![]() |
CHAPTER VII
ENVIRONMENTAL RESEARCH
Research and development activities play an important role in assessment and control of pollution. The important research activities carried out during the year 2001-2002 in various fields like air and water, pollution related research studies, municipal solid waste related research studies, standardization of analytical techniques, analytical quality control (AQC), laboratory development, industries specific research studies are summarized below.
7.1 RESEARCH RELATED TO AIR POLLUTION
7.1.1 Performance Evaluation of Air Quality Models
A study has been initiated to provide scientific means for validation and adoption of air quality models suitable for Indian conditions and for formulating appropriate guidelines. An exhaustive data set including emissions, plume characteristics, measured concentrations of pollutants and meteorological parameters have been generated for the chosen site and software based on Gaussian Plume Model has been developed. The software is being refined and further evaluation work of model parameters has been undertaken.
7.1.2 Development of Certified Reference Material for Air Mixtures
Certified reference materials are a pre-requisite for calibration of air monitoring instruments and also to check the accuracy of analytical methods. The accuracy of analytical data depends on the quality of reference standards, used for calibration. In India, availability of indigenously manufactured reference material is scanty and much work needs to be done in this direction. In order to overcome this problem, the project was taken up with the sponsorship of the Department of Science & Technology. Few standard reference materials for air mixtures have already been prepared on trial basis.
7.1.3 Inter-laboratory Comparison of Ambient Air Quality Monitoring Methods
Inter-laboratory comparison is an effective tool for quality assurance in ambient air quality monitoring. Central Pollution Control Board has been conducting inter-laboratory comparison workshops since 1999. So far, five rounds of inter-laboratory comparisons have been carried out for measurement of sulphur dioxide and nitrogen dioxide. Measurements were mainly done by manual monitoring techniques except on one occasion when continuous monitoring techniques were also employed for measurement of sulphur dioxide and nitrogen dioxide. In the inter-laboratory comparison conducted during December 2001, 15 teams including officials from State Pollution Control Boards, non-governmental organizations, public sector undertakings and industries have participated. The results of the measurements are depicted in Table 7.1. The performance of the participating laboratories for measurement of nitrogen dioxide was poor as the number of outliers for different reference concentrations ranged between 27 to 40%. On the other hand, the performance of the participants for measurement of sulphur dioxide was satisfactory. There was only one outlier out of 15 participants in the reference concentration of 100 µg/m3. It is proposed to carry more of inter-laboratory comparisons workshops for parameters such as carbon monoxide and ozone.
| Participant Code |
Method |
Reference Concentration Nitrogen dioxide (µg/m3) |
Reference Concentration Sulphur dioxide (µg/m3) | ||||
|
28 |
79 |
115 |
16 |
39 |
100 | ||
| 1 |
Chemical |
33* |
73 |
176* |
14 |
40 |
98 |
|
2 |
Chemical |
32 |
94* |
134* |
17 |
41 |
100 |
|
3 |
Chemical |
30 |
108* |
114 |
15 |
33* |
96 |
|
4 |
Chemical |
30 |
85 |
88* |
17 |
12* |
41* |
|
5 |
Chemical |
34* |
107* |
128 |
13* |
44 |
104 |
|
6 |
Chemical |
31 |
90 |
125 |
17 |
42 |
101 |
|
7 |
Chemical |
30 |
93* |
111 |
16 |
46* |
100 |
|
8 |
Chemical |
41* |
87 |
124 |
14 |
45 |
105 |
|
9 |
Chemical |
33* |
105* |
112 |
14 |
44 |
101 |
|
10 |
Chemical |
34* |
94* |
156* |
15 |
90 | |
|
11 |
Chemical |
31 |
72 |
112 |
16 |
37 |
90 |
|
12 |
Chemical |
32 |
79 |
119 |
17 |
43 |
107 |
|
13 |
Analyser |
29 |
75 |
112 |
17 |
39 |
96 |
|
14 |
Analyser |
- |
- |
- |
16 |
43 |
94 |
|
15 |
Analyser |
30 |
77 |
114 |
13* |
40 |
103 |
|
Average Concentration |
32 |
88 |
123 |
15 |
39 |
95 | |
|
No. of Labs exceeding ±(15%) SRT |
5 |
6 |
4 |
2 |
3 |
1 | |
|
Percentage (%) of Labs exceeding ±15%) SRT | 33 |
40 |
27 |
13 |
21 |
7 | |
Values marked with asterisk (*) denote that the values are exceeding the ±(15%) Set Range of Tolerance (SRT)
7.1.4 Correlation of wind speed with ambient levels of pollutants
The wind speed and direction play a major role in dispersion of air pollutants. The stronger the wind, the greater will be dissipation and dilution of pollutants emitted. The wind speed less than 0.28 m/s is classified as calm wind. An attempt has been made to derive correlation of monthly calm condition of wind with monthly ambient CO & NO2 levels at traffic intersection in Delhi during 1997- 2000. It was observed that CO & NO2 concentration is directly proportional to calm condition, i.e more the condition of calm wind, the more is the pollutant concentrations (Fig 7.1 & 7.2).


7.2 RESEARCH RELATED TO WATER POLLUTION
7.2.1 Assessment of Water Pollution from Non-Point Sources
Over the years, reasonable baseline information on water pollution from point sources has been collected, but similar information on non-point sources is not available. During the year, an attempt was made to assess non-point sources of pollution in collaboration with the Punjab State Pollution Control Board. Main findings of the study are as follow:
Experiments are being conducted to quantify pollution load contributed by non-point sources.
7.2.2 Waste Water Toxicity Studies
7.2.3 Recovery of Silver and Mercury from COD Waste
Chemical Oxygen Demand (COD) is an important parameter for determining the pollution potential of domestic and industrial wastewater. During the course of its analysis, silver sulphate is added as catalyst while mercuric sulphate is added to overcome the interference from halides. After analysis, the COD waste containing the compounds of silver and mercury are disposed off. Considering the hazardous nature and cost factor, an effort was made to recover silver as metallic silver and mercury as mercuric iodide.
The COD waste was treated with dilute HCl to precipitate silver as silver chloride. The silver chloride was dissolved in dilute ammonia and sodium sulfide was added to precipitate silver as silver sulfide. The silver sulfide was mixed with flux material and ignited to 1200 0C to separate silver metal and slag material.
The waste after recovery of silver, contains mercury in its compound form. Potassium iodide can precipitate mercury as mercuric iodide. But excess addition of potassium iodide will dissolve the precipitate. Hence, calculated amount of 10% potassium iodide was added to precipitate all mercury as mercuric iodide.
As much as 18 grammes of silver were recovered from 15 litres of COD waste. The recovery percent for both silver and mercury was found to be more than 95%.
7.2.4 Analytical Quality Control (AQC/Water) for the Laboratories of Pollution Control Boards/Committees and EPA Recognized Laboratories
Analytical Quality Control (AQC) is one of the main tools by which the performance of a laboratory can be assessed in terms of accuracy and reliability of analytical data generated by the laboratory. The Central Pollution Control Board is monitoring water quality through 507 monitoring stations under GEMS, MINARS, GAP and YAP Programmes comprising rivers, lakes, wells, and ground waters spread over 23 states and 5 Union Territories through various State Pollution Control Boards. In order to obtain reliable and accurate analytical data, CPCB had started regular and organized Analytical Quality Control (AQC) exercise for laboratories of SPCD/PCC, E(P) Act recognized laboratories Under this project, 8th rounds of AQC exercises covering 21 physico-chemical parameters were carried out for 109 laboratories during 2001. The year wise growth in terms of number of participating laboratories under the scheme is presented In Fig. 7.3.
The overall performance of the laboratories was assessed with respect to Ammonical Nitrogen, Chloride, Chromium, Calcium, Boron, Total Hardness, Potassium, Total Dissolved solids, Conductivity, Chemical Oxygen Demand, Sodium, Magnesium, Fluoride, Sulphate, Total Kjehldal Nitrogen, Nitrate-N, Biochemical Oxygen Demand, Fixed Dissolved solids, Total Suspended Solids, Phosphate-P and pH.
7.2.5 Development, Standardization and Preparation of AQC Samples for Total Coliform and Faecal Coliform for Conducting AQC Exercises
CPCB is conducting AQC exercises covering various physico-chemical parameters. In the AQC exercises, bacterial parameters like Total Coliform and Faecal Coliform are not yet included because of constraints in preparation of bacterial AQC samples and their preservation and despatch under ice-cold condition. To overcome these problems it was decided to prepare lyophilized bacterial samples in solid form like the one developed for BODSEED in collaboration with the Centre for Biochemical Technology (CBT), CSIR, Delhi. The main objectives of the proposed project are:
The microbial samples developed were tested in CPCB laboratory to assess the precision and accuracy of the test results. It is planned to introduce Bacterial samples in AQC Inter-laboratory Proficiency Testing (PT) programme during the forthcoming exercises.
7.2.6 Development of Certified Reference Material (CRM) of Toxic Metals using Industrial Effluents
The need for accurate analytical measurements of metals during environmental monitoring is well recognized and accomplished with use of reference material. Standard Reference Materials (SRM`s) are well characterized materials used to maintain the quality of measurements. The use of Certified Reference Material (CRM) during routine measurement of trace metals is expensive. Therefore, it has become necessary to develop economical and indigenous Certified Reference Material (CRM). CPCB has undertaken a project for preparation of Reference Materials for toxic metals in industrial effluents under sponsorship of the Department of Science & Technology (DST).
The Certified Reference Materials for toxic metals like Chromium Copper and Nickel in Electroplating industrial effluent were selected and the homogeneous samples were distributed to 32 reputed environmental and R&D laboratories in the country for analysis. The analytical data as obtained from 32 laboratories have been compiled, statistically analysed and computed in order to certify its use as reference material. The statistically processed data are graphically presented in Fig. 7.4.
7.2.7 Groundwater Studies for Arsenic contamination

Fig. 7.4 CRM PROJECT - TOXIC METALS IN INDUSTRIAL EFFLUENT - Laboratory results

7.2.8 Study of Fluoride in Ground Water of Talcher-Angul Area
Surface and ground water of Angul-Talcher area in Orissa have been reportedly contaminated by fluoride. In absence of organized water supply, ponds, tubewells and dugwells are used by people for different purposes. The untreated wastewater contaminated with fluoride discharged from industrial units were either accumulated in the lagoon or discharged to the river without adequate treatment. As a result, groundwater was contaminated by percolating through soil. Though fluoride is an important element in drinking water but high level of fluoride replaces hydroxide in bones and is deposited in the bones leading to skeletal fluorosis. To study the level of contamination and trend, Central Pollution Control Board, Zonal Office, Kolkata, conducted a study of fluoride pollution in Talcher-Angul area. In this study, 30 tubewells, 16 dugwells, 19 ponds in the affected villages, identified by Orissa State Pollution Control Board, around Smelter units were selected for sampling and analysis. The occurrence of fluoride was observed in 57% tubewells and in 67% dugwells. The fluoride contamination was in the range of 0.5-1.0 mg/l. Though situation is not alarming with respect to permissible limit i.e. 1.0 mg/l but permissible limit may be exceeded in future, if sources are not controlled. About 10 percent tubewells and dugwells were found having fluoride concentration more than 1 mg/l. It was also observed that the level of fluoride in pond water was 0.49- 3.70 mg/l. The contamination of pond water may be due to deposition of airborne particle containing fluorides emitted from the industrial units. It was reported by the villagers that people are having fluoride related symptoms like pain in lower leg.
7.3 RESEARCH STUDIES RELATED TO MUNICIPAL SOLID WASTE
7.3.1 Study on Compost Quality and its Application in Agriculture
The organic matter, which is a source of humus and plant nutrients, is comparatively less in cultivated soils in tropics. Therefore, soil humus has to be replenished through periodic addition of organic manure in the fields. The organic manure prepared from municipal waste not only provides the plant nutrients and humic materials but also result in hygienic disposal of the organic wastes.
The research study covers the analysis of compost made up of municipal solid waste and the sewage sludge for their manure potential and toxicity due to heavy metals and pathogens, as well as their safe and economic application on agricultural land. The analysis of municipal waste compost has shown 1.26%N, 0.6%P and 0.29% K, and C/N ratio as 19.3 to 1. This compost was applied to supplement the inorganic nutrient requirement of maize crop and to replenish the organic matter in cropped soils. Among 8 treatments each in three replicates at 5840 m2 land at IARI, New Delhi, the treatment with 90 kg urea and 30 kg municipal waste compost/sewage sludge has been found better in terms of yield. The harvest index was calculated as 45.63 and 45.03 from compost and sludge treated fields respectively in best found treatment with 90 kg urea and 30 kg municipal waste compost/sewage sludge. Similar experiments have also been conducted with wheat and pea as Rabi crops.
7.3.2 Assessment of Existing Municipal Solid Waste (MSW) Dump Sites at Hyderabad
The study on the assessment of existing municipal solid waste dumpsites has been initiated with the objectives to establish the impact on water and air pollution due to municipal waste dumpsites located at Autonagar and Golconda in Hyderabad city.
Autonagar MSW Dumpsite is spread over an area of about 47 acres and receives an average of 800 MT garbage per day. About 8.7 lakh m3 MSW estimated as 4.35 lakh tonnes, has been dumped at this dumpsite. This dumpsite is in existence for more than 20 years.
Golconda MSW Dumpsite is spread over an area of about 36 acres and receives an average of about 340 MT/day of garbage. An approximate calculation shows that 6.67 lakh cubic metre MSW has been dumped at Golconda dumpsite, which weighs 3.3 lakh tonnes. This dumpsite is in existence for more than 40 years. The study reveals following findings:
7.3.3 Assessment of Impacts of Completed and Existing MSW Landfill Site
Bangalore
Open dumping practice is commonly adopted for the disposal of solid waste, which causes deterioration of environmental quality. To improve the status of solid waste management in the cities, CPCB with the assistance of NEERI, Nagpur, has undertaken study for development of criteria for selection of sites for sanitary landfill with the following objectives:
Methodology for site selection is being developed and validity of selection criteria is being tested for Bangalore city. At present, there are no specific disposal sites in Bangalore city and waste is disposed haphazardly along the road-sides and other places. Initially, the prevailing system of solid waste management in Bangalore was studied and the landfill requirement for the next 10 years is estimated on the basis of waste generation, its composition, present and proposed processing methods. It is estimated that the total quantity of waste generated in Bangalore is approx.1896 MT/day and the land requirement for disposal for next 10 years is about 295.62 hectares.
Bangalore Mahanagar Palika has identified 4 landfill sites - Kannahalli, Medhiagrahara, Gidennhalli and Seegehalli - for landfilling. Studies on various aspects like environmental parameter, hydrological status, soil characteristics, etc. have been conducted for these sites. The validity of the criteria will be tested and modified, for its adoption in other cities.
Kanpur
CPCB has undertaken a study on Assessment of Impact of the Existing and completed Municipal Landfill Sites at Kanpur, with assistance from National Productivity Council, New Delhi. The objective is to assess the impact of landfills on the surroundings and to prepare an Environmental Management Plan (EMP) for these landfill sites. Major findings of the study carried out are as follow:
7.3.4 Development and Standardization of Soil and Solid Waste Analysis for Analytical Quality Control (AQC)
A research project has been taken up to standardize the analysis of soil (polluted) and solid waste with the focus on conducting AQC exercises to the laboratories of SPCB/PCC and also laboratories recognized under E(P), Act. Under the project plan, different polluted soil, industrial solid waste, Hazardous wastes and Municipal Solid Waste have to be analysed.
Samples of Municipal Solid Waste (MSW) from New Delhi Municipal Corporation Compost plant were collected, homogenized and analyzed for various physico chemical parameters and standardization of methodology was completed. The analytical procedure will be provided to all the laboratories for developing the analytical facilities. After fulfilling the preliminary requirements, AQC samples of these types of waste will be distributed and Inter laboratory Proficiency testing will be conducted in phased manner. The outcome of the project work will be helpful in development of the facilities for analyzing Solid wastes at various laboratories of SPCB/PCC’s and improve their analytical capabilities.
7.3.5 Monitoring of Ground Water Quality around Municipal Solid Waste (MSW) Disposal Sites in Delhi
Delhi is one of the largest Municipal solid Wastes (MSW) generating cities. The quantity of wastes is more than 7000 metric tonnes per day. The wastes are disposed mainly on land at three landfill Sites (LFS), namely Ghazipur (East), Okhla (South) and Bhalswa (North). The wastes include mainly organic materials (60%) obtained from various sources like domestic, vegetable markets, hotels, commercial areas etc. These sites are not provided with any lined materials for avoiding percolation of leachate from the solids and possibility of contamination of groundwater. In order to estimate the levels of groundwater contamination in these localities, a research project on the monitoring of ground water quality around solid waste disposal sites in Delhi has been taken up.
Two rounds of groundwater samples numbering 31 from three sites have been collected and analyzed for various physico-chemical parameters (23 parameters) including heavy metals (9 metals), pesticides (5 pesticides), and bacteriological parameters (2). One round of Air borne microbial counts (Total Coliforms and Fungi) was also carried out during November, 2001. The outcome of the project will be helpful for assessing the impact of MSW sites on Ground water quality, air quality, air borne microbial organisms and to formulate strategic plans for selecting MSW land fill sites.
7.3.6 Inventory of Solid Waste Dumpsite of Municipal Corporations in West Bengal.
The survey studies were undertaken through questionnaire survey & visits to Thirty Municipalities under Kolkata Metropolitan Development Area besides Howrah and Kolkata Corporations. A varying quality of municipal solid wastes have been found handled daily by the municipalities ranging from 5 to 2500 MT. In total, daily about 5000 MT of municipal solid wastes were reportedly generated of which nearly 50 percent is from Kolkata Corporation area and about 17 percent from Howrah Corporation area and the rest from the remaining municipalities. Crude dumping of waste at dump site is a common feature. The Kolkata Municipal Corporation is comparatively better organized having arrangement of waste collection, transportation, segregation of waste, weighing, covering of waste dump and lighting arrangement at sites. At other municipalities neither covering of waste nor any other arrangement has been observed except collection and random transport of portion of generated waste. It has been observed that almost hundred percent of the generated solid waste is being collected and disposed off by both, the Kolkata & Howrah Corporations. Regarding other municipalities, nearly 75 percent of the generated waste are collected and disposed off while remaining solid waste lies unattended. Composting of municipal solid waste is rare except at Kolkata Corporation, which compost about 30 percent of solid waste. Waste utilization for generating electricity of 50 MW was being tried by this corporation. No effective measures for full proof protection have yet been introduced for management of municipal solid waste by the municipalities under Kolkata Metropolitan Development Area except for the Kolkata Municipal Corporation.
7.4 STANDARDIZATION OF METHODOLOGY FOR MEASUREMENT OF CERTAIN HAZARDOUS ORGANIC COMPOUNDS (POLYCHLORINATED BIPHENYL)
Polychlorinated Biphenyls (PCB’s) are a range of substances consisting of a biphenyl molecule with or without alkyl or aryl substitutes in which more than one chlorine atom is substituted in the biphenyl nucleus. PCB’s are the group of highly toxic, synthetic, chlorinated organics compounds, with chlorine substitution around biphenyl group as basic structural unit and constitute 209 individual congeners. It is believed that PCB’s do not occur naturally and they are resistant to chemical and biochemical process. The overwhelming problem with PCB’s is their continuing environmental impact. The PCB species are non-biodegradable, stable with high toxicity and having tendency for bioaccumulation.
The PCB’s have potential industrial applications where non-flammability and heat resistant properties are desired and these compounds are more commonly used in heat transfer system, hydraulics/lubricants, transformers, capacitors as plasticizer and as petroleum additives. The PCB congeners, which contain fewer chlorine substitutions in ortho portion, are more toxic than those have more chlorine in these portions. The most toxic PCB’s are tetra, penta and hexachlorobiphenyl congeners that are un substituted in the other position.
The laboratory of Central/State Pollution Control Board and other environmental laboratories have limited technical expertise about measurements of residual PCB’s in environmental matrices viz. waste waters, industrial effluents, sludge and soil. The project standardization of Methodology for measurement of certain hazardous organic compounds, has been undertaken with following objectives.

The analysis of PCB in environmental sample is complicated task as numerous congeners are available in form of complex mixtures. These congeners form overlapping peaks in the chromatograms, complicating the identification and quantification of PCB isomers. Moreover, several other organic constituents viz. Organo-chlorine pesticide etc interferes with measurement of individual PCB congeners. During the reporting year, the PCB’s in the form of various congeners in standard solutions Aroclor have been analyzed by Gas Chromatograph with Electron Capture Detector (ECD) and studies are further continued with Gas Chromatograph Mass Spectrometre (GC-MS).
7.5 EFFICIENCY TESTING OF AUTOCLAVES USED FOR HOSPITAL WASTE TREATMENT BY SPORE TESTING METHODOLOY
Bio-medical waste generation and its safe disposal has become a matter of serious concern due to increasing health facilities & increase in number of hospitals, nursing homes in metropolitan cities. The Biomedical Waste (Management & Handling) Rules, 1998 notified by Govt. of India, has stipulated rules for proper collection, storage, transportation, treatment and disposal of bio-medical waste. As per Bio-medical Waste Rules, 1998 the hospitals have to install treatment facilities like incinerators, autoclaves, etc. for treatment of bio-medical wastes generated to ensure safe treatment & disposal of infectious hospital waste. These treatment facilities should operate at designed efficiency level.
A project has been undertaken by Central Pollution Control Board since the year 1999-2000 for assessment of efficiency of autoclaves used in hospital waste treatment based on standardized spore testing methodology, for In-situ assessment of the efficiency of autoclaves installed at various hospitals within NCT-Delhi using biological indicator to ascertain 4 Log 10 reduction of Bacillus Stereothermophilus indicator.
During first phase of the project, the standardization of spore testing methodology has been undertaken using Bacillus Stereothermophilus as biological indicator with a view for its application for efficiency testing of autoclaves used for hospital waste treatment. The standardized methodology has been used at autoclaves installed at various hospitals within NCT-Delhi for testing of their efficiency during the reporting year. The observations & findings of field-testing are presented in Table 7.1. The results indicate that the Bio-medical waste treatment autoclaves installed at various hospitals are satisfactory with respect to sterilization of bio-medical waste undertaken at these autoclaves.
Table 7.1: Efficiency Testing / Validation by Spore Testing Methodology of Hospital Autoclaves used for Bio - Medical Waste Treatment
|
S.No. |
Hospital |
Sampling Date |
Location inside Autoclave |
Observations |
Efficiency/Validation by 4 log 10 Reduction Indication |
|
1. |
Autoclave 1 |
20.2.2002 |
Exposed spore strips in 9 tubes & 4 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule; colour changed in ampoules due to overheating |
Satisfactory |
|
2. |
Autoclave 2 |
20.2.2002 |
Exposed spore strips in 5 tubes & 4 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule |
Satisfactory |
|
3. |
Autoclave 3 |
21.2.2002 |
Exposed spore strips in 2 tubes & 2 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule |
Satisfactory |
|
4. |
Autoclave 4 |
21.2.2002 |
Exposed spore strips in 5 tubes & 3 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule |
Satisfactory |
|
5. |
Autoclave 5 |
22.2.2002 |
Exposed spore strips in 8 tubes & 5 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule |
Satisfactory |
|
6. |
Autoclave 6 |
22.2.2002 |
Exposed spore strips in 2 tubes & 2 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule |
Satisfactory |
|
7. |
Autoclave 7 |
22.2.2002 |
Exposed spore strips in 6 tubes & 4 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule |
Satisfactory |
|
8. |
Autoclave 8 |
25.2.2002 |
Exposed spore strips in 8 tubes & 4 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule |
Satisfactory |
|
9. |
Autoclave 9 |
25.2.2002 |
Exposed spore strips in 8 tubes & 4 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule; colour changed in ampoules due to overheating |
Satisfactory |
|
10. |
Autoclave 10 |
27.2.2002 |
Exposed spore strips in 6 tubes & 6 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule |
Satisfactory |
| 11. |
Autoclave 11
|
27.2.2002 |
Exposed spore strips in 5 tubes & 4 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule; colour changed in ampoules due to overheating |
Satisfactory |
|
12. |
Autoclave 12 |
28.2.2002 |
Exposed spore strips in 4 tubes & 4 ampoules in bags inside autoclave |
No turbidity developed in any tube/ampoule |
Satisfactory |
Remarks: In case the spore testing strips do not develop turbidity after exposure and incubation, then the efficiency of autoclave is considered satisfactory (i.e. acceptable sterilization).
7.6 FOLLOW-UP ON LABORATORY ACCREDITATION OF CENTRAL POLLUTION CONTROL BOARD’S LABORATORY
The follow-up continued further for Accreditation of Central Pollution Control Board’s laboratories by National Accreditation Board for testing and calibration Laboratories (NABL), Department of Science & Technology, New Delhi. As a part of implementation of quality assurance system at Central Pollution Control Board laboratories. The following activities have been undertaken during the year:
The procurement and installation of following sophisticated instruments have been undertaken during the reporting period.
The Gas Chromatograph – Mass Spectrometer (GC/MS) system Make `Agilent’ model 6890 Plus Gas Chromatograph with 5973 N Mass Detector along with all standard and specified accessories and set of spares in accordance with the contract has been received under EMCBTA project of World Bank and installed at Instrumentation Laboratory. The instrument is used for analysis of trace level of organics, VOCs, SVOCs, PCBs, PAHs and other toxic and hazardous organic substances.
The Gas Chromatograph - Sample Pre-concentration Trap (GC-SPT) has been installed at CPCB laboratories along with Flame Ionization Detector (FID), Pulse Flame Photometric Detector (PFPD) and Sample Pre Concentration Trap (SPT). The instrument is utilised for analysis of organic compounds, various elements and volatile organic carbon (VOCs) in gas phase.
This instrument has been installed at CPCB laboratories along with all standards and specified accessories and set of spares. The instrument is used for analysis of organic compounds, PCBs, organochlorine pesticide, halogenated hydrocarbons and VOCs in ambient air.
The Benzene, Toluene and Xylene Analyzer (BTX Analyzer) along with Portable Caliberator has been installed at CPCB laboratories along with standard accessories and set of spares. The instrument is used for measurement of Benzene, Toluene and Xylene in ambient air.
The Dynamic Dilution System has been fabricated and installed at CPCB laboratories for dynamic dilution of calibration gases. The system has facilities for generation of known quantity of gas for its onward use in calibration of various ambient air analyzers as well as Analytical Quality Control in air samples.
7.8 INDUSTRY SPECIFIC RESEARCH STUDIES
7.8.1 Alternate Technologies in Vinyl Sulphone Industry
Vinyl sulphone, which is one of the largely used dye intermediate with export potential, is generally marketed as the sulphate ester and has the chemical formula H2N-C6H4-SO2-CH2-CH2 -O-SO3-H. The molecular weight of the vinyl sulphone is 281 and nomenclature is 2-4-(amino phenyl)-sulphonyl ethanol hydrogen sulphate. A study was undertaken to establish alternative technologies which are less polluting in nature.
Vinyl sulphone manufacturers cannot continue with conventional manufacturing process and with primary effluent treatment. Incinerating the effluents is very costly. If the process is modified, the liquid effluent can be sent to CETP provided it can tolerate high TDS. Otherwise, effluent can be treated in solar evaporation plant. It can also be spray dried in case land is not available. The modified process results in conservation of raw materials and recovery of by-products.
7.8.2 Technology Development of Specific Microbial Packages for Treatment of Paper & Pulp Industrial Wastewater
The efficiency of treatment of industrial wastewater depends upon the composition of chemicals and their reaction with microbial action on the wastes. There are specific groups of bacteria, which act effectively with specific types of waste and degrade the waste in a fast and efficient manner. Keeping this fact in view, the project has been taken up in collaboration with the Centre for Biochemical Technology (CSIR), Delhi with sponsorship from the Department of Biotechnology, New Delhi.
Samples from Paper mill were collected and analyzed and characterization has been made for screening the suitable and efficient bacterial composition. Trial runs were made to find out the degradation rate of the microbial package using the effluent. The outcome of the project work will be helpful in development of special microbial package which will treat the paper & pulp wastes effectively in terms of time and pollutants like BOD, Lignin, colour, AOX, TDS etc.
7.8.3 Performance Evaluation and Comparative Study of Pollution Control Measures
The treatment of wastewater is essentially a multistage treatment unit, in which the effluent undergoes through physical, chemical and biological treatments. Wastewater purification involves primarily aeration, reduction and precipitation at various stages of treatment. The aeration methods commonly adopted are -Surface Aeration (SA) - one of the oldest technologies, Diffused Aeration (DA)- presently the most popular technology and Rotating Biological Contactors (RBC) – a relatively new technology.
Performance evaluation studies at total number of 14 wastewater treatment plants, achieving bio-degradation through the technologies either individually or in combination, was conducted. The treatment plants include various categories of industries viz. Silk, Garment Washing & Stitching, Information Technology, Milk Processing, Hotel, Engineering, Tannery and Brewery in addition to Domestic Sewage Treatment Plant.
The study reveals that out of the 14 wastewater treatment plants, 11 plants were meeting the compliance standard and only 3 plants were exceeding the stipulated water quality standards.
Choice of Technology
Surface aeration is used either at old treatment plants or at Common Effluent Treatment Plant (CETP), where high quantity of effluent is to be treated.
Diffused aeration being used at comparatively newer plants for both industrial and domestic wastes and it seems to be the most common and popular technology.
RBC technology found being used at limited number of plants, comparatively recent and designed to treat sewage upto capacity of 220 MLD.
Operating Efficiency
Surface Aeration:
The BOD removal efficiency of ETP’s with SA varied from 79% To 97%. Augmentation of SA with anaerobic lagoon showed satisfactory results with nearly 50% BOD reduction at one of the ETP.
Diffused Aeration:
As such the diffused aeration technology is adopted for treatment of domestic and industrial waste and it is found that treatment plant designed with this technology depict satisfactory results with respect to achieving the BOD limit.
Rotating Biological Contactors:
Although sewage treatment plants with RBC technology at two different industries i.e. engineering and hospitality shows satisfactory results in achieving the final effluent BOD within the limit, yet the plant with this technology requires skilled operation and supervision.
Power Consumption
The RBC technology has the unique advantage of low power consumption over other technologies. Diffused aeration, though one of the most effective methods of biological treatment has disadvantage of high power consumption. The power requirement with RBC technology varies between 35 to 40% of power requirement by diffused or surface aeration. An estimate shows a variation in cost of the power requirement from Re. 3 per kilolitre to Re 7 per kilolitre for diffused aeration, and Re 1 per kilolitre to Re 7 per kilolitre for surface aeration and Re 0.3 per kilolitre to Re 3 per kilolitre for rotating biological contactors.
The Surface Aeration Technology is economically viable for larger plants yet operation and maintenance cost of technology has been found higher. Diffused Aeration Technology has higher efficiency with an added advantage of lower energy requirement therefore, found to be best suited for individual industries. The Rotating Biological Contactor Technology is economical and suitable for smaller plants with capacity up to 100 MLD. It has the unique advantage of occupying the less area in addition to low power consumption. RBC plants have higher initial investment, but the maintenance cost is much lower.
7.8.4 Pollution Potential Studies at Oil Refineries including Sulfur Balance and Material Balance
The CPCB West Zonal Office – Vadodara has undertaken a project in association with IIT, Kanpur for in-depth study of Oil Refineries. All four refineries at western zone, namely M/s Reliance Industries Ltd., Jamnagar, M/s Indian Oil Corporation Ltd (IOC), Vadodara, M/s Hindustan Petroleum Corporation Ltd. (HPCL) and M/s Bharat Petroleum Corporation Ltd, (BPCL) Mahual, Mumbai were selected for the dry and wet studies.
During the year dry studies at all the four refineries and wet study at IOC, Vadodara Refinery have been performed. Wet study could not be performed at other refineries due to disturbances in Gujarat. The highlights of the study findings at Oil Refineries is as below:
M/s Reliance Petroleum Ltd., Jamnagar
It was observed from the data that the maximum quantity of Sulfur is retained in the end products. About 20 T/day of SO2 is released from the stacks connected to heaters and SRU units. The summary of the sulfur balance is presented in Table 7.2.
Table 7.2: Summary of Sulfur Balance at Reliance Petroleum Ltd. Jamnagar
|
Sulfur Availability |
Quantity of Sulfur (T/day) |
|
Retained in Products |
192.0 |
|
Recovered in SRU units |
31.2 |
|
Fuels |
|
|
Fuel oil |
8.2 |
|
Fuel gas |
1.0 |
|
Solid waste |
|
|
Coke |
4.8 |
|
Others (Waste gas from SRU, ETP Sludge, Wastewater etc) |
0.5 |
|
Total Sulfur |
237.7 |
H2S generated from various processes is subjected to amine scrubbing at individual process units and the rich amine solution is subjected to regeneration at Sulfur Recovery Units (SRU) for further recovery of sulfur by Clauss process. The sulfur recovery in the SRU unit is reportedly about 99.9% with an average inlet H2S concentration of 70% v/v. Four Number of SRU streams along with secondary incinerators are in operation in the plant. The secondary incinerator has been installed at each SRU unit to convert the un-recovered H2S into SO2 from the flue gas.
Small quantity of fuel oil is used at the heaters located at various process units. The sulfur content in the fuel varied between 0.5 to 1% w/w. In addition to the fuel oil, fuel gas is being used for heating purposes in the furnaces. The sulfur content in the fuel gas has been reported as 0.02%. No inventory about the rate of consumption of each of the fuel streams is maintained. However, the fuel requirement has been computed based on the heat input capacity of the furnace and calorific value of the fuel used.
Six numbers of Gas Turbines along with waste heat boilers and steam generators cater the power requirements. The total capacity of the combined cycle power plant is about 500 MW. Low sulfur natural gas (Bombay High) and Naphtha are being used for power generation.
M/s Indian Oil Corporation – Gujarat Refinery, Vadodara
The studies at the refinery have been undertaken to review the process and wet study at oil refinery. The important pollution potential points are as below:
The IOCL Gujarat Refinery is a 13.7 MTPA capacity plant with sulfur recovery units. Four types of crude are being processed in the plant. The crude from each source is processed in separate atmospheric distillation units (AU). There are five AU process units are in operating in the plant. AU-5 is dedicated to process imported crude, which contains high sulfur. Furnace oil and fuel gas are being used for heating purposes in the furnaces located at various process units.
Three streams of sulfur recovery units (cold bed process) are in operation in the plant. H2S from the main header is supplied to al three steams in the respective design loads for a maximum recovery of 35TPD and 18 TPD respectively.
7.8.5 Pollution potential Studies at Small Scale Textile, Dyeing and Printing Units at Sanganer, Jaipur (Rajasthan)
Sanganer town is situated at outskirt of Jaipur and known for its textile (bed-sheets) dying and printing at twelve clusters of small-scale industries. The main process involved in textile processing units are de-sizing, bleaching, dying, screen printing and post-print washing. Most of the industries have been using rapid indigo, direct aniline black dyes however, none of the industry has any effluent treatment plant. The untreated industrial wastewater along with untreated domestic sewage may be seen accumulated in many areas in absence of proper drainage. Sometimes, the wastewater joins local nullah/canal through kuchcha drains. The possibility of percolation of coloured effluent resulting into groundwater pollution is quite high.
The proposal of installation of CETP in different clusters mooted by RSPCB was not accepted either, by the industries and their association due to high capital and operational cost. Legal action has been launched by State Pollution Control Board against these industries.
The pollution potential assessment studies have been undertaken by CPCB Zonal Office – Bhopal to assess the pollution generated by the industries in different clusters in Sanganer town and to find out a viable solution for pollution control. The findings and major recommendations of the study include the following:
Most of the industries are very small spread in twelve clusters and cannot afford individual ETPs. CETP may not be viable solution especially in the clusters having lesser number of industries, which can share the cost of CETP and its operation. Besides, providing twelve CETPs in a small town appears uneconomical and non-viable. The Public Health Engineering Department has planned to provide elaborate wastewater collection system in the area terminating into sewage treatment plant. The scheme for acceptance of industrial effluent into public sewer may be undertaken by local authorities based on "Sewer Regulations" of Gujarat State.
7.8.6 Assessment of Residual Pesticides in Vegetables
in Dhapa in Kolkata
The study has been undertaken to determine residues of organo-chlorine pesticides like DDT, HCH, Endosulfan, Aldrin, Dieldrin and Heptachlor in various types of vegetables. The residual pesticides was predominant in radish and cauliflower whereas onion, cabbage and cucumber, comparatively less pesticide residues have been found among thirteen varieties of vegetables under the present study.
Cauliflower and cabbage, the two commercially important vegetables preferred by most consumers during winter season showed contrast picture with regard to accumulation of different forms of pesticides. Cauliflower contained all the forms of residues with higher values (i.e. 2-3 ng/gm) of Heptachlor, DDT and BHC and little lower values (2 - <2 ng/gm) of Aldrin, Dieldrin and Endosulfan. In contrast, cabbage contained only BHC and Heptachlor compounds and the concentration were below 1 ng/gm. Other compounds of chlorinated pesticides were below detection level.
The accumulation of the chlorinated pesticides in terms
of pesticide residue was BHC > Endosulfan > DDT > Aldrin > Dieldrin
> Heptachlor.
Coriander leaf contained pesticide residue with varying concentration ranging between 0.3 ng/gm (dieldrin) to 5.3 ng/gm (BHC). The occurrence of pesticide residues was little different as assessed in order from high to low concentration i.e. BHC> DDT > Endosulfan >Heptachlor> Aldrin > Dieldrin. In general, DDT, BHC and Endosulfan were encountered comparatively in more concentration than Aldrin, Dieldrin and Heptachlor.
7.9 STUDIES ON POLLUTION ASSESSMENT AT RAILWAY STATION
With the growing number of trains/ commuters and their activities at station premises, the overall working and living environment at Railway Stations are increasingly affected. Research studies have been undertaken by the Central Pollution Control Board, East Zonal Office to assess the sanitation conditions in the station premises and other steps taken by Railway authorities.
Howrah station is the only railway station in the country, which has treatment facilities exclusively for the effluent generated from station premises. The Operation and Maintenance of ETP was satisfactory and meeting the stipulated norms for discharge into the Hugli river. Despite regular floor cleaning, the respirable dust has been found significantly high (370 to 460 ug/m3) at platforms receiving local trains. Dust concentration is relatively low (150 to 200 ug/m3) in common waiting lobbies of old and new platforms.