Heavy Metal Contamination of Ganga River at Varanasi in Relation to Atmospheric Deposition

Total Page:16

File Type:pdf, Size:1020Kb

Heavy Metal Contamination of Ganga River at Varanasi in Relation to Atmospheric Deposition Tropical Ecology 51(2S): 365-373, 2010 ISSN 0564-3295 © International Society for Tropical Ecology www.tropecol.com Heavy metal contamination of Ganga river at Varanasi in relation to atmospheric deposition J. PANDEY*, K. SHUBHASHISH & RICHA PANDEY Centre of Advanced Study in Botany, Banaras Hindu University, Varanasi 221 005, India Abstract: We investigated the mid stream water quality of Ganga river as influenced by aerially - driven heavy metals at Varanasi, India. Twelve sampling stations were selected along a 20 km long stretch of the river. Mid stream sub-surface water samples collected at fortnightly intervals from all the sites were acid digested and analyzed for Cd, Cr, Cu, Ni, Pb and Zn. The data revealed that the mid-stream water of river Ganga at Varanasi is invariably contaminated by heavy metals. Highest concentrations of Cd, Cr, Cu, Ni and Pb were recorded during winter and that of Zn during summer season. The overall concentration of heavy metals in water showed the trend : Zn > Ni > Cr > Pb > Cu > Cd. Concentrations of all the heavy metals were high in down - stream sampling stations. Correlation analysis showed that heavy metal concentration in mid-stream water had significant positive relationship with rate of atmospheric deposition at respective sites. Although the concentrations of these metals in water remained below the permissible limits of Indian standards for drinking water, levels of Cd, Ni and Pb at three stations, were above the internationally recommended (WHO) maximum admissible concentrations (MAC). These observations suggest that use of such water for drinking may lead to potential health risk in long-run. The study has further relevance in understanding the atmosphere - water interaction in polluted environment and for management of water bodies even those situated away from direct anthropogenic discharge. Resumen: Investigamos la calidad del agua de la corriente media del río Ganges en relación con los metales pesados transportados por aire en Varanasi, India. Se seleccionaron doce estaciones de muestreo sobre una sección del río de 20 km de largo. Las muestras de agua sub-superficial del centro de la corriente recolectadas quincenalmente en todos los sitios fueron sometidas a digestión ácida para analizar su contenido de Cd, Cr, Cu, Ni, Pb y Zn. Los datos revelaron que el agua de la corriente media del río Ganges en Varanasi está invariablemente contaminada por metales pesados. Las concentraciones más altas de Cd, Cr, Cu, Ni y Pb fueron registradas durante el invierno y la de Zn durante el verano. Las concentraciones generales de metales pesados en el agua mostraron la tendencia Zn > Ni > Cr > Pb > Cu > Cd. Las concen- traciones de todos los metales pesados fueron altas en las estaciones de muestreo ubicadas corriente abajo. Un análisis de correlación mostró que la concentración de metales pesados en el agua de la corriente media tuvo una relación positiva significativa con la tasa de deposición atmosférica en los sitios respectivos. Si bien las concentraciones de estos metales en el agua permanecieron debajo de los límites permisibles de los estándares para el agua potable en la India, los niveles de Cd, Ni y Pb en tres estaciones superaron las concentraciones máximas admisibles (CMA) recomendadas internacionalmente (OMS). Estas observaciones sugieren que el uso de esta agua para consumo humano puede conducir a riesgos potenciales de salud a largo plazo. El estudio tiene además relevancia para el entendimiento de la interacción atmósfera - agua en un ambiente contaminado y para el manejo de cuerpos de agua, incluso de aquellos que se sitúan lejos de descargas antropogénicas directas. Resumo: Investigámos a influência dos metais pesados transportados pelo ar na qualidade do caudal da água do rio Ganga em Varanasi, Índia. Doze estações amostra foram seleccionadas N * Corresponding Author; e-mail: [email protected] 366 ATMOSPHERIC DEPOSITION AND WATER POLLUTION ao longo de 20 km do percurso do rio. As amostras de água da sub-superfície da corrente do rio foram colhidas quinzenalmente de todas as estações, foram digeridas em meio ácido e analisadas em relação ao Cd, Cr, Cu, Ni, Pb e Zn. Os dados revelaram que as águas da corrente do rio Ganga, em Varanasi, estavam invariavelmente contaminadas por metais pesados. As concentrações mais elevadas de Cd, Cr, Cu, Ni e Pb foram registadas durante o inverno enquanto no verão era o Zn. A concentração global em metais pesados na água mostrou a seguinte tendência: Zn > Ni > Cr > Pb > Cu > Cd. As concentrações de todos os metais pesados eram mais elevadas nas estações amostra mais a jusante. A análise de correlação mostrou que a concentração em metais pesados na corrente apresentava uma relação positiva com a taxa de deposição atmosférica nas respectivas estações. Embora as concentrações neste metais pesados na água se encontre abaixo dos limites permissíveis pelos standards indianos para a água de beber, os níveis de Cd, Ni e Pb em três estações, encontravam-se acima dos níveis internacion- almente recomendados (OMS) para as concentrações máximas admissíveis (CMA). Estas observações sugerem que o uso desta água para beber pode conduzir a longo prazo a potencias riscos para a saúde. O estudo tem, ainda, relevância para a compreensão da inter-acção atmosfera - água em ambientes poluídos e para a gestão das massas de água, mesmo daquelas distantes das descargas antropogénicas directas. Key words: Aerial catchment, atmospheric deposition, contamination, Ganga river, heavy metals, pollution. Introduction implications including carcinogenesis induced tumor promotion (Schwartz 1994). The growing cons- Atmospheric depositions of heavy metals have ciousness about the health risks associated with dramatically altered the biogeochemical cycles of environmental chemicals has brought a major shift these elements (Azimi et al. 2003; Friedland & in global concern towards prevention of heavy metal Miller 1999). The impact of long - distance atmos- accumulation in soil, water and vegetables. Atmos- pheric transport of pollutant aerosols on terrestrial pherically driven heavy metals have been shown to environment is well documented, but the impact of significantly contaminate soil and vegetables aerially driven pollutant aerosols on inland water causing a serious risk to human health when plant bodies has received attention only recently (Pan- based foodstuffs are consumed (Pandey & Pandey dey & Pandey 2009a; Thornton & Dise 1998). In 2009b, 2009c; Voutsa et al. 1996). Dietary intake of India, the data so far available on these lines have trace elements depends also on irrigational water been mainly confined to acidic depositions (Kumar use. There may not always be a strong relationship et al. 2001). Less attention has been paid towards between the concentrations of trace elements in atmospheric deposition - linked heavy metal conta- soil and plants (Siegel 2002), but there always mination of freshwater bodies, especially rivers. exists a strong relationship between their During recent years, anthropogenic activities have concentrations in irrigational water and plants dramatically increased the atmospheric deposition (Ahmad & Goni 2009; Sharma et al. 2006). Thus, of pollutant elements even in areas far away from the deposition of heavy metals in water bodies can direct human influence (Pandey & Pandey 2005, doubly increase the human intake through food 2009a). Although the atmospheric deposition of po- chain as well as through drinking water. Most of llutant aerosols is of global concern, this problem the surface discharge sources contaminate soil and is rapidly increasing in developing countries inc- water bodies under limited spatial range, aerial luding India due to continued population pressure emissions being prone to long range transport, coupled with accelerated urban - industrial growth contaminate wider range of ecosystems especially and lack of efficient control measures (Borbely - down wind to emission sources. Furthermore, unlike Kiss et al. 1999; Pandey & Pandey 2009b; Singh & surface discharge, where stream flow restricts mid Agrawal 2005). stream contamination, atmospheric deposition dir- Heavy metals are known to have serious health ectly adds contaminants on water surfaces. PANDEY, SHUBHASHISH & PANDEY 367 The present study was an attempt to investi- different sampling sites is presented in Table 1. gate the relationship between the concentrations The bulk atmospheric deposition was collected of heavy metals in mid stream Ganga water and using bulk samplers which combine the precipi- their input through atmospheric deposition at tation and dry fallout in the same container. These Varanasi. The River Ganga rises in the Gangotri collection systems were maintained at a height of 2 glacier in the Himalaya Mountains at an elevation m to avoid collection of re - suspended soil parti- of 7138 m above mean sea level. It enters the culates and were devised to avoid bird nesting as plains at Hardwar and meanders over a distance described in Pandey & Pandey (2009b). The bulk of above 2290 km across UP, Bihar and West collectors were replaced by clean ones at fort- Bengal, and receives a wide array of chemical nightly intervals. As soon as the samples were constituents including toxicants from a variety of brought to the laboratory, they were acidified with natural and anthropogenic sources (Kar et al. HNO3 (Merck), filtered and stored in dark at 2008). Earlier studies have indicated urban sewage ambient temperature before analysis. and industrial
Recommended publications
  • Foundation of Bridges on River Ganges in India
    Foundation of bridges on river Ganges in India Autor(en): Kumar, Vijay Objekttyp: Article Zeitschrift: IABSE reports = Rapports AIPC = IVBH Berichte Band (Jahr): 80 (1999) PDF erstellt am: 05.10.2021 Persistenter Link: http://doi.org/10.5169/seals-60780 Nutzungsbedingungen Die ETH-Bibliothek ist Anbieterin der digitalisierten Zeitschriften. Sie besitzt keine Urheberrechte an den Inhalten der Zeitschriften. Die Rechte liegen in der Regel bei den Herausgebern. Die auf der Plattform e-periodica veröffentlichten Dokumente stehen für nicht-kommerzielle Zwecke in Lehre und Forschung sowie für die private Nutzung frei zur Verfügung. Einzelne Dateien oder Ausdrucke aus diesem Angebot können zusammen mit diesen Nutzungsbedingungen und den korrekten Herkunftsbezeichnungen weitergegeben werden. Das Veröffentlichen von Bildern in Print- und Online-Publikationen ist nur mit vorheriger Genehmigung der Rechteinhaber erlaubt. Die systematische Speicherung von Teilen des elektronischen Angebots auf anderen Servern bedarf ebenfalls des schriftlichen Einverständnisses der Rechteinhaber. Haftungsausschluss Alle Angaben erfolgen ohne Gewähr für Vollständigkeit oder Richtigkeit. Es wird keine Haftung übernommen für Schäden durch die Verwendung von Informationen aus diesem Online-Angebot oder durch das Fehlen von Informationen. Dies gilt auch für Inhalte Dritter, die über dieses Angebot zugänglich sind. Ein Dienst der ETH-Bibliothek ETH Zürich, Rämistrasse 101, 8092 Zürich, Schweiz, www.library.ethz.ch http://www.e-periodica.ch 351 Foundation of Bridges on River Ganges in India Vijay Kumar Obtained his Science degree from University of General Manager Allahabad and Engineering degree from University U.P.State Bridge Corpn. ' of Roorkee. He has 34 years experience in design 486, Hawa Singh Block, and Construction of Bridges in India and abroad.
    [Show full text]
  • Trend of River Ganga in Uttar Pradesh
    Monitoring of Indian Aquatic Resources Series: MINARS/31/2009–2010 Central Pollution Control Board Ministry of Environment and Forests Website: www.cpcb.nic.in • e-mail: [email protected] DECEMBER 2009 USE BASED CLASSIFICATION OF SURFACE WATERS IN INDIA Designated-Best-Use Class of Criteria water Drinking water source A 1. Total Coliforms Organism MPN/100 ml shall without conventional be 50 or less treatment but after 2. pH between 6.5 and 8.5 disinfection 3. Dissolved Oxygen 6 mg/l or more 4. Biochemical Oxygen Demand 5 days 20 °C 2 mg/l or less Outdoor bathing B 1. Total Coliforms Organism MPN/100 ml shall (organised) be 500 or less 2. pH between 6.5 and 8.5 3. Dissolved Oxygen 5 mg/l or more 4. Biochemical Oxygen Demand 5 days 20 °C 3 mg/l or less Drinking water source C 1. Total Coliforms Organism MPN/100 ml shall after conventional be 5000 or less treatment and disinfection 2. pH between 6 and 9 3. Dissolved Oxygen 4 mg/l or more 4. Biochemical Oxygen Demand 5 days 20 °C 3 mg/l or less Propagation of wild life D 1. pH between 6.5 and 8.5 and fisheries 2. Dissolved Oxygen 4 mg/l or more 3. Free Ammonia (as N) 1.2 mg/l or less Irrigation, industrial E 1. pH between 6.0 and 8.5 cooling, controlled 2. Electrical Conductivity at 25 °C waste disposal micro mhos/cm maximum 2250 3. Sodium absorption ratio maximum 26 4. Boron maximum 2 mg/l Monitoring of Indian Aquatic Resources Series: MINARS/31/2009–2010 GANGA WATER QUALITY TREND Central Pollution Control Board Ministry of Environment and Forests Website: www.cpcb.nic.in • e-mail: [email protected] DECEMBER 2009 © Central Pollution Control Board, 2009 All rights reserved.
    [Show full text]
  • Modeling the Efficacy of the Ganga Action Plan's Restoration of The
    Modeling the Efficacy of the Ganga Action Plan’s Restoration of the Ganga River, India By Shaw Lacy A thesis submitted In partial fulfillment of the requirements For the degree of Master of Science Natural Resources and Environment at The University of Michigan August 2006 Thesis Committee: Professor Michael Wiley Professor Jonathan Bulkley Abstract. To combat rising levels of water pollution in the Ganges River, the Indian gov- ernment initiated the Ganga Action Plan (GAP) in 1984. After twenty years, it is a com- mon perception that the GAP has failed to achieve the goals of a cleaner river. Using available government data on pollution levels and hydrology, I undertook an of the GAP efficacy for fifteen pollution parameters across 52 water quality sampling points moni- tored by India’s Central Pollution Control Board (CPCB) within the Ganga Basin. Dis- solved oxygen, BOD, and COD showed a significant improvement of water quality after twenty years. In addition, fecal and total coliform levels, as well as concentrations of cal- cium, magnesium, and TDS all showed a significant decline. Building on this analysis, a GIS analysis was used to create a spatial model of the majority of the Ganga River net- work using a reach-based ecological classification approach. Using recent GAP monitor- ing data, a multiple linear regression model of expected pollutant loads within each reach (VSEC unit) was created. This model was then used to inventory water quality across the entire basin, based on CPCB criteria. My analysis showed 208 river km were class A, 1,142 river km were class B, 684 river km were class C, 1,614 river km were class D, and 10,403 river km were class E.
    [Show full text]
  • List of 85 Bridges in India
    List of 85 Bridges In India Connecting Name River Length Feet Opened Type cities Bhupen Hazarika Setu, Lohit Assam River 9,150 30,020 2017 Road Tinsukia Dibang River Bridge, Dibang Arunachal Pradesh River 6,200 20,300 2018 Road Bomjur-Meka Mahatma Gandhi Setu, Patna–Hajip Bihar Ganges 5,750 18,860 1982 Road ur Bandra-Worli Sea Link, Mahim Maharashtra bay 5,600 18,400 2009 Road Mumbai Brahmap Rail-cum-roa Bogibeel Bridge, Assam utra River 4,940 16,210 2018 d Dibrugarh Vikramshila Setu, Bihar Ganges 4,700 15,400 2001 Road Bhagalpur Vembanad Rail Bridge, Vembana Kerala d Lake 4,620 15,160 2011 Rail Kochi Digha–Sonpur Bridge, Rail-cum-roa Patna–Sonp Bihar Ganges 4,556 14,948 2016 d ur Arrah–Chhapra Bridge, Arrah–Chhap Bihar Ganges 4,350 14,270 2017 Road ra Godavari Fourth Bridge Kovvur–Rajahmundry Bypass Bridge, Andhra Godavari Pradesh River 4,135 13,566 2015 Road Rajahmundry Munger Ganga Bridge, Rail-cum-Ro Bihar Ganges 3,750 12,300 2020 ad Munger Chahlari Ghat Bridge, Ghaghra Bahraich–Sit Uttar Pradesh River 3,249 10,659 2017 Road apur Jawahar Setu, Bihar Son River 3,061 10,043 1965 Road Dehri Nehru Setu, Bihar Son River 3,059 10,036 1900 Rail Dehri Kolia Bhomora Setu, Brahmap Tezpur–Kalia Assam utra River 3,015 9,892 1987 Road bor Korthi-Kolhar Bridge, Krishna Karnataka River 3,000 9,800 2006 Road Bijapur Netaji Subhas Chandra Kathajodi Bose Setu, Odisha River 2,880 9,450 2017 Road Cuttack Godavari Bridge, Andhra Godavari Rail-cum-roa Pradesh River 2,790 1974 d Rajahmundry Old Godavari Bridge Now decommissioned, Godavari Andhra Pradesh
    [Show full text]
  • Water Resources on Environment: Lok Sabha (Monsoon Session) 2013-14 – Part-II
    Water Resources on Environment: Lok Sabha (Monsoon Session) 2013-14 – Part-II Q. No. Q. Type Date Ans by Members Title of the Questions Subject Specific Political State Ministry Party Representative 08.08.2013 Water Shri Narahari Mahato Conservation of Water Environmental Education, AIFB West Bengal *67 Starred Resources NGOs and Media Shri Manohar Tirkey Freshwater and Marine RSP West Bengal Conservation 08.08.2013 Water Km. Saroj Pandey Water Resource Projects Water Management BJP Chhattisgarh *70 Starred Resources 08.08.2013 Water Smt. Putul Kumari Flood Prone States Disaster Management Ind. Bihar *74 Starred Resources Shri Gorakh Nath Water Management BSP Uttar Pradesh Pandey 08.08.2013 Water Shri Vikrambhai Repairing of Bunds Disaster Management INC Gujarat 708 Unstarred Resources Arjanbhai Maadam 08.08.2013 Water Smt. Jayshreeben Patel Modified AIBP Scheme Agriculture BJP Gujarat 711 Unstarred Resources Dr. Mahendrasinh Water Management BJP Gujarat Pruthvisinh Chauhan 08.08.2013 Water Dr. Sanjay Sinh Sharda Sahayak Yojana Agriculture INC Uttar Pradesh 717 Unstarred Resources 08.08.2013 Water Shri Ramsinh Committee on Floods Disaster Management BJP Uttar Pradesh 721 Unstarred Resources Patalyabhai Rathwa 08.08.2013 Water Shri A.K.S. Vijayan Fast Tracking Dam Water Management DMK Tamil Nadu 722 Unstarred Resources Projects 08.08.2013 Water Shri Prataprao Social Commitment SS 752 Unstarred Resources Ganpatrao Jadhav Alternative Technologies Maharashtra Shri Chandrakant Water Management SS Bhaurao Khaire Maharashtra 08.08.2013 Water
    [Show full text]
  • Lucknow on Singh’S Condition from the Doc- RK Giri and AP Dimri, Heat- Sunday
    7 " (8 8 8 4567'&+- -+-+. 1-/2,)3 -/()0 "( 4"O!!)>6 "4+3+""+!+3+)>A9B/"3! ?)""!2+! 34+351!=2 *4="3*45*!2) )!4+)+"5) 4!+%)4 4=2O4)=4@ )4 B9 $/)5 5)+!%" 4)5! 4>)*?+#>2 3 129$:3 9;/ < ( # 8 %.$.'9! '-" !" ! !234+ $)* n the run-up to the drone ( ++, Iattack on the Indian Air Force (IAF) Station in Jammu on June 27, the Pakistani covert "#$%#&'#%(& agency Inter-Services )*"+#&'(, Intelligence (ISI) had stepped up espionage bids by making -#$.#($&)*+(%, fake calls to gather “sensitive” information about deploy- !234+ .#/+#&(#--+ ments of the Central Reserve )*"+#(&., Police Force (CRPF) at various #5 lated areas, it is imperative to eutralising antibodies locations/establishments in discontinue the use of drones Nagainst the Delta variant -#(/#"'+ Jammu and Kashmir (J&K). n order to ward off any in all social and cultural gath- (B1.617.2) of Covid-19 were not response? They need to be Some voice calls were Idrone strikes on vital securi- erings to eliminate any risk of found in at least 16.1 per cent identified and revaccinated 6+$#/&#'(()*/#""+, made from mobile numbers ty installations in Srinagar, the injury to life and damage to samples from those who had with an alternative vaccine.” 9412**8321 and 9675**0429 district authorities have banned property.” been administered both doses This also suggests that there ./#("#+&%)*'.#'$$, to CRPF officers/personnel the use, possession, sale, stor- Meanwhile, people who of the Covishield vaccine, as per is a need for a second booster with the callers introducing age and transportation of already have drone cameras or a study conducted by to enhance antibodies, he P.&#%"#+-")*'#%+-, themselves as Deputy Director drones with immediate effect.
    [Show full text]
  • STATUS of GROUNDWATER QUALITY in INDIA -Part-II
    GROUNDWATER QUALITY SERIES: GWQS/ 10/2007-2008 STATUS OF GROUNDWATER QUALITY IN INDIA -Part-II CENTRAL POLLUTION CONTROL BOARD (MINISTRY OF ENVIRONMENT AND FORESTS) Website: www.cpcb.nic.in e-mail: [email protected] April, 2008 GROUNDWATER QUALITY SERIES: GWQS/ 10/2007-2008 STATUS OF GROUNDWATER QUALITY IN INDIA Part - II CPCB CENTRAL POLLUTION CONTROL BOARD (Ministry of Environment & Forests, Govt. of India) Parivesh Bhawan, East Arjun Nagar Delhi – 110 032 Website: www.cpcb.nic.in e-mail: [email protected] ii iii CONTRIBUTIONS Guidance, Planning, and Dr. B. Sengupta, Member Secretary Principal Coordinators Dr. R. C. Trivedi, Additional Director Project Coordination, Dr. Sanjeev Agrawal, Scientist `C’ Report Compilation & Ms. Pramila Gupta; JRF Preparation PAMS Division, CPCB, Delhi. Monitoring & Analysis of I) National Institute of Hydrology, Groundwater Samples in Roorkee Metropolitan Cities II) Pollution Control Research Institute (PCRI, BHEL), Haridwar, Uttarakhand. III) Pollution Control Cell, Thane Munucipal Corporation (TMC), Thane. iv CONTENTS LIST OF FIGURES LIST OF TABLES EXECUTIVE SUMMARY 1.0 INTRODUCTION 2.0 METROPOLITAN CITIES 2.1 Faridabad 2.2 Delhi 2.3 Jaipur 2.4 Bhopal 2.5 Indore 2.6 Jabalpur 2.7 Nagpur 2.8 Nasik 2.9 Pune 2.10 Bangalore 2.11 Hyderabad 2.12 Vishakhapatnam 2.13 Patna 2.14 Kochi 2.15 Ahmedabad 2.16 Rajkot 2.17 Surat 2.18 Vadodara 2.19 Asansol 2.20 Dhanbad 2.21 Jamshedpur 2.22 Kolkata 2.23 Amritsar 2.24 Kanpur 2.25 Allahabad 2.26 Varanasi 2.27 Mumbai 3.0 EXPERIMENTAL METHODOLOGY 3.1 Sampling and Preservation 3.2 Chemicals and Reagents 3.3 Physico-chemical and Bacteriological Analysis 3.4 Metal Ion Analysis 3.5 Pesticide and PAH Analysis 4.0 GROUND WATER QUALITY v 4.1 Drinking Water Specifications 4.2 Irrigation Water Quality Criteria 4.3 Classification of Ground Water 4.3.1 Piper Trilinear Classification 4.3.2 Chadha’s Diagram 4.3.3 Durov’s Diagram 4.3.4 U.S.
    [Show full text]
  • Wastewater Treatment for Water Security in India
    Occasional Paper For Restricted Circulation No.13-0418 WASTEWATER TREATMENT FOR WATER SECURITY IN INDIA Meera Sahasranaman & Arijit Ganguly April-2018 INSTITUTE FOR RESOURCE ANALYSIS AND POLICY 202, Riviera, Dwarkapuri Colony, Punjagutta, Hyderabad-500082 Tel: 91-40-42617392 E-Mail:[email protected] www.irapindia.org Wastewater Treatment for Water Security in India Meera Sahasranaman and Arijit Ganguly Abstract With rapid and unplanned urbanisation and economic growth, the demand for fresh water for various purposes is on the rise in India. However, spatio-temporal variations in fresh water availability, vagaries of the monsoon and variability in climate, as well as human, development and management challenges pose great threats to water supplies in the country. While excessive withdrawal from surface and underground sources and inefficient use of water were recognised as reasons for reduced availability of fresh water with respect to space and time, the role of pollution of water sources, both surface and ground water, in reducing the quantum of available fresh water for various uses, has not received due importance. It is estimated that 75-80 per cent of water pollution in terms of volume of water polluted is from domestic sewage. This paper analyses the quality of water in surface water bodies across India. The data on water quality in rivers upstream and downstream of selected cities over a period of time was analyzed to understand the changes in crucial water quality parameters over time. The status of sewage treatment across Indian states was also studied, to understand the gaps in waste water treatment. The existing institutional and legal measures available for the control of water pollution were also analysed.
    [Show full text]
  • Environmental and Social Management Framework (ESMF)
    National Mission for Clean Ganga Ministry of Jal Shakti Department of Water Resources, River Development & Ganga Rejuvenation, Government of India Environmental and Social Management Framework (ESMF) Annex-I - Environmental and Social Baseline Prepared by The Energy and Resources Institute (January 2011) Updated by Lea Associates South Asia Pvt. Ltd (16 March 2020) CONTENTS 1. NATIONAL GANGA RIVER BASIN PROJECT ..................................................................... 1 1.1. INTRODUCTION ................................................................................................................................... 1 1.2. Ganga River Basin Management: Initiatives ....................................................................................... 1 1.3. NMCG: An Evolutionary Journey ......................................................................................................... 2 1.3.1. National Ganga River Basin Authority (NGRBA) ................................................................... 2 1.3.2. National Mission for Clean Ganga (NMCG) .......................................................................... 2 1.4. NMCG Projects .................................................................................................................................... 3 1.4.1. Short-term Action Plan ......................................................................................................... 3 1.4.2. Medium-term Action Plan ....................................................................................................
    [Show full text]
  • Ganga R Environment Manag GRB
    Report Code: 023_GBP_IIT_EQP_ANL_01_ Ver 1_June 2012 Water Quality in the Ganga River and Efficacy of Sewage Treatment Processes in Coliform Removal: A Case for Adopting Tertiary Treatment GRB EMP : Ganga River Basin Environment Management Plan by Indian Institutes of Technology IIT IIT IIT IIT IIT IIT IIT Bombay Delhi Guwahati Kanpur Kharagpur Madras Roorkee 1 | P a g e Report Code: 023_GBP_IIT_EQP_ANL_01_Ver 1_June 2012 2 | P a g e Report Code: 023_GBP_IIT_EQP_ANL_01_Ver 1_June 2012 Preface In exercise of the powers conferred by sub-sections (1) and (3) of Section 3 of the Environment (Protection) Act, 1986 (29 of 1986), the Central Government has constituted National Ganga River Basin Authority (NGRBA) as a planning, financing, monitoring and coordinating authority for strengthening the collective efforts of the Central and State Government for effective abatement of pollution and conservation of the river Ganga. One of the important functions of the NGRBA is to prepare and implement a Ganga River Basin: Environment Management Plan (GRB EMP). A Consortium of 7 Indian Institute of Technology (IIT) has been given the responsibility of preparing Ganga River Basin: Environment Management Plan (GRB EMP) by the Ministry of Environment and Forests (MoEF), GOI, New Delhi. Memorandum of Agreement (MoA) has been signed between 7 IITs (Bombay, Delhi, Guwahati, Kanpur, Kharagpur, Madras and Roorkee) and MoEF for this purpose on July 6, 2010. This report is one of the many reports prepared by IITs to describe the strategy, information, methodology, analysis and suggestions and recommendations in developing Ganga River Basin: Environment Management Plan (GRB EMP). The overall Frame Work for documentation of GRBMP and Indexing of Reports is presented on the inside cover page.
    [Show full text]
  • Current Affairs Compilation 2018
    TLP Phase II – Current Affairs Compilation 2018 www.IASbaba.com Page 1 TLP Phase II – Current Affairs Compilation 2018 Join the most trusted and efficient platform, ILP-2019 for UPSC Prelims and Mains: Especially if you are preparing from Home and Working Professionals’. Know how Topper’s like Rank 4, 6, 9, 14, 23, 31, 39 etc. have achieved it preparing from home. www.IASbaba.com Page 2 TLP Phase II – Current Affairs Compilation 2018 1. The government has recently decided to operationalise the National Financial Regulatory Authority (NFRA). What would be the functions of this organisation and why is it needed? Discuss. Approach: The main body will have two parts- functions of NFRA and its need. Introduction and conclusion is any answer is must. Relating the answer with recent turn of events (especially PNB scam) is must- to explain why the government has decided to operationalise the NFRA after the delay. Answer: Introduction: The Companies Act, 2013 proposed setting up of an independent audit regulator. However, the Union Cabinet has only recently approved the proposal for establishment of the National Financial Regulatory Authority (NFRA). Main Body: Functions of the organisation: Powers includes its ability to investigate, impose penalty and banning operations of auditors and audit firms. Setting the rules and regulations governing the audit sector. The NFRA will have the power to debar erring auditors or audit firm for up to 10 years and impose significant fines on them. The jurisdiction of NFRA for investigation of Chartered Accountants and their firms would extend to listed companies and large unlisted public companies.
    [Show full text]
  • The Study on Water Quality Management Plan for Ganga River in the Republic of India
    No. JAPAN INTERNATIONAL COOPERATION AGENCY (JICA) NATIONAL RIVER CONSERVATION DIRECTORATE (NRCD) MINISTRY OF ENVIRONMENT AND FORESTS THE STUDY ON WATER QUALITY MANAGEMENT PLAN FOR GANGA RIVER IN THE REPUBLIC OF INDIA FINAL REPORT VOLUME II RIVER POLLUTION MANAGEMENT PLAN JULY 2005 TOKYO ENGINEERING CONSULTANTS CO., LTD. CTI ENGINEERING INTERNATIONAL CO., LTD. GE JR 05-038 JAPAN INTERNATIONAL COOPERATION AGENCY (JICA) NATIONAL RIVER CONSERVATION DIRECTORATE (NRCD) MINISTRY OF ENVIRONMENT AND FORESTS THE STUDY ON WATER QUALITY MANAGEMENT PLAN FOR GANGA RIVER IN THE REPUBLIC OF INDIA FINAL REPORT VOLUME II RIVER POLLUTION MANAGEMENT PLAN JULY 2005 TOKYO ENGINEERING CONSULTANTS CO., LTD. CTI ENGINEERING INTERNATIONAL CO., LTD. Foreign Exchange Rate: Master Plan US$ 1 = JPY 109.09 US$ 1 = Rs 45.33 (As of March 2004) Feasibility Study US$ 1 = JPY 103.66 US$ 1 = Rs 43.70 (As of February 2005) FINAL REPORT ON WATER QUALITY MANAGEMENT PLAN FOR GANGA RIVER JULY 2005 GENERAL TABLE OF CONTENTS VOLUME I SUMMARY VOLUME II RIVER POLLUTION MANAGEMENT PLAN VOLUME III MASTER PLAN FOR PROJECT CITIES VOLUME III-1 SEWERAGE MASTER PLAN FOR LUCKNOW CITY VOLUME III-2 SEWERAGE MASTER PLAN FOR KANPUR CITY VOLUME III-3 SEWERAGE MASTER PLAN FOR ALLAHABAD CITY VOLUME III-4 SEWERAGE MASTER PLAN FOR VARANASI CITY VOLUME III-5 NON-SEWERAGE SCHEME VOLUME III-6 SOCIAL CONSIDERATION AND HYGIENE EDUCATION PLAN VOLUME III-7 RECOMMENDATIONS ON SOLID WASTE MANAGEMENT VOLUME III-8 GIS DATA MANAGEMENT VOLUME III-9 INSTITUTIONAL DEVELOPMENT PROGRAMME VOLUME III-10 FINANCIAL AND
    [Show full text]