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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 2000-2001
in various fields like environmental monitoring, pollution assessment, pollution
control, treatability studies, standardisation of analytical techniques, analytical
quality control (AQC); continuous monitoring of air and water quality and meteorological
studies are summarised below.
7.1 STANDARDIZATION OF METHODOLOGY FOR ANALYSIS OF ADSORBABLE ORGANIC HALOGENS (AOX) IN
ENVIRONMENTAL SAMPLES
To propose standard procedure for Adsorbable
organic halogen (AOX) analysis and to develop the capability for estimation of
AOX in different types of environmental samples, the project on standardization
of methodology for analysis of AOX in environmental samples had been taken up
in during 1998-99 and 1999-2000, within the frame work of project work plan following
main activities have been carried out.
Data
generated by participating laboratories are compiled and processed for repeatability,
reproducibility and spike studies. Under intra-laboratory study, analysis for
four standards of 50,100, 200 & 250 mg/l was carried out by each participating
laboratory to assess the recovery and repeatability of results by the methodology
adopted.
After preliminary period data has been generated satisfactorily
by each of the participating laboratory. The continuous check on accuracy was
followed during the analysis of synthetic and field samples by analysis of control
sample, so that time related deterioration of data could be checked. For this
purpose, quality control chart had been established based on the data generated
during analysis of one of the standard viz.100 mg/l. The estimate of standard
deviation from preliminary period data was used to calculate the warning and action
limit of the chart. Control chart based on the preliminary period and control
sample data provided by the participating laboratories were plotted. Common practice
is used ± 2 S and ± 3 S limits for the warning limit (WL) and control limit (CL)
respectively, where S represents standard deviation.
7.2 DEVELOPMENT, STANDARDIZATION AND PREPARATION OF AQC SAMPLES FOR TOTAL COLIFORM AND FAECAL
COLIFORM PARAMETERS FOR CONDUCTING AQC EXERCISES
CPCB is
conducting AQC exercises since 1991 covering 20 physico-chemical parameters. So
far 8 full rounds of exercises in 17 slots were conducted. In this endeavour,
bacterial parameters like Total Coliform and Faecal Coliform are not yet started
which are very much essential from the water quality assessment point of view.
The constraints in preparation of bacterial AQC samples are preservation and despatch
of samples in ice cold condition. To overcome these problems it was decided to
prepare lyphoilized bacterial samples in solid form like the one developed for
BODSEED in collaboration with Centre for Biochemical Technology(CBT), CSIR, Delhi.
The main objectives of the proposed project are :
Bacterial
samples developed by CBT were tested in CPCB laboratory . Further studies in this
project work is in progress.
7.3 DEVELOPMENT OF CERTIFIED REFERENCE MATERIAL (CRM) OF TOXIC METALS USING INDUSTRIAL EFFLUENTS
Trace metals constitute significant health hazard to human
beings and occupies an area of particular concern and priority in environmental
research. Some of the metals such as Fe, Cu, Zn, Mg, Ca are essential nutrients
to aquatic life as well as to human being upto some extent but some other metals
are toxic to plants and animals. 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 material used to maintain the quality of measurements.
The use of certified reference material (CRM) during routine
measurement of trace metals is quite expensive therefore it has become necessary
to develop economical and indigenous Certified Reference Material (CRM). Central
Pollution Control Board has undertaken project for preparation of Reference Material
for toxic metals in industrial effluents under sponsorship of Department of Science
& Technology (DST). During first phase of the project (Year 2000-2001). The Certified
Reference Material for Nickel, Chromium and Copper were proposed to developed.
For preparation of CRMs using electroplating industrial effluent, the samples
and standard solutions for the metals Nickel, Chromium and Copper had been distributed
to 32 reputed environmental and R&D laboratories in the country for analysis.
In order to certify it as Reference Material, the analytical data as obtained
from 32 laboratories have been compiled, statistically processed and computed
in order to certify its use as reference material and to certify its reference
value. During second phase of the project, the stability of the developed CRM's
have been thoroughly studied at room temperature in order to assess the stability,
degradability (if any) in the solution and consequent changes in CRM due to storage.
These samples have been analysed regularly for about an year on monthly frequency.
The change in the metal contents, summary of observations on analytical values
made on the basis of the results are presented in Table 7.1.
Table
7.1 Stability Test of Developed CRMs and Control Samples stored at Room temperature
| S.No. |
Month |
Certified
Reference Material Average Concentration |
Control
SampleAverage Concentration | ||||
| Nickel(mg/l) |
Cromium(mg/l) |
Copper
(mg/l) | Nickel(mg/l) |
Cromium
(mg/l) | Copper(mg/l) | ||
| 1. | April,2000 |
4.25 |
6.50 |
2.10 |
2.53 |
1.45 |
1.97 |
| 2. | May, 2000 | 4.39 |
5.16 |
1.83 |
2.30 |
1.43 |
1.71 |
| 3. | June, 2000 | 4.20 |
5.06 |
1.92 |
2.36 |
1.49 |
1.78 |
| 4. | July, 2000 | 4.06 |
5.18 |
1.87 |
2.27 |
1.45 |
1.73 |
| 5. | August, 2000 | 4.06 |
5.25 |
1.96 |
2.23 |
1.43 |
1.79 |
| 6. | September,2000 | 4.14 |
5.77 |
1.92 |
2.16 |
1.37 |
1.76 |
| 7. | October, 2000 | 3.80 |
7.12 |
1.85 |
2.16 |
1.62 |
1.72 |
| 8. | November, 2000 | 3.73 |
7.74 |
1.81 |
2.14 |
1.54 |
1.72 |
| 9. | December, 2000 | 3.86 |
7.52 |
2.06 |
2.27 |
1.40 |
1.89 |
| 10. | January, 2001 | 3.74 |
6.35 |
2.12 |
2.02 |
1.56 |
1.94 |
| 11. | February, 2001 | 3.72 |
6.52 |
2.06 |
1.99 |
1.39 |
1.93 |
| 12. | March, 2001 | 3.87 |
5.57 |
2.02 |
2.16 |
1.31 |
1.84 |
|
Minimum Value | 3.72 |
5.06 |
1.81 |
1.99 |
1.31 |
1.71` | |
|
Maximum Value | 4.39 |
7.74 |
2.12 |
2.53 |
1.62 |
1.97 | |
|
Average Value | 3.99 |
6.14 |
1.96 |
2.22 |
1.45 |
1.82 | |
|
Average Recovery | 93.88% |
94.62 % |
93.33% |
87.75% |
100% |
92.39 % | |
7.4 DEVELOPMENT
OF TOXICITY BASED STANDARD FOR TEXTILE INDUSTRIES
For
the development of toxicity based Minimum National Standards (MINAS), a collaborative
project had been initiated by CPCB involving five laboratories viz. Gujarat Pollution
Control Board, Gandhinagar; National Institute of Occupational Health, Ahmedabad;
National Environmental Engineering Research Institute, Nagpur and two laboratories
of CPCB located at Kanpur and Delhi. The project work has been undertaken at seven
ETPs and one CETP. The selected treatment plants treat effluents generated from
synthetic and natural fabric processing units and are located in the states of
Gujarat, Uttar Pradesh, Haryana and Rajasthan.
The treated and untreated
wastewater samples were jointly collected thrice from the selected ETPs by all
the five participating laboratories. The samples thus collected were analyzed
for toxicity independently by the laboratories adopting the BIS approved method
based on dimensionless toxicity factor (TF). The Toxicity Factor (TF) is the minimum
dilution required for the hundred percent survival of test fish during a period
of 48 hours.
The analytical results indicates that the range of toxicity
factor in the untreated effluents ranged between 4 to 16, whereas in treated effluent
its value ranged between 1 to 2. Thus the range of percent toxicity reduction
after treatment varied from 75 to 100 percent.
On the basis of results,
the Toxicity factor as one (TF=1) recommended as toxicity standard for textile
industries, under MINAS, the standard indicates that the treated effluent should
not cause any fish mortality, if exposed in the effluents for a period of 48 hrs.
7.5 DEVELOPMENT & STANDARDIZATION OF SPORE TESTING METHODOLOY
FOR EFFICIENCY TESTING OF AUTOCLAVES USED FOR HOSPITAL WASTE TREATMENT
The increasing Bio-medical waste generation has become a matter of serious
concern for safe disposal of hospital waste in recent years due to increasing
health facilities & 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 during the years 1999-2000 & 2000-2001
to develop spore-testing methodology for assessment of efficiency of autoclaves
used in hospital waste treatment. The major objectives of the project are:
The standardization of spore testing methodology has been undertaken using Bacillus Streothermophilus as biological indicator with a view for its application for efficiency testing of autoclaves used for hospital waste treatment. The standardized methodology has been tested at autoclaves installed at various hospitals within NCT-Delhi for testing their efficiency. The observations & findings of field-testing are presented in Table 7.2.
Table
7.2 Efficiency Testing/Validation of Hospital Autoclaves in
NCT-Delhi by
Spore Testing Methodology
| S.No. |
Autoclave
Location | Sampling
Month | Location
inside Autoclave | Observations |
Efficiency
Validation |
| 1. | Autoclave
I Dilshad Garden | June, 2000 | Exposed
spore strips in 12 tubes in bags inside autoclave | No
turbidity developed in any tube | Satisfactory |
| 2 | Autoclave
II Hari Nagar | September, 2000 | Exposed
spore strips into tubes in bags inside autoclave | Turbidity
developed in one tube | Partially satisfactory |
| 3. | Autoclave-III
Najafgarh | September, 2000 | Exposed
spore strips in 5 tubes in bags inside autoclave | No
turbidity developed in any tube | Satisfactory |
| 4. | Autoclave-IV
Sarita Vihar | March, 2001 | Exposed
spore strips in 8 tubes in bags inside autoclave | No
turbidity developed in any tube | 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).
The
results indicate that the Bio-medical waste treatment autoclaves installed at
the hospitals are satisfactory with respect to sterilization of bio-medical waste
undertaken at these autoclaves.