澳大利亚肉牛饲养场排放的间接温室气体NH3和NOx

O. T. Denmead, Deli Chen, D. Griffith, Z. Loh, M. Bai, T. Naylor
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引用次数: 43

摘要

间接温室气体的排放,特别是氮气体氨(NH3)和氮氧化物(NOx),在温室效应中起着重要作用。饲养场是大气NH3的密集来源,但缺乏量化,尽管预计饲养场会产生氮氧化物,但氮氧化物排放率实际上是未知的。在大气中,这些气体参与了几次转化,但最终以气态或液态形式返回地球,然后可以进行进一步的转化,包括形成和排放直接温室气体一氧化二氮(N2O)。IPCC第二阶段指南估计,由于NH3和NOx形成的N化合物在大气中的沉积而间接排放的N2O可能占农业土壤或动物生产系统直接排放的14%。政府间气候变化专门委员会建议,在编制一氧化二氮排放清单估算时,应考虑到这些间接排放。本文是用微气象技术测定澳大利亚两个饲养场NH3和NOx排放量的初步报告。两个饲养场的氮排放以NH3排放为主。两个饲料场冬季NH3平均排放量为46 g N/头。而在0.36 g N/动物d时,氮氧化物的生长量不足该比率的1%。很明显,NH3的释放受地表湿度的支配。表面较湿的饲养场的排放率几乎是另一个饲养场的三倍。IPCC对畜禽NH3和NOx联合排放的默认排放因子为0.2 kg N/kg N排泄,但在我们的工作中,排放因子为0.59 kg N/kg N排泄。NH3和NOx沉积导致的N2O潜在排放估计与直接N2O排放量相同,直接和潜在间接排放的总和约为~3 g N2O- n /动物日。如果在全国范围内应用,这将代表澳大利亚饲养场对N2O的贡献为533g CO2-e,占澳大利亚N2O总排放量的2.2%。
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Emissions of the indirect greenhouse gases NH3 and NOx from Australian beef cattle feedlots
Emissions of indirect greenhouse gases, notably the nitrogen gases ammonia (NH3) and the odd oxides of nitrogen (NOx), play important roles in the greenhouse story. Feedlots are intense, but poorly quantified, sources of atmospheric NH3 and although production of NOx is to be expected in feedlots, rates of NOx emission are virtually unknown. In the atmosphere, these gases are involved in several transformations, but eventually return to the earth in gaseous or liquid form and can then undergo further transformations involving the formation and emission of the direct greenhouse gas nitrous oxide (N2O). The IPCC Phase II guidelines estimate that indirect N2O emissions due to atmospheric deposition of N compounds formed from NH3 and NOx could be ~14% of the direct emissions from agricultural soils or from animal production systems. IPCC recommends that these indirect emissions be accounted for in making inventory estimates of N2O emission. This paper is a preliminary report of emissions of NH3 and NOx from two Australian feedlots determined with micrometeorological techniques. Emissions of nitrogen gases from both feedlots were dominated by emissions of NH3. The average NH3 emission rate over both feedlots in winter was 46 g N/animal.day, while that of NOx was less than 1% of that rate at 0.36 g N/animal.day. It was apparent that NH3 release was governed by the wetness of the surface. Rates of emission from the feedlot with the wetter surface were almost three times those from the other. The IPCC default emission factor for the combined emission of NH3 and NOx from livestock is 0.2 kg N/kg N excreted, but in our work, the emission factor was 0.59 kg N/kg N excreted. Potential emissions of N2O due to NH3 and NOx deposition were estimated to be of the same magnitude as the direct N2O emissions, the sum of direct and potential indirect amounting to ~3 g N2O-N/animal.day. If applied nationally, this would represent a contribution of N2O from Australian feedlots of 533Gg CO2-e or 2.2% of all Australian N2O emissions.
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