Please use this identifier to cite or link to this item: http://hdl.handle.net/11452/32657
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dc.contributor.authorWang, Li Lingjuan-
dc.contributor.authorLi, Qianfeng-
dc.contributor.authorChai, Lilong-
dc.contributor.authorCortus, Erin L.-
dc.contributor.authorWang, Kaiying-
dc.contributor.authorBogan, Bill W.-
dc.contributor.authorNi, Jiqin-
dc.contributor.authorHeber, Albert J.-
dc.date.accessioned2023-05-15T06:30:02Z-
dc.date.available2023-05-15T06:30:02Z-
dc.date.issued2013-
dc.identifier.citationWang-Li, L. vd. (2013). "The national air emissions monitoring study's Southeast Layer Site: Part III. Ammonia concentrations and emissions". Transactions of the Asabe, 56(3), 1185-1197.en_US
dc.identifier.issn2151-0032-
dc.identifier.issn2151-0040-
dc.identifier.urihttp://hdl.handle.net/11452/32657-
dc.description.abstractThis article reports two years of quality-assured measurements of concentrations and baseline emissions of ammonia (NH3) at two tunnel-ventilated high-rise houses (houses 3 and 4) located at an egg production facility in North Carolina. The study was conducted as part of the National Air Emissions Monitoring Study (NAEMS). The inside NH3 concentrations, as represented by the exhaust air, were characterized by significant diurnal and seasonal variations. The lowest exhaust concentrations (17.0 +/- 14.0 ppm in house 3; 15.8 +/- 13.0 ppm in house 4) were observed in early afternoon (i.e., 2:00 p.m. to 3:00 p.m) at the maximum diurnal ventilation rate. The highest concentrations (29.5 +/- 22.7 ppm in house 3; 28.8 +/- 22.2 ppm in house 4) occurred in early morning (i.e., 2:00 a.m. to 3:00 a.m.) when the ventilation rate was the lowest. Similarly, the concentrations were lowest during summer and maximum ventilation rates, and highest during winter and minimum ventilation rates. The average NH3 concentrations were 0.7, 22.9, and 20.7 ppm for inlet air and the exhausts of houses 3 and 4, respectively. The average daily mean NH3 emission rate of house 3 (fully occupied and active) was 0.599 +/- 0.200 g d(-1) hen(-1) (197 +/- 66.3 g d(-1) AU(-1), 18.2 +/- 6.04 g d(-1) m(-2)) at an average ambient temperature of 16.7 degrees C and that of house 4 was 0.600 +/- 0.250 g d(-1) hen(-1) (197 +/- 82.3 g d(-1) AU(-1), 18.2 +/- 7.53 g d(-1) m(-2)) at an average ambient temperature of 16.3 degrees C. Ammonia emission rates exhibited less daily and seasonal variation than inside NH3 concentrations. Slightly elevated NH3 emission rates were observed in early afternoon (12:00 noon to 2:00 p.m), when house temperatures were relatively high. No significant differences in emissions between summer and winter were observed. Factors significantly affecting hen-specific NH3 emissions included house ventilation rate, ambient and exhaust air temperatures, exhaust air humidity ratio, hen population, hen activity, feed and water consumption rates, and manure accumulation time. Among all these factors, house exhaust temperature had the greatest effect on NH3 emission rate, followed by manure accumulation time.en_US
dc.description.sponsorshipAgricultural Air Research Councilen_US
dc.description.sponsorshipAmerican Egg Boarden_US
dc.description.sponsorshipNational Science Foundation (NSF) NSF - Office of the Director (OD) (CBET-0954673)en_US
dc.language.isoenen_US
dc.publisherAmer Soc Agricultural and Biological Engineersen_US
dc.rightsinfo:eu-repo/semantics/closedAccessen_US
dc.subjectAgricultureen_US
dc.subjectAmmoniaen_US
dc.subjectConcentrationen_US
dc.subjectDiurnal patternen_US
dc.subjectEmission rateen_US
dc.subjectHigh-rise layer housesen_US
dc.subjectNAEMSen_US
dc.subjectSeasonal variationen_US
dc.subjectGaseous pollutanten_US
dc.subjectHydrogen-sulfideen_US
dc.subjectCarbon-dioxideen_US
dc.subjectBroileren_US
dc.subjectHighriseen_US
dc.subjectRatesen_US
dc.subjectNorth Carolinaen_US
dc.subjectUnited Statesen_US
dc.subjectAmmoniaen_US
dc.subjectConcentration (process)en_US
dc.subjectHousesen_US
dc.subjectManuresen_US
dc.subjectParticulate emissionsen_US
dc.subjectTemperatureen_US
dc.subjectVentilationen_US
dc.subjectVentilation exhaustsen_US
dc.subjectWater supplyen_US
dc.subjectAmmonia concentrationsen_US
dc.subjectDiurnal patternen_US
dc.subjectEmission ratesen_US
dc.subjectExhaust temperatureen_US
dc.subjectManure accumulationsen_US
dc.subjectNAEMSen_US
dc.subjectSeasonal variationen_US
dc.subjectWater consumption rateen_US
dc.subjectAir temperatureen_US
dc.subjectAmmoniaen_US
dc.subjectAtmospheric pollutionen_US
dc.subjectConcentration (composition)en_US
dc.subjectDiurnal variationen_US
dc.subjectEgg productionen_US
dc.subjectEmissionen_US
dc.subjectEnvironmental monitoringen_US
dc.subjectManureen_US
dc.subjectMeasurement methoden_US
dc.subjectSeasonal variationen_US
dc.subjectVentilationen_US
dc.subjectAir pollutionen_US
dc.titleThe national air emissions monitoring study's Southeast Layer Site: Part III. Ammonia concentrations and emissionsen_US
dc.typeArticleen_US
dc.identifier.wos000322504200036tr_TR
dc.identifier.scopus2-s2.0-84884174071tr_TR
dc.relation.publicationcategoryMakale - Uluslararası Hakemli Dergitr_TR
dc.contributor.departmentUludağ Üniversitesi/Ziraat Fakültesi/Biyosistem Mühendisliği Bölümü.tr_TR
dc.contributor.orcid0000-0003-0087-6718tr_TR
dc.identifier.startpage1185tr_TR
dc.identifier.endpage1197tr_TR
dc.identifier.volume56tr_TR
dc.identifier.issue3tr_TR
dc.relation.journalTransactions of the Asabeen_US
dc.contributor.buuauthorKılıç, İlker-
dc.contributor.researcheridAAG-8511-2021tr_TR
dc.relation.collaborationYurt dışıtr_TR
dc.subject.wosAgricultural Engineeringen_US
dc.indexed.wosSCIEen_US
dc.indexed.scopusScopusen_US
dc.wos.quartileQ3en_US
dc.contributor.scopusid55156382800tr_TR
dc.subject.scopusBarns; Ammonia; Fans (Equipment)en_US
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