College of Resources and Environment, Hunan Agricultural University, Changsha, 410128, China.
Environ Sci Pollut Res Int. 2019 Jan;26(2):1871-1879. doi: 10.1007/s11356-018-3766-4. Epub 2018 Nov 20.
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 10 μm (PM), PM, PM, PM, 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 NH per hog house averaged 210.42 μg s. The emissions of PM per hog house averaged 2.017 μg h for PM, 2.149 μg h for PM, 2.305 μg h for PM, 3.950 μg h for PM, and 9.317 μg h for TSP. The emissions of PM per hog house average 2.017 μg h, 2.149 μg h, 2.305 μg h, 3.950 μg h, and 9.317 μg h, respectively for PM, PM, PM, PM, and PM. In each hog house, while the quantity of manure determined the concentration of NH, biological fermentation bed was able to control the ammonia volatilization compared with other three manure handling methods. The largest percentage of fine PM (< 10 μm) is produced by the manual waterless method for manure handling. When it came to the manual waterless method, largest amount of fine PM (< 10 μm) was founded to form. Among various contributions of secondary inorganic PM to PM, the NH was a dominant factor. Based on our experiment, the absolute concentration of NH was inversely proportional to the concentration of PM when the background influence was removed.
大气颗粒物(PM)和来自牲畜饲养的氨污染由于全球范围内牲畜养殖场的兴起而逐渐成为环境关注点。然而,关于与氨有关的大气颗粒物形成的研究仍然有限。因此,在中国南方,对四种不同建筑设计和粪便处理方式的猪舍进行了一项总悬浮颗粒物(TSP)、直径小于 10μm(PM)、PM、PM、PM 和氨的调查研究。从 2016 年到 2017 年,在三个育肥期对四个猪舍进行了监测。每个猪舍的 NH 排放量平均为 210.42μg·头。每个猪舍的 PM 排放量平均为 2.017μg·h 的 PM、2.149μg·h 的 PM、2.305μg·h 的 PM、3.950μg·h 的 PM 和 9.317μg·h 的 TSP。每个猪舍的 PM 排放量平均为 2.017μg·h、2.149μg·h、2.305μg·h、3.950μg·h 和 9.317μg·h 的 PM、PM、PM、PM 和 PM。在每个猪舍中,尽管粪便量决定了 NH 的浓度,但生物发酵床能够控制氨气挥发,而其他三种粪便处理方法则不能。在手动无水的粪便处理方法中,产生的细颗粒物(<10μm)最多。当涉及到手动无水的粪便处理方法时,发现形成了最多量的细颗粒物(<10μm)。在 PM 中二次无机 PM 的各种贡献中,NH 是一个主要因素。根据我们的实验,在去除背景影响后,NH 的绝对浓度与 PM 的浓度成反比。