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

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4.0 SCOPE<br />

This method is applicable for measurement of oxides of nitrogen in ambient air.<br />

5.0 RANGE AND SENSITIVITY<br />

5.3 Instruments usually have multiple measurement ranges; typically 0 to 0.2, 0.5,<br />

1.0 or 2.0 ppm v/v. For ambient monitoring, the most commonly used ranges are<br />

the 0 to 0.5 and 0 to 1.0 ppm v/v.<br />

5.4 The lower detectable limit is determined by the instrument range being used. For<br />

the 0 to 0.5 ppm range a lower detectable limit of 0.01 ppm can be achieved (3).<br />

6.0 INTERFERENCES<br />

6.2 The chemiluminescent reaction of nitric oxide and ozone is not generally subject<br />

to interferences from commonly found pollutant species such as ozone, carbon<br />

monoxide and sulfur dioxide (4). However, any compound capable of being<br />

converted to nitric oxide in the instrument converter (Section 8.1.3) could be a<br />

possible interferent in the measurement of NOx. In this regard, gaseous<br />

ammonia could present a problem at elevated temperatures (600 o C) in thermal<br />

converters; also certain organic nitrates and nitrites have been shown to<br />

decompose stoichiometrically to nitric oxide (5,6,7). Nitric acid reaching the<br />

converter is also decomposed to NO. A continuous method for measuring nitric<br />

acid at ambient levels based on a modified chemiluminescence analyzer has<br />

been reported (8).<br />

7.0 PRECISION AND ACCURACY<br />

7.3 Precision is defined by the stability and repeatability of response to NO.<br />

Response instability due to baseline drift should be equivalent to no more than +<br />

0.020 ppm v/v over a 24-h period, and the noise level to no more than + 0.005<br />

ppm v/v in the 0 to 0.5 ppm instrument range. Repeatability of response to a<br />

standard NO-air mixture should have a coefficient of variation not greater than<br />

2%. This latter precision figure represents the composite error that is associated<br />

with both the NO measurement and the standardization operations (9).<br />

7.4 Accuracy is dependent on the calibration equipment flow systems, and the<br />

absolute concentration of the NO standard gas cylinder. The calibration flow<br />

system specifications contained in the Section 10.2, together with a NO standard<br />

gas cylinder of Standard Reference Material (SRM) or Certified Reference<br />

Material (CRM) <strong>quality</strong> (Section 9.2) are capable of performing instrument<br />

calibrations to an accuracy of + 5%.<br />

129

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