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

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4.2.7 Laboratory requirements<br />

The samples collected from site are analysed in the laboratory. If possible a kiosk can be<br />

constructed at the site and common laboratory apparatus such as refrigerator, balance, oven,<br />

spectrophotometer etc. can be kept at the site so that the collected samples can be analysed at the<br />

site and the losses due to improper sample preservation, transportation can be minimised.<br />

However, enough space must be available with sufficient power at site. If constructing a kiosk at<br />

site is not possible then the samples must be properly preserved and transported to the laboratory<br />

for analysis. The laboratory instrument must be calibrated regularly so as to minimise errors.<br />

4.2.8 Quality assurance<br />

In India a nationwide network would involve large number of monitoring agencies that<br />

would conduct monitoring at number of locations in India. The <strong>quality</strong> assurance<br />

programme aims at achieving comparability of data from various agencies. Quality<br />

assurance can be within laboratory <strong>quality</strong> assurance programme. Internal <strong>quality</strong><br />

assurance may be understood to include normal internal procedures such as periodic<br />

calibrations, duplicate checks, split samples, spiked samples and the keeping of<br />

adequate and neat records (WHO, 1977). External <strong>quality</strong> assurance may be taken to<br />

include those activities that are performed on a more occasional basis, usually outside<br />

the normal routine operations, e.g., on-site system surveys, independent performance<br />

audits, interlaboratory comparisons, and periodic evaluation of internal <strong>quality</strong><br />

assurance data (WHO, 1977). The <strong>quality</strong> assurance procedures are described in detail<br />

in the next chapter.<br />

4.2. 9 Data Handling and Presentation<br />

<strong>Air</strong> <strong>quality</strong> depends on the physical characteristics of the area and the site observations<br />

must be recorded so that data interpretation can be easier. Site observations can be<br />

type of area, whether residential, industrial, sensitive or traffic intersections, distance<br />

from nearby sources, whether location is in a market place etc. Height of instrument<br />

above ground level should also be recorded. The data should be validated by rejecting<br />

erroneous data, applying corrections as per the calibrations performed of flow rates etc.<br />

The data should be recorded on the prescribed formats. The sample of format for<br />

recording data is shown in Annexure-III. Software programs have been developed for<br />

doing data entry in dBase and analysis is done using FoxPro. The data presentation<br />

should be such that the objectives of monitoring are met. One of the objective of<br />

monitoring is to determine compliance to NAAQS so 24-hourly average and annual<br />

average should be computed as NAAQS are given for these averages except for CO<br />

where 8 –hourly and 1-hourly averaging should be performed. 98 th percentile should be<br />

calculated as the NAAQS states that 24-hourly standard can be violated 2% of the times<br />

but not on two consecutive days. One of the objectives is to understand scavenging<br />

behaviour of environment. It is known that particulate matter is scavenged from the<br />

environment during monsoons and in order to understand seasonal variations, monthly<br />

averaging should be done and plotted. Best fit lines should be plotted to determine<br />

trends in air <strong>quality</strong>.<br />

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