readings in working tubewells. This was impossible in most cases because the withdrawal pipe, cable wire and phalange joints in them do not allow our

water level indicator to move down the well. The distance of our sample tubewell from the recharge structure was also not standardised.

5) For the above reasons, the readings might not be accurately indicative of the status of groundwater level and quality in the area.

SECTION 3 3.1 DETAILS OF STUDY AREA Hydrometeorological Conditions Alaknanda, our study area is a micro catchment domain within NCT Delhi, so Delhi climate and precipitation pattern was used for the study due to lack of data for localized studied domain.

Table 5.2 Average Month-wise precipitation with rainy days in Delhi

Month

Jan

Feb

Ma r

Apr Ma . y

Jun

No v.

Dec Annu . al

38.

8 2.1

Jul Au Sep Oct y g 191 197 105 19. .6 .4 .3 3 7.4 7.9 4.0 0.8

Rainfall 14. 13.

9.9 5.5 9.2 (in mm) 5 2 Rainy days 1.2 1.0 0.8 0.5 0.8 Evaporation 71 101 177 300 400 (in mm) Source: Indian Meteorological Department

2.8

4.3

611.3

0.1

0.4

27.0

333

233

102

78

2224

133

147

149

The normal annual rainfall in the district is 611.3 mm. The rainfall in the district increases from the southwest to the northwest. About 81% of the annual rainfall is received during the monsoon months July, August and September. The rest of the annual rainfall is received as winter rain and as thunderstorm rain in the pre and post monsoon months as shown in The variation of rainfall from year to year is large. On an average rain of 2.5 mm or more falls on 27 days in the year, of these, 19 days are during the monsoon months. The average annual evaporation losses are 2224 mm

Hydrological Conditions

Alaknanda lies in the South District in political boundaries of Delhi region. The South district of NCT Delhi covers 250 Sq. Km. of area in which 45.2 Sq. Km. area shows mountainous undulating terrain exposed with Delhi quartzite.

The region is characterized by few meter of overburden composed of unconsolidated clay, silt, sand and varying proportions of Kankars, followed by quartzite. Moderately fractured zones in the quartzite are prevalent at the depth of 30 to 90 m and the fractures gradually decrease as depth increases . The weathered zone is found at every place above hard rock but thickness of weathered zone varies from place to place. The depth to water level varies widely in this district and is ranging from 30 to 65m bgl . The depth of fresh / saline water interface varies from 75 to 100 m. The thickness of the fresh water zone varies from 30 to

85 m. The yield of 30 to 50 m deep tube wells is 36 m続 /hr ( 8000 gallons/ hr) to 135 m続 /hr ( 30000 gallons/ hr) for 2.5 to 15m of drawdown. The groundwater quality is generally potable in nature.

Nitrate content varies between 98 to 980 ppm.

Image 5.2 Geological section of Alaknanda uncovered from the section of South district of Delhi. Source: CGWB

SECTION 4 4.1 FINDINGS & CONCLUSIONS Rainwater Harvesting status in Alakananda Most of the area in the housing colonies of Alakananda is concretized. Even the small parks in the area, have not been planned to receive surplus runoff from the surrounding catchment. Hence, due to the natural topography of the area, the rainwater runoff gets drained out quickly. The storm water drains that carry the runoff from rooftops and roads in the area too are concrete lined.

The geological structure of the area is such that it has a very low specific yield of 0.06-0.12.

According to CGWB records only 3%-5% of natural recharge can occur via natural pathway.

As a result, there is very little natural recharge to groundwater. Only the top soil stratum absorbs some water which also evaporates within a few days.

Thus ground water recharge occurring naturally is negligible.

Rainwater Harvesting for Artificial recharge to groundwater Several housing complexes in Alakananda have adopted rainwater harvesting. The number & potential of their rainwater harvesting structures are as given in the table below Apartment Name (Yr of completion of RWH) Mandakini (2007) NRI Complex (2006) Narmada (2009) Nilgiri (2008) Gangotri (2008) Aravali (2007 & 2009) *Yamuna Apartments

No. of Recharge structures 6

Runoff water expected to the structure (m続) 11,500

Quantified Recharge (80% efficiency) (m続) 9200

6

14,523

11,618

1

4000

3200

2

1500

1200

1

3900

3120

3

7800

6040

2

10,000

8,000

*Structures could not be opened for verification. Records were also not available Apart from those in Yamuna Apartments, none of the rainwater harvesting structures were made as a part of the initial construction of the flats. Rainwater Harvesting was neither a part of the developmental plan of Delhi Development Authority nor was it mentioned in the handing over documents as additional recommended works in the locality.

It was on the initiative of the environmentally aware and responsible citizens of Alakananda that so many rainwater harvesting structures were made later by the Residents Welfare Association of each area. The initial awareness about rainwater harvesting was created by NGO-FORCE and Coca-Cola India as a part of its Delh- wide campaign – JAL BEEMA ABHIYAAN. In this campaign, FORCE members along with Central Groundwater Board officials, Delhi Jal Board officials and the local political leaders went from locality to locality to create awareness and initiate action plans for rainwater harvesting.

All the structures were designed by Central Groundwater Board and FORCE and their construction was funded by the Residents Welfare Association. In many cases, the association also received support from corporates such as Coca-Cola India and from the rainwater harvesting financial support scheme by Delhi Jal Board.

The method usually followed is that of Recharge Trenches with one or more recharge wells.

The conduits used for transporting rainwater runoff to the structures are usually the storm water drains in the area. The structure has an arrangement for first flush with a semi-closed inlet i.e. a bypass arrangement for regular drain flow or first 10 minutes of mild rainfall has been provided. In many cases, shutters have been provided to manually monitor this process. The recharge structures are completely covered, equipped with ventilation apertures.

The local Resident Welfare Associations are responsible for the maintenance of the rainwater harvesting structures and their catchments. They are also educated on issues related to possible contaminants in runoff because of domestic waste water / garbage etc. The structures are cleaned in the pre monsoon season every year - the filters are excavated, cleaned and then filled back (here also corporate or government support is sometimes availed of by the RWAs). The conduits/ storm water drains are also cleaned of leaves, plastics and other clogging agents.

Groundwater draft as compared to Rainwater Harvesting

A Comparison of the average annual extraction of groundwater vis a vis the calculated artificial recharge to groundwater shows some interesting results Apartment Name (Year of completion) Mandakini (2007)

NRI Complex (2006)

No. of Recharge structures 6 {RT1=4 RS=1 RA=1} 6 {RT1=4 RT2=1 RS=1}

Recharge potential of to structure (m³ / yr) 11,500

14,523

Expected Recharge (at 80% efficiency (m³ / yr) 9200

11,618

No. of Bore wells (govt+Private ) 3 (1+2)

10 (0+10) [Small submersible s]

Annual draft of Ground water (m³/yr)**

Difference between Recharge and Draft (m³)

7776 + 1424

10,368

+ 1250

Narmada (2009) Nilgiri (2008)

1 {R T 2=1} 2 {R A =2}

4000

3200

1 (1+0)

4860

1660

1500

1200

0

0

+ 1200

Gangotri (2008)

1 {R S=1}

3900

3120

3 {3+0}

11,664

- 8544

Aravali (2009)

2 {R AB=2}

7800

6040

4 {4+0}

14,580

- 8540

Yamuna

2 (RT2)

10,000

8,000

2

7776

+ 224

Index : R T 1 = Recharge Trench with one recharge well R T 2 = Recharge Trench with two recharge wells RS = Recharge Shaft with borewell RA = Recharge trench with abandoned borewell **(avg. rate 1.5l/s & 0.8l/s for submersibles and avg.

time of 2.5hr/day for MCD and 1.5hr/day for Private Tube well Source: RWA records of Rainwater Harvesting done in their area and interviews with RWA members, MCD & DJB staff.

As can be seen from the above table, 1) With a well planned, implemented and maintained rainwater harvesting system, it is possible to recharge more to groundwater than is being withdrawn from the groundwater reserves by operational tubewells in the area

2) Hence Rainwater Harvesting can not only neutralise the impact of groundwater extraction, it can actually add a surplus to the aquifer thus leading to a long term rise in the water table.

3) With minimal maintenance and community involvement, rainwater harvesting is sustainable and its impact can be observed year after year.

Even in housing complexes like Narmada, Gangotri and Aravali, where though Rainwater harvesting has been done, the groundwater draft in the locality is much higher, atleast partial water balance is being achieved. Also, as subsequent results will show, the localised rise in water table around the recharge structure will actually increase the water table for the operational tubewells in the area.

Groundwater status Community Observations of water level The members of most of the Residentsâ&#x20AC;&#x2122; Welfare Associations in the area are aware citizens who take an active interest in the community issues of their localities. They are aware about

the potential benefits of rainwater harvesting. Many of them have also been observing the tubewells in their areas for any rise in yield / water table.

The table below lists down their observations on groundwater that they shared with us in the interviews we had with them.

Apartment Name (Year of completion)

Recharge potential of to structure (m続 / yr)

Premonsoon and post monsoon Water table fluctuation (m)

Mandakini (2007)

11,500

+2.5 (each year)

NRI Complex (2006)

14,523

+3

Narmada (2009)

4000

Nilgiri (2008)

1500

Gangotri (2008) ( Rishi apartments)

3900

Rise in water table in the first year itself after RWH

Aravali (2009)

7800

An MCD tubewell used for horticulture which had dried up, started yielding water after the first post RWH monsoon -

Yamuna

10,000

Structure made in 2010 -

It is clear from the observations above, that the RWAs have observed and recorded a rise in water table every year after the making of the rainwater harvesting structures. In case of structures which have been operational for several years now, the recorded rise is an average for those years. The RWA has either observed this rise in the Recharge Well itself, or in an operational tubewell near one of the RWH structures in the area.

Pre & Post Monsoon 2010 Water Level

S.NO

Society 1 NRI Complex

Structure Borewell (running)

2 Mandakini

Abandoned Borewell

3 Rishi 4 Nigiri 5 Narmada 6 Aravali 7 Yamuna

Pre-Monsoon Post-Monsoon 2010 water Level 2010 water Level ( mbgl) ( mbgl) 43 39.5 15.73

13.6

RWH Borewell

18.1 20.9

17 7.6

RWH

9.49

5.18

not available Not available

not available Not available

NOTES: 1) The pre and post monsoon depth readings for a locality were taken in the same borewell. Hence the comparisons are point to point comparisons 2) At some places it was not possible to take depth readings because of inability to lower measurement instrument into a nearby borewell / tubewell.

3) We had also approached Central Groundwater Board for sharing the water evel readings of their nearest Peizometer. However the nearest peizometers were in Pushpa Vihar and Tughlaquabad – both of which were more than 3-4 kms away from our study area. Those readings would not have been indicative of the local groundwater scenario.

Pre & Post Monsoon 2010 Water Quality The results of the chemical and microbiological analysis of the water samples are presented in Table7.2. The pre- monsoon pH values of the recharged water from aquifer ranged from 6.3 to 9.2 with a mean value of 7.9. It is easy to distinguish from the table that pH values of abandoned bore well are highly alkaline. This is because the sample has been taken from the top surface of static groundwater. Hence, it has surface influences and is not a true representation of aquifer water. Running bore wells provide satisfactory results.

Sampled water had low–medium values for conductivity (median conductivity 82.31µmScm1) and low–medium level of Total Dissolved Solid (158-1330 ppm.). In almost all the recharge borewell sample water was found to be well within fresh water range and the nearby running borewells has also got satisfactorily agreeable levels.

Fluoride was detected within permissible range in all the collected samples. The microbiological quality of the sampled water was assessed by examination of the common microbial indicator E. Coli yields very fine result. In all the collected water samples, except one E. Coli was not detected, Even in the only one, Narmada, it lies within permissible limits. This may be due to the fact that in Narmada Apartment the recharge structure is yet to start operational this monsoon so the sample collected was from static water level in the bore and may have colonies of bacteria.

The only Indicator which is to be dealt with was Nitrate. Normal permissible levels of Nitrate is 45 mg/l. In all the samples collected nitrate level was found to be very high, about ten times larger than permissible level.

The only satisfying result in concentration of nitrate was found in Mandakini Apartment recharge borewell i.e. 13.4 mg/l. which mean that in a properly maintained recharge structure and catchment Artificial recharge is not the causative factor of higher Nitrate level.

As per CGWB records nitrate concentration in the ground water of area is high and the artificial recharge is helping to dilute excess nitrate in Ground Aquifer.

In Artificial Recharge even if some nitrate contamination does happen, Desiltation chamber and slow sand filter carrying process of Biological denitrification, reduces nitrate to a gaseous nitrogen species. The gaseous product is primarily nitrogen gas, but it may also be nitrous oxide or nitric oxide. A broad range of bacteria, including many in the genera Pseudomonas, Micrococus, Archromobacter, Thiobacillus, and Bacillus can reduce nitrate.

Also natural biological denitrification occurs extensively if a sufficient source of reducing organic carbon is present. Such organic compounds as glucose, and starch or mixtures of these (e.g. a sugary brewery waste) are common carbon sources. If Catchment is not well maintained and household wastes or other contaminations carrying nitrate do enter Aquifer through Artificial recharge, then these above mentioned organic Carbon sources which are extensively utilized and present in extensive amount in each household would also be Recharged along with nitrate and enhance denitrification process acting as a catalyst.

But above such trend is not reflected in any other parameter like Total Hardness in terms of CaCO3 mg/l and phosphate level. Thus higher nitrate level is in Aquifer and Artificial Recharge is diluting to bring down its level in Alaknanda A comparison with post monsoon observations taken in December 2010, shows the results as shown in table .

The decrease in concentration of silica etc indicates a dilution natural water contaminants because of rainwater harvesting. The decrease in nitrates also indicates that the runoff is relatively free of sewage / leachates from dumped solid waste and has therefore contributed to the decline in the nitrate level of the groundwater. However, the increase in phosphates fluorides and TDH seems to indicate that the runoff contains residues from soaps / detergents and fluorinated water. This issue needs to be addressed by the RWAs through a stronger mass education drive on prevention of contamination to rainwater runoff.

Contribution of Aquifer Characteristics to Observed rise in Water Table The extraordinary results gained by Recharge structures in Alaknanda is also aided by local Hydro geological attributes of aquifer. The Geological section of Alakananda area as seen from Central Groundwater Board reports of the district shows that the aquifer is a confined aquifer

Image 5.3: Aquifer attributes of Alaknanda.

The Regional aquifer is bounded by hard rock interface on both sides so the horizontal water movement is not there. Hence the water recharged in the area, remains confined to this aquifer and bound within the localized domain. This is the reason why the rise in water table as because of the impact of artificial recharge to groundwater is so visible in Alakananda.

The above information also implies that this type of aquifer is very sensitive to excesssive extraction of groundwater. With insignificant natural recharge, and excessive withdrawal, the water table will deplete very rapidly. Hence joint efforts of communities and all the stakeholders are needed to ensure Alaknanda groundwater balance.

Financial Implications & Benefits Of Rainwater Harvesting

The number and size (and hence the cost) of rainwater harvesting structures in an area is directly related to the runoff available at the rainwater harvesting site. The cost is also related to the usage type of the area where the rainwater harvesting structure is being made. In all urban areas, the cost of community rainwater harvesting is relatively high because it has to be reinforced suitably so that the usage type of the top surface can be restored to its earlier status. Also, since the area is likely to be subjected to higher surface pressures, heavy concrete reinforcement are important to ensure safety of users and nearby buildings.

Designing a rainwater harvesting system that is retro-fitted onto an existing building / locality is also costlier because of the dismantling and adaptations that have to be done before the rainwater harvesting system can be installed. However, the cost of a Rainwater harvesting system designed as an integrated component of a new construction project is relatively much lower.

The cost borne per beneficiary of a community rainwater harvesting done in a planned colony, like those in Alaknanda, is much lesser as compared to similarly efficient structures

made by individuals. This is because of optimization of recharge potential at each rainwater harvesting site. Also in these areas, there are separate storm water drains, which join the MCD drains on the main road. These storm water drains carry water from the rooftops and the pavements. Hence, here the drains serve as collective conduits for recharge structures and no additional costs needs to be incurred for channelizing runoff to the structures.

We tried to calculate the total cost of rainwater harvesting that has been done in all the study areas in Alakananda. However, due to unavailability of records, we were not able to get costs for all structures made. Also, since the structures had been made in different years, a detailed exercise to calculate present value of the cost incurred would have been needed to get an accurate expenditure estimate.

However, on the basis of information we collected and estimates provided by RWA members, approximately Rs 35 lakh (Rs 3.5 million) has been spent on rainwater harvesting in the area. The total rainwater harvesting potential created with this amount is 53223 cu.m. per year.

Thus, if the lifespan of a rainwater harvesting project is assumed to be 20 years ( as per norms of CGWB), then the cost per litre of recharge is merely Rs. 0.003 /i.e. just Rs 3 per cu.m. With this minimal investment, the residents have ensured a sustainable, and growing source of water supply for themselves.

Infact, in most cases, the cost to the community of such projects is less than 33% of the cost mentioned above. This is because of the financial support extended for Rainwater harvesting projects by corporates such as Coca-Cola India and the Delhi government Cost saving because of Saving Energy In all areas where the water table is low, groundwater is pumped up with electricity driven submersible or surface installed water pumps. These motors usually vary in power from 1 HP to 7 HP (735 Watts to 5145 Watts). In Alakananda too similar motors are used for groundwater extraction.

In a study by Central Groundwater Board, it was shown that with every 1 meter rise in ground water level, energy consumption in withdrawal of water is reduced by 0.4 KWH ( Kilo Watt Hour).

In the study area, we were able to record 23 running tubewells ( though there might actually be more). These supply water to the parks present inside apartments and also to supply water during scarcity. On an average they are run for four hours (two mornings and two in the evening).

As the water level is deeper so an average 7 hp motor is present in each of these bore wells whose running cost is somewhat around 10-12 units (KWH) in an hour.

Hence total consumption would be 475 Kilo Watts per day.

So calculating the energy saving and money in electric bills will be:

Due to installation and well operational Recharge structure in Alaknanda water table has risen up by 3m. on an average in each of the apartment.

Using the CGWB norm of 0.4 KWH saved per metre of rise in water table, for each of the 23 tubewells, a saving of 4.8 Kilo Watts per day would have been made i.e approx 110 Kilo Watts per day would be saved Average cost of electricity in Delhi is

Rs. 4.15 per KWH (unit).

Thus total saving of electricity per day

Rs 457/ day Rs 13,710 per month Rs 1,64,720 per year

Thus with the installation of groundwater recharge structure in housing apartments in Alakananda; an amount of Rs. 13,710 per month and Rs. 1,64,720 per annum is saved.

Assuming no further increase in cost of electricity or no further increase in water table, even the current savings in electricity are enough to pay back the entire capital investment of the rainwater harvesting structures over their lifetime.

We did not go house to house asking whether they had tubewells. However, since Alakananda has been a water deficit area, it is reasonable to assume that there would be more private tubewells. Hence, the actual saving in electricity costs may be much higher than what has been shown in the above calculation.

Over and above the monetary saving, by cutting down on electricity consumption, rainwater harvesting will also contribute towards reduction in global warming.

Social Impact Of Rainwater Harvesting In Alakananda One of the strongest and most visible impacts of rainwater harvesting in Alakananda has been in community awareness, empowerment and recognition that they have received from all sectors.

Alakananda was one of the pioneers of rainwater harvesting in Delhi. Yamuna Apartments was the first to do rainwater harvesting though it was done as a part of the building construction and hence it was not noticed by other localities. Subsequently, Rishi Apartments made its rainwater harvesting structure. This was made with guidance from Centre for Science and Environment (and NGO). The project was widely publicised in media as one of the first models of rainwater harvesting in Delhi. This project was cited in all reports about rainwater harvesting as an example. It made Rishi Apartments a wellrecognised name among all environmentally aware people in Delhi.

However, the real social impact of rainwater harvesting in Alakananda, started to manifest itself after the project at NRI Complex was initiated by the Residents Welfare Association.

The project â&#x20AC;&#x201C; made with 50% financial support from Coca-Cola India â&#x20AC;&#x201C; was inaugurated by

the RWA with great fanfare. They invited all the RWAs of nearby colonies, all the residents of NRI complex, community leaders from other areas and the political leaders of the area – the MLA and the Municpal Counciller. The Chief Guest for the inaugural ceremony was the Honble Chief Minister of Delhi.

The RWA conducted a traditional ceremony (pooja) for an auspicious start to the project.

The ceremony and the Chief Minister’s personal support for rainwater harvesting was widely covered in media reports. Also, the involvement of the residents and other nearby RWAs in the project right from its inception, went a long way towards enthusing other community leaders to adopt the same in their areas.

The RWA of NRI complex got wide coverage in the media as responsible, environmentally aware citizens. The Chief Minister’s active involvement gave the RWA recognition also as partners with government in making Delhi Water Secure. RWAs from all over Delhi, got in touch with the NRI Complex RWA to understand the practical issues to be handled when doing rainwater harvesting. Since the NRI Complex RWA had a positive experience and reinforcement of self image through the project, they were a major influence for other RWAs to follow suit.

With a repetition of the same process in all other Alakananda Rainwater Harvesting projects, it has become a badge of honour for an RWA to have done rainwater harvesting. Also, the positive word-of mouth that was generated has probably been the single biggest contributor to the rainwater harvesting movement in Delhi.

There has been a spate of rainwater harvesting project implementations in the past 3-4 years. This has been fuelled largely by the media recognition given to the initial adopters in Alakananda. Also, the RWAs, government, NGOs such as FORCE and other supporters such as Coca-Cola India worked in close co-ordination making it possible to learn from each project and adapt the learnings for improvements in the future.

This sharing of learnings also impacted the government’s rainwater harvesting policy to make it more people friendly. The problems that RWAs encountered in taking support through the Delhi Government’s financial assistance scheme for rainwater harvesting were discussed with the authorities by the people themselves – notably those from NRI Complex, Mandakini Enclave etc. Based on the community recommendation, the government modified the policy to make sure that every RWA that took up rainwater harvesting was guaranteed atleast 50% of the support and the remaining too was to be expedited based on adherence to designs. Practical realities, like construction problems because of cable lines, drains etc were also discussed with the government. The subsequent policy modifications made the verification norms more flexible and accomodative of ground level realities.

Also, the close interaction with local political leaders created interest in them for rainwater harvesting. Through their word of mouth, the movement spread further. One interesting offshoot of the rainwater harvesting campaigns was that politicians got an opportunity to interact with the residents of each locality on a welfare issue in which there was no scope for negative politics. Their whole-hearted support to the NGOs has also helped cement a positive relationship between the RWAs and the political leaders.

The good response to rainwater harvesting and encouraging results, further encouraged the government to give more inducements – both financial and public image boosting - to the public to adopt rainwater harvesting. First, the Delhi Government made Rainwater Harvesting a key evaluation criterion with 25% weightage ,for RWA effectiveness. Based on RWA scores on these criterion, annual awards were given to the Best RWAs of Delhi. Hence, the best award almost always went to RWAs that had done rainwater harvesting. To top it all, the Chief Minister instituted a special award – The Chief Minister’s Best Rainwater Harvester Award - for RWAs and individuals who had adopted rainwater harvesting.

In 2008, Mandakini Enclave won the Chief Minister’s best Rainwater Harvesters Award. They were awarded their prize in the Annual Bhagidari Mela attended by 1600 Resident’s Welfare Associations and the bureaucratic heads of every department in Delhi government. They also made a presentation on the rainwater harvesting in their area to all RWAs. This was a big morale booster for Alakananda RWAs. Today, the RWAs of Alakananda and its residents are perhaps the strongest and most vocal champions of rainwater harvesting. Other civil society groups like Lioness Club, Rotary Club, Inner Wheel Club, Art of Living and RWAs of many other areas joined in the Rainwater Harvesting mission. As the ripples of learning spread, the recharge drive and the message of save water and share water travelled far and wide. It is because of this that rainwater harvesting in Delhi is primarily a voluntary, people led pogram. With more support to such RWAs, they can definitely help the city become the country’s first – WATER SECURE city Long Term Indirect Benefits of Rainwater Harvesting Much progress has been made in the last decade in understanding that water has not only an economic value, but social, religious, cultural and environmental values as well, and that these are often interdependent.

If we incorporate nonuse values (hidden benefits) of the water which is being recharged by these structures then these cost of making them will lag far behind the benefits they give.

Some of the non use values i.e. positive externalities are like: •

Benefits of preserving groundwater resource for future generations.

•

Prevention of degradation of ecosystem services.

•

Benefits to individuals through reduced expenditure on water disease treatment i.e. health-related costs.

•

Decreased water treatment costs by dilution of the contaminants which are generated due to excessive overdraft of water.

•

Increased property values due to ready availability of water.

SECTION 5 CASE STUDY Mandakini Apartments, Alakananda To add further to our understanding of the impact of artificial recharge through Rainwater harvesting, we took up a case study of Mandakini Enclave.

Mandakini enclave, a DDA colony in South Delhi, spread over 29 acres. It has 612 households. All the residents are middle class income group. It is a well maintained residential area. Since the water table all around was depleting, the residents took up cause and six Rainwater harvesting structure were constructed within the colony in a span of three months only in 2007.

Apartment is cleaned everyday by MCD and private sweepers. The ground has easy gradient on all sides. The subsurface topography of Mandakini is generally rocky on the surface, followed by alluvial soil at 3-4 meter depth and finally sand.

Before the start of the rainwater harvesting project, submersible pumps in extraction tube wells were lowered upto a depth of 45-50 m below ground level. Hence it may be assumed that the water table was 20-30 metres below ground level.

Rainwater Harvesting Details Source of water to the harvesting structure is only rain water through storm water drains.

•

Total catchment Area meters

About 80,000 sq.

•

Paved/ Rooftop/ Pucca area

45,000 sq. meters

•

Open/ Green area

35,000 sq. meters.

•

Annual Runoff

20,235 cum.

•

Runoff used for ground water

11500 cum.

Recharge and surface storage For checking the entry of contaminated water, shutters have been provided to the structures. This provides provision for bypass to prevent entry of contaminated water and allowing entry of rainwater during monsoon period. The shutters can be shut or opened when required.

The provision of bypass is essential as any accidental, regular household flow in the storm water drains, even during the monsoon, can be stopped from getting into RWH structure.

This ensures detergent and phenyl water thrown in balconies and open areas does not contaminate groundwater.

Regarding the conditions of drains leading to RWH chambers, because of natural slope, water flows smoothly in the drains and there is no stagnation. Also scavengers are engaged by the Mandakini Enclave RWA, for periodic cleaning and desilting of drains. In addition to these, Jalis have been provided at strategic places in the drains to keep them clean of debris.

Technical details of the project Central Ground Water Board provides help and guidance. Detailed field investigations were carried out and technical designs of rainwater harvesting structures were prepared.

Rainwater harvesting scheme adopted by Mandakini apartment has made use of an abandoned tube well, putting it to productive use which had otherwise no utility. Therefore the entire water harvesting scheme in the colony comprised of •

Recharge Trenches

4 nos

•

Recharge Shaft

1 nos

•

Recharge through abandoned tube well

1 nos

Fig. Detailed layout plan of Mandakini Apartment with location of Rainwater harvesting structures and flow of Runoff.

Example Of Design Of The Recharge Trenches Made In Mandakini

Partnerships with Stakeholders FORCE NGO which played a critical role in the adoption and fuelling Water recharge movement in Alaknanda is still active for the cause and organizes a number of promotional

activities involving the local residents.

Special workshops are organized by RWA with FORCE time to time for creating awareness among the residents of Rainwater harvesting and precautions to be taken to prevent contamination of water to these recharge structures. In addition circulars are issued on per year basis to the residents listing out “Do’s and Don’ts” to ensure safe and sustainable rain water harvesting. FORCE also guides and supports (with financial assistance from corporate partners like Coca-Cola India) RWAs for ensuring pre-monsoon annual maintenance of their RWH structures.

Financial Assistance The estimated expenditure on six structures was Rs. 5,70,000 which has been contributed as: •

Coca Cola (India) Ltd.

Rs. 3,00,000 (sponsor)

•

Residents of Mandakini enclave

Rs. 1,70,000/-

•

Government of NCT of Delhi

Rs 1,00,000/-

The Rs. 1, 00,000 contribution of Government of Delhi came from Delhi Jal Board under its BHAGIDARI SCHEME. The money was prudently deposited in RWA account by residents and was used subsequently in the annual cleaning and maintenance

Impact of Rainwater Harvesting on water levels in Mandakini Enclave The runoff expected to be available for the prepared artificial recharge structure was calculated to be 11,500 m³. Taking an efficiency of 80% of the recharge structure 9200 m³ of water is being recharged every year by harvesting Rainwater. The natural recharge is assumed to be negligible as almost entire apartment is built up and the smaller open areas due to their slope and geology are unable to significantly contribute towards groundwater recharge.

Mandakini Enclave Apartment has one MCD tube well for watering parks and other activities and two private tube wells. The average yield of all the tube wells was around 1.5 liter/s Also, interviews with local MCD workers and Residents Welfare Association reveals that average running time for MCD tube well was around 2.5 hour a day over the year and that of private one was around 1.5 hr. Therefore annual draft of ground water: 1.5*60*60*30*12*2.5/1000

+

1.5*60*60*30*12*1.5/1000

= 7776 m³ Thus every year 1424 m³ of water is successfully additionally injected into the aquifer even after taking into account the annual withdrawal of water for the

Apartment. That is perhaps the reason why that the result of artificial recharging in Mandakini apartment was reflected from the very first rainy season in 2007 given in the Table below.

TABLE 6.1

LEVEL OF WATER IN 2007(in meters)

Water Recharge structure unit no.

S1

May

June

July

August

Rise in water table

20

19

18

15

5

S2

25

23

26

22

3

S3

27

25

23

20

7

S4

20

18

17

15

5

S5

30

24

22

19

11

S6

25

23.5

19

22

3

Thus there has been on an average 5.5 m rise in the water table which was very encouraging in such a short period and as a result of only first rainy season for the system.

Mandakini Apartment was among the first apartment to adopt artificial recharge of Groundwater. They were also one of the first to win the Chief Ministerâ&#x20AC;&#x2122;s Special Rainwater Harvesting Award. It was their dedicated efforts, awards and success story of continuous rise in water table which inspired other neighboring colonies to adopt RWH. Cost to Community of doing rainwater harvesting Total cost of Scheme(including 6 recharging structures).

Rs. 6,00,000

Since there are 612 flats in the locality, the cost per flat is

Rs 600000/612

i.e community cost of making a capital investment in rainwater harvesting will be Rs.981/- per flat. This will make them water secure atleast for the next 20 years.

The rainwater harvesting structures also need to be maintained. Cost of maintenance is approx 2500/- per year per structure i.e Rs 15,000 per year.

Hence running cost of project per flat will be Rs 24 per year When compared with the fact that in Delhi the average household monthly bill for the highly subsidized metered water supply by DJB is Rs. 400-700 per month, this seems like a small price to pay for water security and mental peace.

SECTION 6 RECOMMENDATIONS New technology, traditional wisdom and people’s participation hold the key to resolving water management problems. This has successfully been demonstrated by the communities in Alaknanda.

The results from the artificial recharge schemes adopted by them have shown that there is a demonstrable, sustainable rise in water level because of rainwater harvesting. The results have also shown that the rise can be sustained even when there is large scale withdrawal of groundwater also from the same area.

The technology used for rainwater harvesting i.e. recharge trenches with recharge wells and the methodology for re-directing rainwater runoff to those structures, is also shown to be very efficient in adding to the active aquifers in an area. That is the reason why, despite there being little natural infiltration in the area because of large scale concreting, the recharge to groundwater was still made possible by the rainwater harvesting systems. The Impact Analysis report also shows that more needs to be done to prevent household used water flows into the rainwater harvesting systems or to add filters to the structure designs that remove soap water residues.

A cost-benefit analysis of rainwater harvesting in Alakananda, shows that with a nominal one time investment on asset creation of just Rs 1000/- and an annual Maintenance cost of Rs 25 / person, it is possible for a community to make itself Water Secure. Also, the savings in electricity consumption are enough to write off the entire cost of the project. Effectively, it means that it costs lesser for a community to adopt rainwater harvesting and make itself Water Secure, than it does to extract water with depleting ground water levels.

Rainwater Harvesting is a means of not just ensuring Water Security, but also of ensuring Community Empowerment and Participative Governance. When rainwater harvesting is adopted in a Partnership format with communities leading the way and administration supporting them, it can be a powerful tool for social transformation. As our experience in Alakananda showed, the Residents Welfare Associations moved from strength to strength simply because of their rainwater harvesting efforts. They not just made themselves water secure, but helped create a positive atmosphere of collective working. They became a credible voice for change – so much so that their inputs made the government modify its Rainwater Harvesting Policy.

The Study brings out another developmental perspective. Technological solutions need to be “appropriate” in order to contribute to development. Getting people involved and owning the changes is the key to its sustainability. Community participation must be allowed an important role in all conservation efforts, especially in urban water.

Alakananda was able to create within itself a microcosm reflecting the above developmental perspectives. This win-win situation not only enabled Alaknanda residents to increase its water resource when the entire south Delhi was dreading a water crisis. It also helped

Alakananda reduce risk and costs related to its own water supplies. In the process it set a model for effective and sustainable management of water supplies for Delhi government and for urban communities to influence policy change. In addition partnerships with NGOs and other local community groups offer a way of accessing experience and expertise in participatory approaches.

On the basis of the above, the recommendations for the future of rainwater harvesting are: 1) Rainwater Harvesting must be adopted in urban areas at a community level 2) For ensuring measurable rise in water levels, appropriate rainwater harvesting technology must be used to enable direct recharge to the active aquifer.

3) A community led and partnership based approach to rainwater implementation is necessary to ensure sustainability of the projects.

harvesting

4) Cleaning and maintenance of the structures needs to be planned in consultation with the community. This should also include maintenance of catchment topography and keeping it contamination free 5) Up-gradation of rainwater harvesting filtration system needs to be done to enable removal of soap residues from rainwater runoff in storm water conduits 6)

Community initiative and leadership in rainwater harvesting must be ensured. Media plans must include giving credit in mass media to the Community leaders. This is necessary to kickstart a voluntary, community led rainwater harvesting movement.