Air quality expert group - Fine particulate matter (PM2.5) in ... - Defra
Air quality expert group - Fine particulate matter (PM2.5) in ... - Defra
Air quality expert group - Fine particulate matter (PM2.5) in ... - Defra
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<strong>PM2.5</strong> <strong>in</strong> the UK<br />
30<br />
35. For non-automatic <strong>PM2.5</strong> monitor<strong>in</strong>g, QA/QC may also <strong>in</strong>clude audit<strong>in</strong>g of the<br />
filter weigh<strong>in</strong>g facilities to ensure that all documented procedures are be<strong>in</strong>g<br />
followed correctly, that the lab is managed and operated effectively, and that all<br />
staff are suitably tra<strong>in</strong>ed for the tasks required of them.<br />
2.3.6 Particulate data ratification<br />
36. Initial data validation checks carried out by the Central Management and<br />
Control Unit (CMCU) and QA/QC units to allow “provisional” data to be<br />
reported to the public are followed by more thorough check<strong>in</strong>g at three-month<br />
<strong>in</strong>tervals. This latter process is called data “ratification”. These checks ensure<br />
that the f<strong>in</strong>al reported data are reliable and consistent.<br />
37. Ratification takes <strong>in</strong>to account all the available <strong>in</strong>formation on the operation of<br />
the <strong>particulate</strong> monitors as outl<strong>in</strong>ed <strong>in</strong> the follow<strong>in</strong>g paragraphs. The first step<br />
of ratification is to go back to the “raw” unvalidated data from the analyser;<br />
this allows traceability of all operations on the data with<strong>in</strong> the ratification<br />
process to be ma<strong>in</strong>ta<strong>in</strong>ed.<br />
38. In general, the ratification of <strong>PM2.5</strong> monitor<strong>in</strong>g data should follow similar<br />
procedures and allow the same full traceability as applies to other <strong>particulate</strong><br />
and gaseous monitor<strong>in</strong>g data. General procedures should <strong>in</strong>clude:<br />
• ratification of the basic report<strong>in</strong>g averages (e.g. hourly or 15-m<strong>in</strong>ute data)<br />
<strong>in</strong> order to maximise data <strong>quality</strong>, not of the composite daily means which<br />
may mask <strong>in</strong>strument operat<strong>in</strong>g problems; and<br />
• tak<strong>in</strong>g account of all <strong>in</strong>formation about the monitor<strong>in</strong>g site and its<br />
surround<strong>in</strong>g location dur<strong>in</strong>g the ratification process.<br />
39. FDMS <strong>in</strong>struments require ratification of both base (non-volatile) and reference<br />
or purge (volatile) measurement channels. These parameters are used to<br />
calculate the total <strong>PM2.5</strong> concentration <strong>in</strong> ambient air on an hour-by-hour basis.<br />
40. S<strong>in</strong>ce for an FDMS <strong>in</strong>strument, total <strong>PM2.5</strong> mass concentration is the sum of<br />
the volatile and non-volatile parts, the data process<strong>in</strong>g and report<strong>in</strong>g of these<br />
three concentrations are <strong>in</strong>extricably l<strong>in</strong>ked. A total <strong>PM2.5</strong> concentration can<br />
only be reported if valid volatile and non-volatile measurements were made.<br />
Similarly, if the total <strong>PM2.5</strong> mass concentration is judged to be unreliable (e.g.<br />
excessive noise), then both the volatile and non-volatile parts are deleted. Figure<br />
2.4 presents FDMS concentrations for a problematical AURN monitor<strong>in</strong>g site<br />
where we are try<strong>in</strong>g to measure especially low concentrations. There are several<br />
features to note here:<br />
• The volatile concentrations dur<strong>in</strong>g this period were low so that the<br />
total mass concentration is only slightly greater than the non-volatile<br />
concentration.<br />
• Unfortunately, all air <strong>quality</strong> <strong>in</strong>struments are affected by signal noise. This<br />
noise becomes more apparent as sensitivity is <strong>in</strong>creased to detect the lower<br />
concentrations. The FDMS <strong>in</strong>strument at this site appears to be produc<strong>in</strong>g<br />
noisy data throughout, believed to be related to difficulties <strong>in</strong> controll<strong>in</strong>g<br />
the enclosure temperature.