Aerodynamic performance of a low-speed wind tunnel
The determination of the odour mass flow emitted from a source is a very important step and forms the basis for all subsequent considerations and calculations. Wastewater treatment plants, as well as waste treatment facilities, consist of different kinds of odour sources. Unfortunately, most of the...
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description | The determination of the odour mass flow emitted from a source is a very important step and forms the basis for all subsequent considerations and calculations. Wastewater treatment plants, as well as waste treatment facilities, consist of different kinds of odour sources. Unfortunately, most of the sources are passive sources, where no outward air flow-rate can be measured, but where odorants are obviously emitted. Thus, a type of sampling is required that allows to measure the emitted odour flow-rate (OFR). To achieve this, different methods are in use worldwide. Besides indirect methods, such as micrometeorological atmospheric dispersion models, which have not been used in Germany (in other countries due to different problems, direct methods are also used). Direct measurements include hood methods, commonly divided into static flux chambers, dynamic flux chambers and wind tunnels. The wind tunnel that we have been operating in principle since 1983 is different from all subsequent presented wind tunnels, in that we operate it at a considerably lower wind speed than the others. To describe the behaviour of this wind tunnel, measurement of the flow pattern in this low-speed tunnel are under way, and some initial results are presented here. |
doi_str_mv | 10.2166/wst.2004.0220 |
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Wastewater treatment plants, as well as waste treatment facilities, consist of different kinds of odour sources. Unfortunately, most of the sources are passive sources, where no outward air flow-rate can be measured, but where odorants are obviously emitted. Thus, a type of sampling is required that allows to measure the emitted odour flow-rate (OFR). To achieve this, different methods are in use worldwide. Besides indirect methods, such as micrometeorological atmospheric dispersion models, which have not been used in Germany (in other countries due to different problems, direct methods are also used). Direct measurements include hood methods, commonly divided into static flux chambers, dynamic flux chambers and wind tunnels. The wind tunnel that we have been operating in principle since 1983 is different from all subsequent presented wind tunnels, in that we operate it at a considerably lower wind speed than the others. To describe the behaviour of this wind tunnel, measurement of the flow pattern in this low-speed tunnel are under way, and some initial results are presented here.</description><identifier>ISSN: 0273-1223</identifier><identifier>ISBN: 9781843394792</identifier><identifier>ISBN: 1843394790</identifier><identifier>EISSN: 1996-9732</identifier><identifier>DOI: 10.2166/wst.2004.0220</identifier><identifier>PMID: 15484743</identifier><language>eng</language><publisher>England: IWA Publishing</publisher><subject>Air flow ; Air Pollutants - analysis ; Atmospheric diffusion ; Atmospheric models ; Chambers ; Environmental Monitoring - methods ; Flow pattern ; Flow rates ; Mass flow ; Measurement methods ; Meteorological Concepts ; Models, Theoretical ; Odorants ; Odorants - analysis ; Odors ; Pollution dispersion ; Waste Disposal, Fluid - methods ; Waste treatment ; Wastewater treatment ; Wastewater treatment plants ; Wind ; Wind speed ; Wind tunnels</subject><ispartof>Water science and technology, 2004-01, Vol.50 (4), p.57-64</ispartof><rights>Copyright IWA Publishing Aug 2004</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c381t-bcdcc9f87b5c80bc2edef579f41153089718e6d93231b304c92a2acffbdfa6c3</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>309,310,314,780,784,789,790,27924,27925</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/15484743$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><contributor>Koe, LCC</contributor><contributor>Liang, DT</contributor><contributor>Stuetz, RM (eds)</contributor><creatorcontrib>Frechen, F-B</creatorcontrib><creatorcontrib>Frey, M</creatorcontrib><creatorcontrib>Wett, M</creatorcontrib><creatorcontrib>Löser, C</creatorcontrib><title>Aerodynamic performance of a low-speed wind tunnel</title><title>Water science and technology</title><addtitle>Water Sci Technol</addtitle><description>The determination of the odour mass flow emitted from a source is a very important step and forms the basis for all subsequent considerations and calculations. Wastewater treatment plants, as well as waste treatment facilities, consist of different kinds of odour sources. Unfortunately, most of the sources are passive sources, where no outward air flow-rate can be measured, but where odorants are obviously emitted. Thus, a type of sampling is required that allows to measure the emitted odour flow-rate (OFR). To achieve this, different methods are in use worldwide. Besides indirect methods, such as micrometeorological atmospheric dispersion models, which have not been used in Germany (in other countries due to different problems, direct methods are also used). Direct measurements include hood methods, commonly divided into static flux chambers, dynamic flux chambers and wind tunnels. The wind tunnel that we have been operating in principle since 1983 is different from all subsequent presented wind tunnels, in that we operate it at a considerably lower wind speed than the others. 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Wastewater treatment plants, as well as waste treatment facilities, consist of different kinds of odour sources. Unfortunately, most of the sources are passive sources, where no outward air flow-rate can be measured, but where odorants are obviously emitted. Thus, a type of sampling is required that allows to measure the emitted odour flow-rate (OFR). To achieve this, different methods are in use worldwide. Besides indirect methods, such as micrometeorological atmospheric dispersion models, which have not been used in Germany (in other countries due to different problems, direct methods are also used). Direct measurements include hood methods, commonly divided into static flux chambers, dynamic flux chambers and wind tunnels. The wind tunnel that we have been operating in principle since 1983 is different from all subsequent presented wind tunnels, in that we operate it at a considerably lower wind speed than the others. To describe the behaviour of this wind tunnel, measurement of the flow pattern in this low-speed tunnel are under way, and some initial results are presented here.</abstract><cop>England</cop><pub>IWA Publishing</pub><pmid>15484743</pmid><doi>10.2166/wst.2004.0220</doi><tpages>8</tpages></addata></record> |
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subjects | Air flow Air Pollutants - analysis Atmospheric diffusion Atmospheric models Chambers Environmental Monitoring - methods Flow pattern Flow rates Mass flow Measurement methods Meteorological Concepts Models, Theoretical Odorants Odorants - analysis Odors Pollution dispersion Waste Disposal, Fluid - methods Waste treatment Wastewater treatment Wastewater treatment plants Wind Wind speed Wind tunnels |
title | Aerodynamic performance of a low-speed wind tunnel |
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