Liu Z, Powers W, Murphy J, Maghirang R
Department of Biological and Agricultural Engineering, Kansas State University, Manhattan 55506.
J Anim Sci. 2014 Apr;92(4):1656-65. doi: 10.2527/jas.2013-7160. Epub 2014 Feb 3.
Literature on NH3 and H2S emissions from swine production facilities in North America was reviewed, and a meta-analysis was conducted on measured emissions data from swine houses and manure storage facilities as well as concentration data in the vicinity of swine production facilities. Results from more than 80 studies were compiled with results from the 11 swine sites in the National Air Emissions Monitoring Study (NAEMS). Data across studies were analyzed statistically using the MIXED procedures of SAS. The median emission rates from swine houses across various production stages and manure handling systems were 2.78 and 0.09 kg/yr per pig for NH3 and H2S, respectively. The median emission rates from swine storage facilities were 2.08 and 0.20 kg/yr per pig for NH3 and H2S, respectively. The size of swine farm that may trigger the need to report NH3 emissions under the Emergency Planning and Community Right-to-Know Act (EPCRA) is 3,410 pigs on the basis of the median NH3 emission rate (4.86 kg/yr per pig), but the threshold can be as low as 992 pigs on the basis of the 90th-percentile emission rates (16.71 kg/yr per pig). Swine hoop houses had significantly higher NH3 emission rate (14.80 kg/yr per pig) than other manure-handling systems (P < 0.01), whereas deep-pit houses had the highest H2S emission rate (16.03 kg/yr per pig, P = 0.03). Farrowing houses had the highest H2S emission rate (2.50 kg/yr per pig), followed by gestation houses, and finishing houses had the lowest H2S emission rate (P < 0.01). Regression models for NH3 and H2S emission rates were developed for finishing houses with deep pits, recharge pits, and lagoons. The NH3 emission rates increased with increasing air temperature, but effects of air temperature on H2S emission rates were not significant. The recharge interval of manure pits significantly affected H2S but not NH3 emission rates. The H2S emission rates were also influenced by the size of the operation. Although NH3 and H2S concentrations at the edge of swine houses or lagoons were often higher than corresponding acute or intermediate minimum risk levels (MRL), they decreased quickly to less than corresponding chronic or intermediate MRL as distances from emission sources increased. At the distances 30 to 1,185 m from emission sources, the average ambient concentrations for NH3 and H2S were 46 ± 46 µg/m(3) and 4.3 ± 8.6 µg/m(3) respectively.
对北美洲养猪生产设施中氨(NH₃)和硫化氢(H₂S)排放的文献进行了综述,并对来自猪舍、粪便储存设施的实测排放数据以及养猪生产设施附近的浓度数据进行了荟萃分析。80多项研究的结果与国家空气排放监测研究(NAEMS)中11个养猪场的结果进行了汇总。使用SAS的混合程序对各项研究的数据进行了统计分析。不同生产阶段和粪便处理系统的猪舍中,NH₃和H₂S的年排放率中位数分别为每头猪2.78千克和0.09千克。猪粪便储存设施中,NH₃和H₂S的年排放率中位数分别为每头猪2.08千克和0.20千克。根据NH₃排放率中位数(每头猪4.86千克/年),依据《应急规划与社区知情权法案》(EPCRA)可能触发报告NH₃排放需求的养猪场规模为3410头猪,但根据第90百分位数排放率(每头猪16.71千克/年),阈值可能低至992头猪。猪棚舍的NH₃排放率(每头猪14.80千克/年)显著高于其他粪便处理系统(P < 0.01),而深坑式猪舍的H₂S排放率最高(每头猪16.03千克/年,P = 0.03)。产仔舍的H₂S排放率最高(每头猪2.50千克/年),其次是妊娠舍,育肥舍的H₂S排放率最低(P < 0.01)。针对有深坑、回灌坑和泻湖的育肥舍,建立了NH₃和H₂S排放率的回归模型。NH₃排放率随气温升高而增加,但气温对H₂S排放率的影响不显著。粪便坑的回灌间隔对H₂S排放率有显著影响,但对NH₃排放率无显著影响。H₂S排放率还受养殖场规模的影响。尽管猪舍或泻湖边缘的NH₃和H₂S浓度通常高于相应的急性或中间最低风险水平(MRL),但随着与排放源距离的增加,它们会迅速降至低于相应的慢性或中间MRL。在距离排放源30至1185米处,NH₃和H₂S的平均环境浓度分别为46±46微克/立方米和4.3±8.6微克/立方米。