Abstract
In contrast to the measurement of gaseous emissions which can be routinely undertaken with an accuracy of a few percent, the measurement of particulate emissions is far more difficult. This arises primarily from the maldistribution of particle concentration within the duct or chimney coupled to the non-uniformity of the gas velocity. It is also partly due to sampling difficulties. Variations in the particle concentration from point to point within a duct or flue may arise for several reasons. These include incomplete mixing downstream of a junction if the two gas streams bear different particle loads, or incomplete mixing downstream of a point where air has leaked into the process gas stream. Since the air is likely to be relatively cool this problem should be detected during the preliminary probing of the gas temperature which is a normal part of the testing procedure. It may then be necessary to seal the leak or to move the sampling position. The other factors which upset the uniformity of the particle distribution are sedimentation and inertial effects when the gas passes round bends or obstacles to the flow. These factors are discussed in the next section.
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References
Bohnet, M. (1978) in Air Pollution Control, Part III (ed. W. Strauss), John Wiley & Sons, New York, pp. 94–7.
British Standard BS 3405 (1983) Measurement of particulate emission, including grit and dust (simplified method), British Standards Institution.
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Her Majesty’s Inspectorate of Pollution (1993) Environmental Protection Act 1990, Technical Guidance Note (Monitoring) M1, Sampling Facility Requirements for the Monitoring of Particulates in Gaseous Releases to Atmosphere. HMSO, London.
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© 1998 Chapman & Hall
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Clarke, A.G., Bartle, G. (1998). Particulate emissions by extractive sampling. In: Clarke, A.G. (eds) Industrial Air Pollution Monitoring. Springer, Dordrecht. https://doi.org/10.1007/978-94-009-1435-3_3
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DOI: https://doi.org/10.1007/978-94-009-1435-3_3
Publisher Name: Springer, Dordrecht
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