GANGA ACTION PLAN IN INDIA – AN OVERVIEWFile/Sikka[1].pdfGANGA ACTION PLAN IN INDIA – AN...
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GANGA ACTION PLAN IN INDIA – AN OVERVIEW
PRESENTATION BY BRIJESH SIKKA, DIRECTORMINISTRY OF ENVIRONMENT & FORESTS, GOVT. OF INDIA
SABESP INTERNATIONAL SEMINAR AT SAO PAULO, BRAZIL7TH TO 8TH NOVEMBER, 2006
STRUCTURE OF PRESENTATIONSTRUCTURE OF PRESENTATIONSTRUCTURE OF PRESENTATION
Background of the project
Sources of pollution, present status of water quality of rivers in India and River Action Plan Model
National River Conservation Plan
Ganga Action Plan
Appropriate technologies for sewage treatment
Lessons learnt & strategies/initiatives adopted
Area 3.28 million sq. km. (2% of world’s total )Population(2001) 1027 million(16% of world’s total)
(2005) 1060 millionCoordinates 80 4’ and 3706’ North latitudes
6807’ and 97025 East longitudesClimate Tropical (Tropic of Cancer divides India
two halves)Land Frontier 15,200 km.Coastline 7,500 km.No.of States/UTs 28 States and 7 Union Territories,
including the National Capital Region ofDelhi.
INDIA AT A GLANCE
BACKGROUNDBACKGROUND
Rivers in India are life lines of the people closely linked with our culture and tradition closely bound with the health and well being of large population
Restoring the health of rivers, which have become polluted, is very important
(Cleaning of major rivers is a monitorable target in 10th Five Year Plan)
Ganga at Hardwar during Kumbh
Total riverine length under different levels of pollution in India
Severely polluted
15%
Relatively clean66%
Moderatly polluted
19%
Severely pollutedModeratly pollutedRelatively clean
S.S.NoNo
Level of PollutionLevel of Pollution Pollution Pollution CriteriaCriteria
Riverine Riverine length, Km.length, Km.
Riverine length, Riverine length, percentagepercentage
01.01. Severely pollutedSeverely polluted BOD > 6 mg/lBOD > 6 mg/l 60866086 1515
02.02. Moderately Moderately pollutedpolluted
BOD 3BOD 3--6 mg/l6 mg/l 86918691 1919
03.03. Relatively cleanRelatively clean BOD < 3 mg/lBOD < 3 mg/l 3026630266 6666
WATER QUALITY STATUS
Analysis of 11 years data with respect to BOD values as indicator of organic pollution
River Basin >6 mg/l 3-6 mg/l <3 mg/l Total Indus 70 132 3917 4119Ganga 1760 3612 7318 12690Bramaputra 0 0 5013 5013Narmada 120 360 902 1382Mahanadi 210 370 1393 1973Godavari 960 856 2676 4492Krishna 840 956 1988 3784Cauvery 70 320 928 1318Other river basins 2056 2085 6131 10272
Total 6086 8691 30266 45043
Bio-Chemical Oxygen Demand (BOD)
River Basin-wise riverine length(in kms.)under different levels of pollution
MAIN SOURCES OF POLLUTIONMAIN SOURCES OF POLLUTION
DISPOSALOF DEADBODIES & ANIMAL
CARCASSES
OPEN DEFECATION
&CATTLE
WALLOWING
RUNOFF FROM SOLID &
MEDICAL WASTES &
AGRICULTRALFIELDS
NONNONPOINTPOINT
SOURCESSOURCES
20%
MUNICIPAL SEWAGEMUNICIPAL SEWAGE
INDUSTRIAL INDUSTRIAL POLLUTIONPOLLUTION
80%
POINT SOURCESPOINT SOURCES
Solid waste disposal
Animal bathingDisposal of dead body
NONNON--POINT SOURCES OF POLLUTIONPOINT SOURCES OF POLLUTION
Burning Ghat
Pollution from squatter settlements
POLLUTANT LOADS FROM VARIOUS SOURCES IN GANGA BASIN
Non-point (livestock)
0.5%
Non-point (agricultural
runoff)3.2%
Non-point (household in
rural areas)2.1%
Point (municipal
sewage from urban areas)
78.2%
Point (industry)16.0%
Pollution contribution from in-river activities such as cattle wallowing, washing of clothes, throwing of half-burnt/unburnt bodies and flowers into the river is very minor but difficult to estimate. However, these need to be controlled in order to maintain the aesthetics & hygienic condition of the river.
CLASSIFICATION OF WATER QUALITY OF INDIAN RIVERS
CLASSIFICATION OF WATER QUALITY CLASSIFICATION OF WATER QUALITY OF INDIAN RIVERSOF INDIAN RIVERS
A.DRINKING WATER SOURCE WITHOUT CONVENTIONAL TREATMENT BUT AFTER DISINFECTION
B.OUTDOOR BATHING
C.DRINKING WATER SOURCE WITH CONVENTIONAL TREATMENT FOLLOWED BY DISINFECTION
D.PROPOGATION OF WILD LIFE
E. IRRIGATION, INDUSTRIAL COOLING AND WATER DISPOSAL
A.A. DRINKING WATER SOURCE WITHOUT CONVENTIONAL DRINKING WATER SOURCE WITHOUT CONVENTIONAL TREATMENT BUT AFTER DISINFECTIONTREATMENT BUT AFTER DISINFECTION
B.B. OUTDOOR BATHINGOUTDOOR BATHING
C.C. DRINKING WATER SOURCE WITH CONVENTIONAL DRINKING WATER SOURCE WITH CONVENTIONAL TREATMENT FOLLOWED BY DISINFECTIONTREATMENT FOLLOWED BY DISINFECTION
D.D. PROPOGATION OF WILD LIFEPROPOGATION OF WILD LIFE
E.E. IRRIGATION, INDUSTRIAL COOLING AND WATER DISPOSALIRRIGATION, INDUSTRIAL COOLING AND WATER DISPOSAL
BATHING QUALITY (B CLASS) BATHING QUALITY (B CLASS) STANDARD FOR INDIAN RIVERSSTANDARD FOR INDIAN RIVERS
BODBOD -- BIOBIO--CHEMICAL OXYGEN DEMANDCHEMICAL OXYGEN DEMANDDODO -- DISSOLVED OXYGENDISSOLVED OXYGENMPNMPN -- MOST PROBABLE NUMBERMOST PROBABLE NUMBER
BODBOD 3 mg/l (MAXIMUM)3 mg/l (MAXIMUM)
DO DO 5 mg/l (MINIMUM)5 mg/l (MINIMUM)
COLIFORM (FAECAL)COLIFORM (FAECAL) 500 (DESIRABLE)500 (DESIRABLE)
2500 (MAX. PERMISSIBLE)2500 (MAX. PERMISSIBLE)
PERMISSIBLE LIMITPERMISSIBLE LIMITPARAMETERSPARAMETERS
MPN 100 ml
Pollution abatement works in major rivers in the country commenced with the launching of Ganga Action Plan (GAP) Phase-I in 1985
GAP-I was extended as GAP-II from 1993 onwards to cover Gomti, Yamunaand Damodar, three main tributaries of Ganga
Pollution abatement works in major rivers in the country commePollution abatement works in major rivers in the country commenced with nced with the launching of the launching of GangaGanga Action Plan (GAP) PhaseAction Plan (GAP) Phase--I in 1985I in 1985
GAPGAP--I was extended as GAPI was extended as GAP--II from 1993 onwards to cover II from 1993 onwards to cover GomtiGomti, , YamunaYamunaand and DamodarDamodar, three main tributaries of , three main tributaries of GangaGanga
The The programmeprogramme was further broad based in 1995 to include other major rivers was further broad based in 1995 to include other major rivers and reand re--named as National River Conservation Plan (NRCP)named as National River Conservation Plan (NRCP)
NATIONAL RIVER CONSERVATION PLAN (NRCP)
NATIONAL RIVER CONSERVATION PLAN NATIONAL RIVER CONSERVATION PLAN (NRCP)(NRCP)
Maha Kumbh at Allahabad
NATIONAL RIVER CONSERVATION PLANNATIONAL RIVER CONSERVATION PLAN
A National River Conservation Authority (NRCA) chaired by the Hon’ble Prime Minister of India is in place to provide the policy framework and oversee implementation of NRCP
Chief Ministers of the concerned States, Union Ministers and various experts are its members
The National River Conservation Directorate (NRCD) The National River Conservation Directorate (NRCD) coordinates implementation of pollution abatement schemes under the NRCP
NRCP presently covers 160 towns along 34 stretches of polluted NRCP presently covers 160 towns along 34 stretches of polluted rivers in 20 Statesrivers in 20 States
Present approved cost of NRCP is Rs. 4735 crore ( around US $ Present approved cost of NRCP is Rs. 4735 crore ( around US $ 1 1 billion) billion)
FUNDING PATTERN
Projects approved before March, 2001 are 100% funded by the Central Government with land cost to be borne by the concerned State Government
Projects approved after March, 2001 are being funded on 70:30 cost sharing basis between Centre and the State
Out of the State share of 30%, local bodies to contribute 10% of the cost
Operation and maintenance (O&M) of assets created is the full responsibility of the State Government/local body
FUNDING PATTERNFUNDING PATTERN
Projects approved before March, 2001 are 100% funded by the Projects approved before March, 2001 are 100% funded by the Central Government with land cost to be borne by the concerned Central Government with land cost to be borne by the concerned State Government State Government
Projects approved after March, 2001 are being funded on 70:30 coProjects approved after March, 2001 are being funded on 70:30 cost st sharing basis between Centre and the Statesharing basis between Centre and the State
Out of the State share of 30%, local bodies to contribute 10% oOut of the State share of 30%, local bodies to contribute 10% of the f the costcost
Operation and maintenance (O&M) of assets created is the full Operation and maintenance (O&M) of assets created is the full responsibility of the State Government/local bodyresponsibility of the State Government/local body
NATIONAL RIVER CONSERVATION PLAN NATIONAL RIVER CONSERVATION PLAN NATIONAL RIVER CONSERVATION PLAN
NRCANRCA(HON’BLE PRIME MINISTER)(HON’BLE PRIME MINISTER)
IN STATESIN STATESMINISTRY OFMINISTRY OF
ENV. & FORESTSENV. & FORESTSMONITORINGCOMMITTEE
(MEMBER, PLANNINGCOMMISSION)CHIEF CHIEF
SECRETARYSECRETARY
STEERING COMMITTEESTEERING COMMITTEE(SECY. ENV & FORESTS)(SECY. ENV & FORESTS)
STATESTATENODAL DEPT.NODAL DEPT.
PROJECT PROJECT MONITORING CELLMONITORING CELLUNDER DIVISIONALUNDER DIVISIONAL
COMMISSIONERCOMMISSIONER
STANDING STANDING COMMITTEE (MEF)COMMITTEE (MEF)
PROJECTADVISORY
COMMITTEE
NRCDNRCDSECRETARIATSECRETARIAT
MONITORING MECHANISMMONITORING MECHANISMMONITORING MECHANISM
T O W NT O W N
R I V E R
RIVER ACTION PLAN MODELRIVER ACTION PLAN MODEL
CREMATORIACREMATORIA
RFDRFDLCSLCS
FORIRRIGATION
FORIRRIGATION
TREATED EFFLUENTTREATED EFFLUENT
SEWERSEWER
RFDRFD
NA
LLA
S
INDUSTRY
ETPETP
STPSTPPUMPINGSTATIONPUMPINGSTATION
NATIONAL RIVER CONSERVATION PLAN NATIONAL RIVER CONSERVATION PLAN NATIONAL RIVER CONSERVATION PLAN
Major type of works covered under NRCP and their capital cost inpercentage terms vis-à-vis the total project cost:
Interception & diversion of sewage – 52%Sewage treatment plants – 37%Low cost sanitation – 7%Crematoria – 0.6%Ghat/river front development – 1.2%Public awareness & participation – 0.3%
The component of ‘Institutional strengthening and capacity building of local bodies’ is now also being taken up for ensuring greater sustainability of the sanctioned projects
Major type of works covered under NRCP and their capital cost inMajor type of works covered under NRCP and their capital cost inpercentage terms vispercentage terms vis--àà--vis the total project cost:vis the total project cost:
Interception & diversion of sewage Interception & diversion of sewage –– 52%52%Sewage treatment plants Sewage treatment plants –– 37%37%Low cost sanitation Low cost sanitation –– 7%7%Crematoria Crematoria –– 0.6%0.6%GhatGhat/river front development /river front development –– 1.2%1.2%Public awareness & participation Public awareness & participation –– 0.3%0.3%
The component of ‘Institutional strengthening and capacity The component of ‘Institutional strengthening and capacity building of local bodies’ is now also being taken up for ensurinbuilding of local bodies’ is now also being taken up for ensuring g greater sustainability of the sanctioned projects greater sustainability of the sanctioned projects
78 mld UASB STP at Agra
GANGA BASINGANGA BASINGANGA BASIN
River Ganga originates from Himalayas and traverses approximately 2500 kms. before discharging into Bay of Bengal.Catchment area of Ganga Basin is about 840,000 km2 (25% of India’s landmass)
River Ganga originates from Himalayas and traverses approximatelRiver Ganga originates from Himalayas and traverses approximately y 2500 2500 kmskms. before discharging into Bay of Bengal.. before discharging into Bay of Bengal.CatchmentCatchment area of Ganga Basin is about 840,000 kmarea of Ganga Basin is about 840,000 km22 (25% of India’s (25% of India’s landmass)landmass)
Nearly 400 million people (40% of the country population) live in the Basin
Ganga is regarded as a sacred river and extensively used for bathing, apart from serving as source of water supply and irrigation
GANGA ACTION PLAN (GAP) PHASE-IGANGA ACTION PLAN (GAP) PHASEGANGA ACTION PLAN (GAP) PHASE--II
The Ganga Action Plan Phase-I (GAP-I) was launched in 1985
GAP-I covered 25 Class-I towns (having population above 100,000) in 3 states
The Ganga Action Plan PhaseThe Ganga Action Plan Phase--I (GAPI (GAP--I) was launched in 1985I) was launched in 1985
GAPGAP--I covered 25 ClassI covered 25 Class--I towns (having population above 100,000) I towns (having population above 100,000) in 3 statesin 3 states
GAPGAP--I has been completed at a I has been completed at a cost of Rs. 452 crore (US $ 100 cost of Rs. 452 crore (US $ 100 million)million)
Sewage treatment plants having Sewage treatment plants having capacity of 865 capacity of 865 mldmld have been have been createdcreated
GANGA ACTION PLAN PHASE-IIGANGA ACTION PLAN PHASEGANGA ACTION PLAN PHASE--IIII
Under GAP-I, 865 mld i.e. only 65% of the original pollution load of 1340 mld could be tackled. This percentage as per the present pollution load of 2900 mld has been reduced to around 30%
Due to financial constraints, the balance pollution load is being tackled in phases under the 2nd phase of GAP
Under GAPUnder GAP--I, 865 I, 865 mldmld i.e. only 65% of the original pollution load of i.e. only 65% of the original pollution load of 1340 1340 mldmld could be tackled. This percentage as per the present could be tackled. This percentage as per the present pollution load of 2900 pollution load of 2900 mldmld has been reduced to around 30%has been reduced to around 30%
Due to financial constraints, the balance pollution load is beinDue to financial constraints, the balance pollution load is being g tackled in phases under the 2tackled in phases under the 2ndnd phase of GAPphase of GAP
Pollution abatement works in 59 towns Pollution abatement works in 59 towns in 5 States costing in 5 States costing RsRs. 653 . 653 CroreCrore (around (around US $ 150 million) are presently under US $ 150 million) are presently under implementation under GAP Phaseimplementation under GAP Phase--IIII
Additional sewage treatment capacity of Additional sewage treatment capacity of 780 780 mldmld is envisaged under GAP Phaseis envisaged under GAP Phase--IIII
STP at Kolkata
2,2
10,6
8,6
5,1
15,5
4.5 5,4
3,12.3 2,2
0
2
4
6
8
10
12
14
16
KANNAUJ KANPUR ALLAHABAD VARANASI PATNA
1986 2005
STANDARD( 3 mg/l or less)
Bio-chemical Oxygen Demand(Summer Average)
BO
D(m
g/l)
1987
TOWNS
IMPROVEMENT IN WATER QUALITY OF GANGAIMPROVEMENT IN WATER QUALITY OF GANGADespite rapid increase inDespite rapid increase in population, urbanization & industrial growth, the water population, urbanization & industrial growth, the water quality of quality of GangaGanga has shown discernible improvement over the prehas shown discernible improvement over the pre--GAP periodGAP period
6,66,5 6,75,9
8,1 8.08.38,4
4,7
7.6
0
1
2
3
4
5
6
7
8
9
KANNAUJ KANPUR ALLAHABAD VARANASI PATNA
1986 2005
TOWNS
Dissolved Oxygen (Summer Average)
DO
(mg/
l)
1987
STANDARD( 5 mg/l or more)
IMPROVEMENT IN WATER QUALITY OF GANGAIMPROVEMENT IN WATER QUALITY OF GANGA
Mid-term Evaluation of GAP-I carried out by experts from universities and R&D institutions in 1995 concluded that
Reduction of discharge of organic matter, a necessary first step in restoring the water quality has been achieved to a fair level GAP as conceived and implemented is an appropriate programme for application to other river basins also
A Cost Benefit Analysis of GAP-I carried out by Harvard Institute of International Development from 1996-98 concluded that
River cleanup programmes involve a long time period and large resources for effective actionIn terms of both the time taken and cost involved, GAP compares favourably with those of other major rivers of the world like Thames, Rhine and Danube
MidMid--term Evaluation of GAPterm Evaluation of GAP--I carried out by experts from I carried out by experts from universities and R&D institutions in 1995 concluded thatuniversities and R&D institutions in 1995 concluded that
Reduction of discharge of organic matter, a necessary first stepReduction of discharge of organic matter, a necessary first step in in restoring the water quality has been achieved to a fair level restoring the water quality has been achieved to a fair level GAP as conceived and implemented is an appropriate GAP as conceived and implemented is an appropriate programmeprogramme for for application to other river basins alsoapplication to other river basins also
A Cost Benefit Analysis of GAPA Cost Benefit Analysis of GAP--I carried out by Harvard Institute I carried out by Harvard Institute of International Development from 1996of International Development from 1996--98 concluded that98 concluded that
River cleanup River cleanup programmesprogrammes involve a long time period and large involve a long time period and large resources for effective actionresources for effective actionIn terms of both the time taken and cost involved, GAP compares In terms of both the time taken and cost involved, GAP compares favourablyfavourably with those of other major rivers of the world like Thames, with those of other major rivers of the world like Thames, Rhine and Danube Rhine and Danube
EVALUATION OF GAP PHASEEVALUATION OF GAP PHASE--II
PRESENT FOCUS OF GANGA ACTION PLAN PHASE-II
PRESENT FOCUS OF GANGA ACTION PRESENT FOCUS OF GANGA ACTION PLAN PHASEPLAN PHASE--IIII
Need for prioritization of works due to financial constraints
Pollution level of river Ganga and its tributaries in the middle stretch is comparatively higher due to:- low river flow resulting in lower dilution effect - higher pollutant contribution from towns located in this
densely populated zoneTherefore, 4 large, important and rapidly expanding towns (2-3% per annum population growth rate) in the critical middle stretch of the river, which are major sources of pollution, are the main focus for taking up pollution abatement works under GAP-II in future
Need for prioritization of works due to financial constraintsNeed for prioritization of works due to financial constraints
Pollution level of river Ganga and its tributaries in the middlPollution level of river Ganga and its tributaries in the middle stretch e stretch is comparatively higher due to:is comparatively higher due to:-- low river flow resulting in lower dilution effect low river flow resulting in lower dilution effect -- higher pollutant contribution from towns located in thishigher pollutant contribution from towns located in this
densely populated zonedensely populated zone
Therefore, 4 large, important and Therefore, 4 large, important and rapidly expanding towns (2rapidly expanding towns (2--3% per 3% per annum population growth rate) in annum population growth rate) in the critical middle stretch of the the critical middle stretch of the river, which are major sources of river, which are major sources of pollution, are the main focus for pollution, are the main focus for taking up pollution abatement taking up pollution abatement works under GAPworks under GAP--II in future II in future
PRESENT FOCUS OF GANGA ACTION PLAN PHASE-II
PRESENT FOCUS OF GANGA ACTION PRESENT FOCUS OF GANGA ACTION PLAN PHASEPLAN PHASE--IIII
Project proposals for the towns of Kanpur, Allahabad and Varanasi on main river Ganga and Lucknow on river Gomti prepared under the JICA (Japan International Cooperation Agency) aided Development Study on ‘Water Quality Management Plan for Ganga river’
These project proposals had been posed to JBIC (Japan Bank for International Cooperation) for assistance
Project proposal for Varanasi has already been approved by JBIC for funding
Project proposals for the other three towns are under consideration of JBIC for funding in future as a part of their ODA Rolling Plan package
Project proposals for the towns of Project proposals for the towns of KanpurKanpur, Allahabad and , Allahabad and VaranasiVaranasi on on main river main river GangaGanga and and LucknowLucknow on river on river GomtiGomti prepared under the prepared under the JICA (Japan International Cooperation Agency) aided Development JICA (Japan International Cooperation Agency) aided Development Study on ‘Water Quality Management Plan for Study on ‘Water Quality Management Plan for GangaGanga river’river’
These project proposals had been posed to JBIC (Japan Bank for These project proposals had been posed to JBIC (Japan Bank for International Cooperation) for assistanceInternational Cooperation) for assistance
Project proposal for Project proposal for VaranasiVaranasi has already been approved by JBIC for has already been approved by JBIC for funding funding
Project proposals for the other three towns are under consideratProject proposals for the other three towns are under consideration of ion of JBIC for funding in future as a part of their ODA Rolling Plan JBIC for funding in future as a part of their ODA Rolling Plan package package
GANGA ACTION PLAN PROJECT AT VARANASI
GANGA ACTION PLAN PROJECT AT GANGA ACTION PLAN PROJECT AT VARANASIVARANASI
Project cost estimated at around Rs. 500 crore (US $ 110 million)
Assistance being received from JBIC for 85% of the project cost.
Project consists of the following components:Sewerage system (laying of new as well as rehabilitating the existing sewerage system)200 mld sewage treatment plant Community toilet complexes in slum areas Construction of dhobi/washermen ghats and bathing ghatsPublic awareness & participation programmeInstitutional development programmefor the local body
Project cost estimated at around Project cost estimated at around RsRs. 500 . 500 crorecrore (US $ 110 million) (US $ 110 million)
Assistance being received from JBIC for 85% of the project cost.Assistance being received from JBIC for 85% of the project cost.
Project consists of the following components:Project consists of the following components:Sewerage system (laying of new as well as rehabilitating the Sewerage system (laying of new as well as rehabilitating the existing sewerage system)existing sewerage system)200 200 mldmld sewage treatment plant sewage treatment plant Community toilet complexes in slum areas Community toilet complexes in slum areas Construction of dhobi/Construction of dhobi/washermen washermen ghatsghats and bathing and bathing ghatsghatsPublic awareness & participation Public awareness & participation programmeprogrammeInstitutional development Institutional development programmeprogrammefor the local body for the local body Ghat at Varanasi
SEWAGE GENERATION & TREATMENT CAPACITY IN INDIA
SEWAGE GENERATION & TREATMENT SEWAGE GENERATION & TREATMENT CAPACITY IN INDIACAPACITY IN INDIA
Total population of India (2001) - 1027 millionPopulation in urban areas - 285 millionClass I Cities (population > 100,000) - 414Class II Cities (population 50,000-100,000) - 489Total sewage generation (2001) - 29129 mldInstalled STP capacity - 6190 mld
(21.3 %)Treatment capacity gap - 22939 mld
(78.7%)Planned treatment capacity - 1742.6 mld
(6.0%)
Total population of India (2001) Total population of India (2001) -- 1027 million1027 millionPopulation in urban areas Population in urban areas -- 285 million285 millionClass I Cities (population > 100,000) Class I Cities (population > 100,000) -- 414414Class II Cities (population 50,000Class II Cities (population 50,000--100,000) 100,000) -- 489489Total sewage generation (2001)Total sewage generation (2001) -- 29129 29129 mldmldInstalled STP capacity Installed STP capacity -- 6190 6190 mldmld
(21.3 %)(21.3 %)Treatment capacity gap Treatment capacity gap -- 22939 22939 mldmld
(78.7%)(78.7%)Planned treatment capacityPlanned treatment capacity -- 1742.6 1742.6 mldmld
(6.0%)(6.0%)
STANDARDS FOR TREATED SEWAGESTANDARDS FOR TREATED SEWAGEUNDER NRCPUNDER NRCP
FOR DISCHARGEFOR DISCHARGE
INTO WATER BODYINTO WATER BODY ON LANDON LAND
BOD (mg/l)BOD (mg/l)
T S S (mg/l)T S S (mg/l)
FAECAL (MPN/100 ml)FAECAL (MPN/100 ml)COLIFORMSCOLIFORMS
3030
5050
10001000
1000010000
100100
200200
(Desirable)(Desirable)
(Maximum)(Maximum)
SELECTION OF APPROPRIATE SEWAGE TREATMENT TECHNOLOGY
SELECTION OF APPROPRIATE SEWAGE SELECTION OF APPROPRIATE SEWAGE TREATMENT TECHNOLOGYTREATMENT TECHNOLOGY
Large number of STPs constructed under GAP Phase-I were based on activated sludge process (ASP) and trickling filter technology
Problems encountered in their proper O&M due to Large power requirementHigh O&M cost Frequent power breakdowns Financial constraints of the maintaining agency/local bodyNon-availability of adequate skilled manpower to run these STPs
This led to the need for selection of appropriate sewage treatment technologies more suited to local conditions under NRCP
Large number of Large number of STPsSTPs constructed under GAP Phaseconstructed under GAP Phase--I were based on I were based on activated sludge process (ASP) and trickling filter technologyactivated sludge process (ASP) and trickling filter technology
Problems encountered in their proper O&M due to Problems encountered in their proper O&M due to
Large power requirementLarge power requirementHigh O&M cost High O&M cost Frequent power breakdowns Frequent power breakdowns Financial constraints of the maintaining agency/local bodyFinancial constraints of the maintaining agency/local bodyNonNon--availability of adequate skilled manpower to run these availability of adequate skilled manpower to run these STPsSTPs
This led to the need for selection of appropriate sewage treatmeThis led to the need for selection of appropriate sewage treatment nt technologies more suited to local conditions under NRCPtechnologies more suited to local conditions under NRCP
SELECTION OF APPROPRIATE SEWAGE TREATMENT TECHNOLOGY
SELECTION OF APPROPRIATE SEWAGE SELECTION OF APPROPRIATE SEWAGE TREATMENT TECHNOLOGYTREATMENT TECHNOLOGY
MAJOR FACTORS AFFECTING CHOICE OF TREATMENT TECHNOLOGY
Wastewater flow and characteristics
Degree of treatment required
Availability, cost and requirement of land
Power requirement for the technology
Ability of a technology to withstand power failures
Capital cost
Ease in maintenance, availability of skilled staff
Extent of sludge production and its disposal requirements (sludge disposal is often difficult and may involve substantial part of the STP cost)
MAJOR FACTORS AFFECTING CHOICE OF TREATMENT TECHNOLOGYMAJOR FACTORS AFFECTING CHOICE OF TREATMENT TECHNOLOGY
Wastewater flow and characteristics Wastewater flow and characteristics
Degree of treatment requiredDegree of treatment required
Availability, cost and requirement of landAvailability, cost and requirement of land
Power requirement for the technologyPower requirement for the technology
Ability of a technology to withstand power failuresAbility of a technology to withstand power failures
Capital cost Capital cost
Ease in maintenance, availability of skilled staff Ease in maintenance, availability of skilled staff
Extent of sludge production and its disposal requirements (sludExtent of sludge production and its disposal requirements (sludge disposal is ge disposal is often difficult and may involve substantial part of the STP costoften difficult and may involve substantial part of the STP cost) )
SELECTION OF APPROPRIATE SEWAGE SELECTION OF APPROPRIATE SEWAGE TREATMENT TECHNOLOGYTREATMENT TECHNOLOGY
Conventional Activated Sludge Process (ASP)Up-flow Anaerobic Sludge Blanket (UASB) + Polishing Pond (+aeration?)Fluidized Aerobic Bio-Reactor (FAB)/Moving Bed Bio-Reactor (MMBR)Aerated Lagoon Waste Stabilization Pond (WSP)Karnal Technology/ Sewage fed agro-forestry
Treatment technologies considered
O & M aspectsCost (Construction and O&M)Land RequirementResource recovery and reuse (gas, sludge and treated water)
Life cycle cost comparison of the various treatment options
UPFLOW ANAEROBIC SLUDGE BLANKET (UASB) PROCESS
UPFLOW ANAEROBIC SLUDGE UPFLOW ANAEROBIC SLUDGE BLANKET (UASB) PROCESSBLANKET (UASB) PROCESS
Process based on upward flow of wastewater through a sludge layeProcess based on upward flow of wastewater through a sludge layer of micror of micro--organisms. organisms. Organic matter digested by microOrganic matter digested by micro--organisms in the digestion compartment.organisms in the digestion compartment.
Mixture of bioMixture of bio--gas, sludge and water enter a three phase separator. Biogas, sludge and water enter a three phase separator. Bio--gas is separated in a gas is separated in a gas collector, sludge particles settle in the settling chamber agas collector, sludge particles settle in the settling chamber and flow back to the digestion nd flow back to the digestion compartment, while the treated effluent is discharged via an ovecompartment, while the treated effluent is discharged via an overflow weir.rflow weir.
AdvantagesLow energy requirement / minimal electro –mechanical devices
Lower HRT and hence more compact installation
Lower production of stabilized excess sludge
Production and recovery of bio-gas (with higher calorific value), which can be used as an energy source
System is resilient to peak loading and power cuts
Relatively simple routine O&M
UPFLOW ANAEROBIC SLUDGE BLANKET (UASB) PROCESS
UPFLOW ANAEROBIC SLUDGE UPFLOW ANAEROBIC SLUDGE BLANKET (UASB) PROCESSBLANKET (UASB) PROCESS
DisadvantagesAdequate post treatment (polishing pond or aerated lagoon) of UASB effluent is required to meet the discharge standards
Anaerobic bacteria (particularly methanogens) are susceptible to inhibition by a large number of toxic compounds
Start-up of the process is relatively slow if seed sludge is not available
Fecal coliform removal in the process is poor
Due to anaerobic activity the structures of the STP are likely to corrode faster. Anti-corrosive treatment is required for various parts of the STP Yamuna Nagar STP
FLUIDIZED AEROBIC BIO-REACTOR (FAB) FLUIDIZED AEROBIC BIOFLUIDIZED AEROBIC BIO--REACTOR (FAB) REACTOR (FAB)
42 mld STP at Lucknow
A submerged attached growth aerobic process having fluidized bed of plastic media as a base for bio-film in deep reactors
Bacterial reaction carried out in two stages for maximizing the BOD removal efficiency
AdvantagesVery low space requirement (nearly 1/5th to
1/8th of ASP process). Thus very compact installation
Low temperature sustaining capability
Does not require sludge recycling
Sludge handling is easy as it is fully digested and is lower than other aerobic technologies
Very high coliform removal. A chlorine dose of around 3 mg/l is sufficient to meet the standards
Existing treatment facilities can be upgraded by conversion of existing tanks to FAB reactors with small modifications
WASTE STABILIZATION PONDSWASTE STABILIZATION PONDSWASTE STABILIZATION PONDS
Process based on solar energy and, therefore, appropriate for Indian climatic conditions
Treatment system comprises of three types of ponds in series (anaerobic pond – 1 day HRT, facultative pond – 5 days HRT and maturation pond – 3 to 4 days HRT)
Anaerobic and facultative ponds enable BOD reduction while maturation ponds enable pathogen removal
Multiple number of facultative and maturation ponds can be provided to suit the treated effluent quality, including fecal coliform standards
The system has very low O&M costs
Requires minimal trained manpower
The system is extremely robust and can withstand hydraulic and organic shock loads
Requires large land area (1.0 – 2.0 Ha./mlddepending upon temperature and sewage characteristics)
KARNAL TECHNOLOGY(Sewage fed Agro-forestry)
KARNAL TECHNOLOGYKARNAL TECHNOLOGY(Sewage fed Agro(Sewage fed Agro--forestry)forestry)
Methodology consists of growing trees on ridges (1 m wide, 50 cm high) and disposing untreated sewage in furrows or shallow trenches (2 m wide)
The total discharge of untreated sewage is regulated (5- 15 cm in depth) so that it is consumed within 12 – 18 hours and there is no standing water left in the trenches
Each tree acts as a bio- pump, absorbing water and nutrients from the sewage and releasing water into the environment through transpiration
Amount of untreated sewage to be applied depends upon the age & type of plants, climatic conditions, soil texture and the quality of sewage
KARNAL TECHNOLOGY(Sewage fed Agro-forestry)
KARNAL TECHNOLOGYKARNAL TECHNOLOGY(Sewage fed Agro(Sewage fed Agro--forestry)forestry)
Application of sewage should be controlled in order to ensure that water is either evaporated or consumed within 12 – 18 hours and there is no water stagnation. This will lower production of foul smell, eliminate mosquito breeding and ensure that wastewater does not percolate down to contaminate groundwater
Species of trees used are Eaucalyptus, Poplar and Leucaena
Trees are fully grown within 7-8 yrs and are used as fuel-wood, timber or pulp, leading to revenue generation
Land requirement is very high (1.5 – 2.0 ha./mld)
TECHNOLOGY OPTIONS FOR DISINFECTION OF TREATED SEWAGE
TECHNOLOGY OPTIONS FOR TECHNOLOGY OPTIONS FOR DISINFECTION OF TREATED SEWAGE DISINFECTION OF TREATED SEWAGE
Fecal coliform standards for treated effluent of STPs being constructed under NRCP introduced in the year 2000
Except for waste stabilization ponds and Karnal technology, other treatment processes require disinfection of treated sewage in order to meet these standards
Various technology options for disinfection tried out on pilot scale under NRCP are
Chlorination - most commonly used, cheap, but likely to lead to formulation of trihalo- methanes if the dosage is high
UV radiation - both capital and O&M costs are very expensive, treated effluentquality needs to be further improved for lowering the SS and BOD levels
DHS (down hanging sponge) system – technology tried out for first time in Karnal UASB STP and appears very promising
Fecal Fecal coliformcoliform standards for treated effluent of standards for treated effluent of STPsSTPs being constructed under NRCP being constructed under NRCP introduced in the year 2000introduced in the year 2000
Except for waste stabilization ponds and Except for waste stabilization ponds and KarnalKarnal technology, other treatment technology, other treatment processes require disinfection of treated sewage in order to meeprocesses require disinfection of treated sewage in order to meet these standardst these standards
Various technology options for disinfection tried out on pilot sVarious technology options for disinfection tried out on pilot scale under NRCP are cale under NRCP are
Chlorination Chlorination -- most commonly used, cheap, but likely to lead to formulation omost commonly used, cheap, but likely to lead to formulation of f trihalotrihalo-- methanesmethanes if the dosage is highif the dosage is high
UV radiationUV radiation -- both capital and O&M costs are very expensive, treated effluentboth capital and O&M costs are very expensive, treated effluentquality needs to be further improved for lowering the SS and BODquality needs to be further improved for lowering the SS and BOD levelslevels
DHS (down hanging sponge) systemDHS (down hanging sponge) system –– technology tried out for first time in technology tried out for first time in KarnalKarnal UASB STP and appears very promisingUASB STP and appears very promising
Technology Land required(Ha./mld)
Capital costs(Rs. lakhs/mld)
O&M costs(Rs. lakhs/mld/year)
Activated Sludge Process 0.2 - 0.25 40 - 45 3.5
Trickling Filter 0.2 - 0.25 35 - 40 3.0 - 3.5
Aerated Lagoons 0.6 20 - 25 2.25 - 2.75
UASB + Polishing Unit 0.2 30 - 35 1.5 - 2.0
Waste Stabilization Ponds 1.0 - 2.0 10 - 15 0.5
Karnal Technology 1.5 - 2.0 2 - 5 0.25 - 0.30
FAB 0.03 35 - 40 2.5 - 3.0
COMPARISON OF VARIOUS TECHNOLOGIES
COMPARISON OF VARIOUS COMPARISON OF VARIOUS TECHNOLOGIESTECHNOLOGIES
Selection of treatment technology for a particular location should be based on life cycle cost comparison of various feasible options
C-TECH (CYCLIC ACTIVATED SLUDGE PROCESS)CC--TECH (CTECH (CYCLICYCLIC AACTIVATEDCTIVATED SSLUDGELUDGE PPROCESS)ROCESS)
Fully aerobic process based on Activated Sludge Fully aerobic process based on Activated Sludge principles where organic matter is digested by microprinciples where organic matter is digested by micro--organisms developed and maintained in the reactor in organisms developed and maintained in the reactor in presence of oxygenpresence of oxygen
Operates in a cyclic mode of Fill, Aeration, Settle and Operates in a cyclic mode of Fill, Aeration, Settle and Decant cycle. The reactor is first filled and aerated. After Decant cycle. The reactor is first filled and aerated. After completion of aeration process, contents are allowed to completion of aeration process, contents are allowed to settle in the same basin which is followed by decanting settle in the same basin which is followed by decanting of clear water from the top using moving weir decanters.of clear water from the top using moving weir decanters.
Unique system design incorporating Oxygen Uptake Unique system design incorporating Oxygen Uptake Rate (OUR) determination and precise treatment for each Rate (OUR) determination and precise treatment for each batch under treatment , achieves optimum efficiency with batch under treatment , achieves optimum efficiency with minimal power consumption. minimal power consumption.
PLC and computer based fully automatic process. Plant PLC and computer based fully automatic process. Plant performance is independent of operator’s attention and performance is independent of operator’s attention and skills.skills.
Gives very good effluent quality – BOD < 5 mg/l, SS < 10 mg/l, NH4-N < 2 mg/l, TP < 1 mg/l. Treated water can be reused for industrial/agricultural purposes
Very compact process. Offers 50% area savings as compared to conventional schemes
Capable of handling wide variation of incoming loads
Power consumption directly proportional to incoming load. Offers 50% power savings against conventional schemes
When offered with gas recovery and power generation features , no external power is required for the plant and the plant generates surplus power which can be sold
Fully Automatic – negligible manpower is required for plant operation
All submerged metal parts in Stainless Steel
Lower maintenance costs as compared to ASP. No chemicals required.
No sludge bulking, pin flocs and rising sludge problems
C-TECH AdvantagesCC--TECH AdvantagesTECH Advantages
12.5 mld STP at Panaji, Goa
SELECTION OF APPROPRIATE SEWAGE TREATMENT TECHNOLOGY
SELECTION OF APPROPRIATE SEWAGE SELECTION OF APPROPRIATE SEWAGE TREATMENT TECHNOLOGYTREATMENT TECHNOLOGY
Try to use use as little mechanization and electric power as possible
Adopt waste stabilization pond and Karnal technology wherever adequate & cheap land is available
Decentralize, wherever feasible (save on transportation costs)
Carry out life cycle cost comparison of various feasible options
Benefit from warmer temperatures in India
Re-use treated effluent for irrigation to the extent possible
Practice resource recovery and try to generate some income to offset part of the O&M cost (pisci-culture, sale of sludge & treated effluent, bio-gas reuse)
Try to use Try to use useuse as little mechanization and electric power as possible as little mechanization and electric power as possible
Adopt waste stabilization pond and Adopt waste stabilization pond and KarnalKarnal technology wherever adequate & technology wherever adequate & cheap land is availablecheap land is available
Decentralize, wherever feasible (save on transportation costs)Decentralize, wherever feasible (save on transportation costs)
Carry out life cycle cost comparison of various feasible optionsCarry out life cycle cost comparison of various feasible options
Benefit from warmer temperatures in India Benefit from warmer temperatures in India
ReRe--use treated effluent for irrigation to the extent possibleuse treated effluent for irrigation to the extent possible
Practice resource recovery and try to generate some income to ofPractice resource recovery and try to generate some income to offset part of fset part of the O&M cost (the O&M cost (piscipisci--culture, sale of sludge & treated effluent, bioculture, sale of sludge & treated effluent, bio--gas reuse)gas reuse)
FOR SUSTAINABLE SEWAGE TREATMENT, NEED TO KEEP IN MIND THE FOLLOWINGFOR SUSTAINABLE SEWAGE TREATMENT, NEED TO KEEP IN MIND FOR SUSTAINABLE SEWAGE TREATMENT, NEED TO KEEP IN MIND THE FOLLOWINGTHE FOLLOWING
Bottlenecks in Project Implementation & MaintenanceBottlenecks in Project Implementation & MaintenanceBottlenecks in Project Implementation & MaintenanceDelays in land acquisition/encroachments Delays in land acquisition/encroachments Inadequate capacity of local bodies/agencies Inadequate capacity of local bodies/agencies Contractual problemsContractual problemsCourt casesCourt casesFinancial constraints of the local bodies, leading Financial constraints of the local bodies, leading to improper O&M of assets createdto improper O&M of assets createdLow level of public awareness & participationLow level of public awareness & participationErratic Power supplyErratic Power supply
LESSONS LEARNT AND STRATEGIES/ LESSONS LEARNT AND STRATEGIES/ INITIATIVES ADOPTEDINITIATIVES ADOPTED
LESSONS LEARNT AND STRATEGIES/ INITIATIVES ADOPTED
LESSONS LEARNT AND STRATEGIES/ LESSONS LEARNT AND STRATEGIES/ INITIATIVES ADOPTEDINITIATIVES ADOPTED
Due to fund constraints, treatment of full pollution load of even major rivers like Ganga has not yet been addressed.
Focus under NRCP to be on large towns, which are gross polluters, so that resources are not spread thinly
Creation of sewerage infrastructure is the primary responsibility of the State Government & the concerned local bodies. Centre can at best supplement the State’s efforts.
Government of India will continue to fund only the down-steam component of the sewerage system ( trunk/intercepting sewers, sewage treatment plants, effluent disposal system) under NRCP
Due to fund constraints, treatment of full pollution load of eveDue to fund constraints, treatment of full pollution load of even major n major rivers like rivers like GangaGanga has not yet been addressed. has not yet been addressed.
Focus under NRCP to be on large towns, which are gross polluters, so that resources are not spread thinly
Creation of sewerage infrastructure is the primary responsibilitCreation of sewerage infrastructure is the primary responsibility of the y of the State Government & the concerned local bodies. Centre can at besState Government & the concerned local bodies. Centre can at best t supplement the State’s efforts.supplement the State’s efforts.
Government of India will continue to fund only the downGovernment of India will continue to fund only the down--steam steam component of the sewerage system ( trunk/intercepting sewers, component of the sewerage system ( trunk/intercepting sewers, sewage treatment plants, effluent disposal system) under NRCPsewage treatment plants, effluent disposal system) under NRCP
Strategies/Initiatives AdoptedStrategies/Initiatives Adopted
LESSONS LEARNT AND STRATEGIES/ INITIATIVES ADOPTED
LESSONS LEARNT AND STRATEGIES/ LESSONS LEARNT AND STRATEGIES/ INITIATIVES ADOPTEDINITIATIVES ADOPTED
All the other upsteam components of sewerage infrastructure in the city (house connections, branch & lateral sewers, etc.) to be funded by State Governments/local bodies from their own resources on priority
State Governments to delegate necessary powers to local bodies under 74th Constitutional Amendment for generation of revenue through levy of user charges, property tax, etc.
Institutional capacities of the local bodies to be strengthened to ensure greater sustainability of the programme
A detailed plan for recovering operation & maintenance costs to become an integral part of the project proposal
All the other All the other upsteamupsteam components of sewerage infrastructure in the components of sewerage infrastructure in the city (house connections, branch & lateral sewers, etc.) to be fucity (house connections, branch & lateral sewers, etc.) to be funded by nded by State Governments/local bodies from their own resources on priorState Governments/local bodies from their own resources on priorityity
State Governments to delegate necessary powers to local bodies under 74th Constitutional Amendment for generation of revenue through levy of user charges, property tax, etc.
Institutional capacities of the local bodies to be strengthened to ensure greater sustainability of the programme
A detailed plan for recovering operation & maintenance costs to become an integral part of the project proposal
Strategies/Initiatives AdoptedStrategies/Initiatives Adopted
LESSONS LEARNT AND STRATEGIES/ INITIATIVES ADOPTED
LESSONS LEARNT AND STRATEGIES/ LESSONS LEARNT AND STRATEGIES/ INITIATIVES ADOPTEDINITIATIVES ADOPTED
Strategies/Initiatives AdoptedStrategies/Initiatives AdoptedCitizens Monitoring Committees to be created and activated for public awareness and education in each town
Greater initiatives to be taken at State/local body level for more involvement & participation of the public in the programme
Uninterrupted power supply through dedicated feeder lines to be provided to the assets created under the programme
Citizens Monitoring Committees to be created and activated for public awareness and education in each town
Greater initiatives to be taken at State/local body level for more involvement & participation of the public in the programme
Uninterrupted power supply through dedicated feeder lines to be provided to the assets created under the programme
LESSONS LEARNT AND STRATEGIES/ INITIATIVES ADOPTED
LESSONS LEARNT AND STRATEGIES/ LESSONS LEARNT AND STRATEGIES/ INITIATIVES ADOPTEDINITIATIVES ADOPTED
Strategies/Initiatives AdoptedStrategies/Initiatives Adopted
State Government/local body to concurrently undertake programmes from their own resources to tackle the other non-point pollution sources
Release of funds to state implementing agencies to be linked with performance
A Tripartite MoU between the Central Government, State Government & local body to be entered into outlining the roles and responsibilities of each party before sanction of the project(under consideration)
State Government/local body to concurrently undertake programmes from their own resources to tackle the other non-point pollution sources
Release of funds to state implementing agencies to be linked witRelease of funds to state implementing agencies to be linked with h performanceperformance
A Tripartite MoU between the Central Government, State Government & local body to be entered into outlining the roles and responsibilities of each party before sanction of the project(under consideration)