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Concentrations and emissions of particulate matter and ammonia from extensive livestock farm in South China

机译:南方广大畜牧农场颗粒物质和氨的浓度和排放

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Atmospheric particulate matter (PM) and ammonia pollution from livestock feeding have gradually become the environmental concerns due to the spring up of livestock farms in worldwide. However, researches about the formation of atmospheric particulate matter related to ammonia are still limited. Therefore, a study to survey the total suspended particles (TSP), PM with the diameter less than 10m (PM10), PM4, PM2.5, PM1, and ammonia was conducted at four types of hog houses distinguished by its building design as well as manure handling methods in South China. Four hog houses were monitored during three fattening periods from 2016 to 2017. The emissions of NH3 per hog house averaged 210.42gs(-1). The emissions of PM per hog house averaged 2.017gh(-1) for PM1, 2.149gh(-1) for PM2.5, 2.305gh(-1) for PM4, 3.950gh(-1) for PM10, and 9.317gh(-1) for TSP. The emissions of PM per hog house average 2.017gh(-1), 2.149gh(-1), 2.305gh(-1), 3.950gh(-1), and 9.317gh(-1), respectively for PM1, PM2.5, PM4, PM10, and PM10. In each hog house, while the quantity of manure determined the concentration of NH3, biological fermentation bed was able to control the ammonia volatilization compared with other three manure handling methods. The largest percentage of fine PM (10m) is produced by the manual waterless method for manure handling. When it came to the manual waterless method, largest amount of fine PM (10m) was founded to form. Among various contributions of secondary inorganic PM to PM1, the NH3 was a dominant factor. Based on our experiment, the absolute concentration of NH3 was inversely proportional to the concentration of PM1 when the background influence was removed.
机译:畜牧饲料的大气颗粒物质(PM)和氨污染逐渐成为全球畜牧农场涌现的环境问题。然而,关于与氨相关的大气颗粒物质形成的研究仍然有限。因此,在四种类型的猪房中,对直径小于10m(PM10),PM4,PM2.5,PM1和氨的总悬浮颗粒(TSP),PM4,PM2.5,PM1和氨的研究进行了调查作为华南地区的粪便处理方法。在2016年至2017年的三个育肥期间监测了四个猪屋。每嘴巴的NH3排放平均为210.42g(-1)。 PM4,3.9505(-1)PM4,3.950GH(-1)的PM1,2.149GH(-1)PM1,2.149GH(-1)的PM1,2.149gh(-1)的排放量为2.0179gh(-1)。 -1)用于TSP。 PM1,PM2分别为PM1,PM2的PM1,PM2分别为2.017gh(-1),2.149gh(-1),2.305g(-1),3.950g(-1)和9.317gh(-1)。 5,PM4,PM10和PM10。在每个猪房中,虽然粪肥量确定NH 3的浓度,但与其他三种粪便处理方法相比,生物发酵床能够控制氨挥发。最大的PM(&LT 19米)的百分比由手工造成的粪便处理制造。当它来到手动无水方法时,成立了最多的PM(&lt 19m)形成。在二级无机PM至PM1的各种贡献中,NH3是一种显性因素。基于我们的实验,当除去背景影响时,NH3的绝对浓度与PM1的浓度成反比。

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