Ambient Air quality Monitoring Guidlines. - Maharashtra Pollution ...

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Concentration (µg/m 3 ) 2.2.3 Long Term Variations Status and Trend in annual average concentration of respirable suspended particulate matter (RSPM) in residential areas, industrial areas and traffic intersection area is shown in Fig.2.4. RSPM levels measured at traffic intersection have decreased during 2001 as compared to previous years. RSPM levels at locations in residential areas and traffic intersection were higher than the NAAQS (annual average) during 2001. Concentration (µg/m3) 400 350 300 250 200 150 100 50 0 400 350 300 250 200 150 100 50 0 Figure 2.3: Monthly Average Concentrations of RSPM (1999-2001) at BSZ Marg, New Delhi. Traff. Int. Res. Areas Ind. Areas NAAQS (Res. Areas) NAAQS (Ind. Areas) Months 1998 1999 2000 2001 Year January February March April May June July August September October November December Fig. 2.4: Trend in Annual Average Concentration of Respirable Suspended Particulate Matter in Delhi. 68
3.0 AIR QUALITY MONITORING Ambient air quality monitoring is required to determine the existing quality of air, evaluation of the effectiveness of control programme and to identify areas in need of restoration and their prioritization. National Air Quality Monitoring Programme is described in this chapter alongwith details on pollutants measured and their frequency. Guidelines for monitoring are made for carrying out ambient air quality monitoring under NAMP and description of the programme is essential as the monitoring is carried out to meet the objectives of NAMP. 3.2 Objectives of Air Quality Monitoring The major objectives for air quality monitoring are as below: (i) Background Data In order to generate background data, air quality monitoring is conducted to assess existing level of contamination and to asses possible effects of air contamination occurring in future. (ii) Status and Trend Evaluation The objective is to determine air pollution status and trend information from any continuous air quality monitoring programme. The information is used to determine, whether pollution control strategies as advised by implementing authority are giving acceptable values that is lowering of pollution levels or new or additional control are required to achieve acceptable levels. (iii) Environment Exposure Level Determination The air quality monitoring and survey concern itself with systematic study of considerable segment of environment to define inter-relationship of source of pollution, atmospheric parameter and measurable manifestations in order to evaluate the character and magnitude of existing problem. (iv) Scavenging Behaviour of Environment To understand natural scavenging or cleansing process undergoing in the environment through pollution dilution, dispersion, wind movement, dry deposition, precipitation and chemical transformation of pollutants generated. (v) Air Quality Management To assess the present status to judge effectiveness of air pollution control strategies and long term management of air quality. 69
Page 1 and 2:
1.0 INTRODUCTION Air pollutants are
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The Central Pollution Control Board
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S.No. Problem Area Type of Industry
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(viii) High population exodus to th
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a) Seasonal Variation in Carbon Mon
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Concentration (µg/m 3 ) 2.2.3 Long
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3.2 National Air Monitoring Program
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Number of Monitoring Stations 40 35
Page 17 and 18: 4.0 GUIDELINES FOR MONITORING For s
Page 19 and 20: The variability of pollutant concen
Page 21 and 22: areas, traffic intersections etc. O
Page 23 and 24: Station Type Description Type C Res
Page 25 and 26: available then monitoring of specif
Page 27 and 28: manpower and needs to be calibrated
Page 29 and 30: averaging should be done and plotte
Page 31 and 32: necessary to readjust the position
Page 33 and 34: 5.0 QUALITY ASSURANCE AND QUALITY C
Page 35 and 36: (a) Inter Laboratory Proficiency Te
Page 37 and 38: 2. Infrastructure for conducting In
Page 39 and 40: ZERO GAS VALVE PRESSURE REGULATOR (
Page 41 and 42: is to assess its ability to perform
Page 43 and 44: The mixing ratio of O3 (ppb) must n
Page 45 and 46: (vi) Lack of Dedicated Manpower If
Page 47 and 48: Site staff must be trained so that
Page 50 and 51: NATIONAL AMBIENT AIR QUALITY MONITO
Page 52 and 53: Delhi - 110 032 e-mail : cpcb@alpha
Page 54 and 55: FOREWORD Under the Air (Prevention
Page 56 and 57: Table No. References 161 LIST OF TA
Page 58 and 59: 3.0 INTRODUCTION Air pollutants are
Page 60 and 61: The Central Pollution Control Board
Page 62 and 63: S.No. Problem Area Type of Industry
Page 64 and 65: (viii) High population exodus to th
Page 66 and 67: Monthly average of CO measured at B
Page 70 and 71: 3.2 National Air Monitoring Program
Page 72 and 73: Number of Monitoring Stations 40 35
Page 74 and 75: 4.0 GUIDELINES FOR MONITORING For s
Page 76 and 77: The data requirements, which are re
Page 78 and 79: their levels and determine trends.
Page 80 and 81: Station Type Description traffic vo
Page 82 and 83: Criteria for SO2 Measurements Sourc
Page 84 and 85: calibration parameters change. Meas
Page 86 and 87: The following must be followed for
Page 88 and 89: changed in inclement weather. Set t
Page 90 and 91: 5.0 QUALITY ASSURANCE AND QUALITY C
Page 92 and 93: (a) Inter Laboratory Proficiency Te
Page 94 and 95: The primary requirement for conduct
Page 96 and 97: ZERO GAS VALVE PRESSURE REGULATOR (
Page 98 and 99: is to assess its ability to perform
Page 100 and 101: The mixing ratio of O3 (ppb) must n
Page 102 and 103: (xiii) Lack of Dedicated Manpower I
Page 104 and 105: laboratory staff must be trained so
Page 106 and 107: 1. AIR SAMPLING - GASEOUS 1.0 TITLE
Page 108 and 109: 52 Fig. 1 Sampling Train
Page 110 and 111: 54 Fig. 4 Critical Orifice Device
Page 112 and 113: the pollutant and accordingly selec
Page 114 and 115: contracts with change in humidity.
Page 116 and 117: and temperature has been set down i
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The impulse frequency emitted is pr
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CIRCUIT DIAGRAM - 1 64
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FIG. 1 (a) CIRCUIT DIAGRAM 66
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3. DETERMINATION OF SUSPENDED PARTI
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measurement precision dominates at
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6.4.4 Equilibration Rack - This rac
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Receive Filters, inspect (light tab
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of the face-plate. Look underneath
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Atmosphere". Federal Register, 52 F
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5.0 INTERFERENCES 5.1 Passive Depos
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6.4.4 Numbering Machine - Though fi
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chain-of-the custody log-book and o
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5. DETERMINATION OF SULPHUR DIOXIDE
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88 FIG. 1.0 SO2 SAMPLING TRAIN
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The wavelength calibration of the i
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(ii) The absorbance of the reagent
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pipe cleaner after use. If, the tem
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(A - Ao) (10 3 ) (B) C = ----------
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Then the air sample flows into a re
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integral part of the apparatus, or
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6.4 Pressure Regulator The output s
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FIG. 2 SCHEMATIC DIAGRAM OF A CALIB
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7. CONTINUOUS MEASUREMENT OF CARBON
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6.0 APPARATUS 6.1 NDIR Analyser - f
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BLOWER SAMPLE INLET PORT FOUR WAY V
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Maintain the same sample cell flow
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14.0 CALIBRATION PROCEDURE 14.1 Ana
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connected to the output manifold, t
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FIG. 3 MULTIPLE CYLINDER CALIBRATIO
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(Nondispersive Infrared Spectrometr
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5.0 INTERFERENCES 5.1 Nitric oxide
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7.1.6 Air Pump - Capable of maintai
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9.1.3.2 Solution B - Pipet 25 ml of
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9.4.7 A randomly selected 5-10% of
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9. CONTINUOUS MEASUREMENT OF OXIDES
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8.0 APPARATUS 8.1 Chemiluminescene
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SAMPLE INLET PUMP AIR DRYER OZONE G
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FIG. 3 CALIBRATION SYSTEM COMPONENT
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10.3.1 Flow Conditions - Insure tha
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ates constant. For each calibration
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10. DETERMINATION OF OZONE IN THE A
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7.0 APPARATUS 7.1 Sampling Probe -
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9.4 Blank Correction - Measure the
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11. CONTINUOUS MEASUREMENT OF OZONE
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FIG. 1 SCHEMATIC DIAGRAM OF A TYPIC
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8.2 Air Inlet Filter - A Teflon fil
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9.0 REAGENTS 9.1 Purity - All reage
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Where : Ozone Conc.CTA = the ozone
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1. AIR SAMPLING - GASEOUS 1.0 TITLE
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55 Fig. 1 Sampling Train
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57 Fig. 4 Critical Orifice Device
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the pollutant and accordingly selec
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(iii) Technical Data Measuring rang
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3.1.3 Wind Speed Temperature measur
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(v) Preparation for Use (a) Selecti
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CIRCUIT DIAGRAM - 1 67
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FIG. 1 (a) CIRCUIT DIAGRAM 69
Page 232 and 233:
3. DETERMINATION OF SUSPENDED PARTI
Page 234 and 235:
measurement precision dominates at
Page 236 and 237:
6.4.4 Equilibration Rack - This rac
Page 238 and 239:
Receive Filters, inspect (light tab
Page 240 and 241:
of the face-plate. Look underneath
Page 242 and 243:
Atmosphere". Federal Register, 52 F
Page 244 and 245:
5.0 INTERFERENCES 5.1 Passive Depos
Page 246 and 247:
6.4.4 Numbering Machine - Though fi
Page 248 and 249:
chain-of-the custody log-book and o
Page 250 and 251:
5. DETERMINATION OF SULPHUR DIOXIDE
Page 252 and 253:
91 FIG. 1.0 SO2 SAMPLING TRAIN
Page 254 and 255:
The wavelength calibration of the i
Page 256 and 257:
(ii) The absorbance of the reagent
Page 258 and 259:
pipe cleaner after use. If, the tem
Page 260 and 261:
(A - Ao) (10 3 ) (B) C = ----------
Page 262 and 263:
Then the air sample flows into a re
Page 264 and 265:
integral part of the apparatus, or
Page 266 and 267:
6.4 Pressure Regulator The output s
Page 268 and 269:
FIG. 2 SCHEMATIC DIAGRAM OF A CALIB
Page 270 and 271:
7. CONTINUOUS MEASUREMENT OF CARBON
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6.0 APPARATUS 6.2 NDIR Analyser - f
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BLOWER SAMPLE INLET PORT FOUR WAY V
Page 276 and 277:
Maintain the same sample cell flow
Page 278 and 279:
14.0 CALIBRATION PROCEDURE 14.1 Ana
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connected to the output manifold, t
Page 282 and 283:
FIG. 3 MULTIPLE CYLINDER CALIBRATIO
Page 284 and 285:
(Nondispersive Infrared Spectrometr
Page 286 and 287:
5.0 INTERFERENCES 5.1 Nitric oxide
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7.1.6 Air Pump - Capable of maintai
Page 290 and 291:
9.1.3.2 Solution B - Pipet 25 ml of
Page 292 and 293:
9.4.7 A randomly selected 5-10% of
Page 294 and 295:
9. CONTINUOUS MEASUREMENT OF OXIDES
Page 296 and 297:
9.0 APPARATUS 8.1 Chemiluminescene
Page 298 and 299:
SAMPLE INLET PUMP AIR DRYER OZONE G
Page 300 and 301:
FIG. 3 CALIBRATION SYSTEM COMPONENT
Page 302 and 303:
10.6.1 Flow Conditions - Insure tha
Page 304 and 305:
ates constant. For each calibration
Page 306 and 307:
10. DETERMINATION OF OZONE IN THE A
Page 308 and 309:
7.0 APPARATUS 7.1 Sampling Probe -
Page 310 and 311:
9.4 Blank Correction - Measure the
Page 312 and 313:
11. CONTINUOUS MEASUREMENT OF OZONE
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FIG. 1 SCHEMATIC DIAGRAM OF A TYPIC
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8.2 Air Inlet Filter - A Teflon fil
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9.0 REAGENTS 9.3 Purity - All reage
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Where : Ozone Conc.CTA = the ozone
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