Gao Zong-Yuan, Xu Chang, Ni Yuan-Zhi, Shen Gen-Xiang, Miao Wen-Liang, Wang Zhen-Qi, Fu Kan, Qian Xiao-Yong, Cao Guo-Min
School of Resources and Environmental Engineering, East China University of Science and Technology, Shanghai 200237, China.
State Environmental Protection Key Laboratory of Environmental Health Impact Assessment of Emerging Contaminants, State Environmental Protection Key Laboratory of Formation and Prevention of Urban Air Pollution Complex, Shanghai Academy of Environmental Sciences, Shanghai 200233, China.
Huan Jing Ke Xue. 2022 Apr 8;43(4):1829-1843. doi: 10.13227/j.hjkx.202107126.
In order to obtain the ammonia emission level and space-time distribution characteristics of the poultry production industry in the Yangtze River Delta, an online high-resolution monitoring system was used to continuously monitor the atmospheric ammonia concentration in the breeding house and compost shed in a typical large-scale layer farm. By obtaining the ammonia emission level and emission factor during each growth stage, we established the localized ammonia emission inventory for the poultry production industry in the Yangtze River Delta. The results showed that the average daily (NH) in the breeding house and compost shed for spring, summer, autumn, and winter were (1.85±0.38), (4.58±0.33), (3.87±0.12), and (2.83±0.47) mg·m and (2.04±0.50), (4.04±1.04), (2.51±0.67), and (1.55±0.16) mg·m respectively. Ammonia emissions showed a significant daily hourly change trend. The highest hourly ammonia concentration in the layer house appeared from 13:00-14:00 in the afternoon, and the minimum appeared from 01:00-03:00 in the morning. The highest hourly ammonia concentration in the compost shed occurred between 16:00-19:00 in summer and autumn, whereas the diurnal changes in spring and winter were not significant. Hourly changes in ammonia emissions during the day were mainly affected by daily temperature, poultry activities, and manure management. Ammonia concentrations at different growth stages of laying hens showed significant differences. (NH) from young chickens, laying hens, and pre-eliminated chickens were (1.85±0.38), (2.83±0.47), and (1.61±0.32) mg·m, respectively. The ammonia emission rate from laying hens reached 1.53 times and 1.65 times that of young chickens and pre-eliminated chickens, respectively. Metabolism levels and feed intake at different growth stages were the main reasons for the differences in ammonia emissions. Ammonia emission factors for the layer house and compost shed in spring, summer, autumn, and winter were (0.13±0.02), (0.54±0.01), (0.39±0.01), and (0.17±0.01) g·(bird·d) and (0.07±0.01), (0.17±0.02), (0.08±0.01), and (0.04±0.01) g·(bird·d), respectively. Annual ammonia emission factors reached (0.11±0.06) kg·(bird·a) and (0.03±0.02) kg·(bird·a), respectively. Our results suggest that ambient temperature, ventilation mode, chicken house type, and manure removal frequency were the main influencing factors of ammonia emissions from poultry production. The uncertainty ranges of the ammonia emission coefficients reached±122%,±79%, and±74%, and±56%, respectively. Great uncertainties were generated when empirical emission factors were used for emission inventory establishment. Based on the results of online monitoring, model simulation, and literature analysis, we established an ammonia emission inventory for the poultry production industry within the Yangtze River Delta region by adopting the emission factors of (0.16±0.08) kg·(bird·a). In 2019, the total ammonia emission from poultry production was (108.81±54.41) kt. In terms of spatial distribution, ammonia emission intensities in the northern regions were significantly higher than those in the southern parts. The ammonia emission intensities during summer were 3.38-3.56 times higher than those in spring and winter.
为获取长江三角洲地区家禽养殖业的氨排放水平及时空分布特征,采用在线高分辨率监测系统,对典型大型蛋鸡养殖场的鸡舍和堆肥棚内的大气氨浓度进行持续监测。通过获取各生长阶段的氨排放水平和排放因子,建立了长江三角洲地区家禽养殖业本地化氨排放清单。结果表明,鸡舍和堆肥棚内春、夏、秋、冬四季的日均氨浓度分别为(1.85±0.38)、(4.58±0.33)、(3.87±0.12)和(2.83±0.47)mg·m以及(2.04±0.50)、(4.04±1.04)、(2.51±0.67)和(1.55±0.16)mg·m。氨排放呈现出显著的日变化趋势。蛋鸡舍内每小时氨浓度最高值出现在下午13:00 - 14:00,最低值出现在凌晨01:00 - 03:00。堆肥棚内每小时氨浓度最高值在夏季和秋季出现在16:00 - 19:00,而春季和冬季的日变化不显著。白天氨排放的每小时变化主要受日温度、家禽活动及粪便管理影响。蛋鸡不同生长阶段的氨浓度存在显著差异。雏鸡、产蛋鸡和淘汰前鸡的氨浓度分别为(1.85±0.38)、(2.83±0.47)和(1.61±0.32)mg·m。产蛋鸡的氨排放率分别达到雏鸡和淘汰前鸡的1.53倍和1.65倍。不同生长阶段的代谢水平和采食量是氨排放差异的主要原因。鸡舍和堆肥棚春、夏、秋、冬四季的氨排放因子分别为(0.13±0.02)、(0.54±0.01)、(0.39±0.01)和(0.17±与(0.07±0.01)、(0.17±0.02)、(0.08±0.01)和(0.04±0.01)g·(只·d)。年氨排放因子分别达到(0.11±0.06)kg·(只·a)和(0.03±0.02)kg·(只·a)。研究结果表明,环境温度、通风方式、鸡舍类型及清粪频率是家禽生产氨排放的主要影响因素。氨排放系数的不确定范围分别达到±122%、±79%、±74%和±56%。采用经验排放因子建立排放清单时产生了很大的不确定性。基于在线监测、模型模拟及文献分析结果,采用(0.16±0.08)kg·(只·a)的排放因子,建立了长江三角洲地区家禽养殖业氨排放清单。2019年,家禽生产的氨排放总量为(108.81±54.41)kt。在空间分布上,北部地区的氨排放强度显著高于南部地区。夏季的氨排放强度比春季和冬季高3.38 - 3.56倍。