灌溉玉米温室气体排放的生命周期评估及其在价值链中的意义。

T. Grant, T. Beer
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引用次数: 37

摘要

这一多机构项目的生命周期评估部分确定了使用玉米生产玉米片所涉及的农场前、农场内和农场后活动的温室气体排放。当排放以二氧化碳当量(CO2-e)表示时,农场前排放占生命周期排放的约6%,农场活动占生命周期温室气体排放的约36%,农场后活动占生命周期温室气体排放的约58%。我们用一包400克的玉米片作为功能单位。温室气体排放的最大单一来源是农场施肥产生的一氧化二氮排放(每包0.126千克二氧化碳)。排在第二位的是生产玉米片所消耗的电力(每包0.086千克二氧化碳)。包装(盒加包,0.06公斤二氧化碳排放量)的制造是第二大来源,然后是油炸玉米片的油(每包0.048公斤二氧化碳排放量)。化肥排放的温室气体主要是一氧化二氮(N2O),其全球变暖潜能值为310千克CO2-e/千克N2O。在典型的灌溉农场系统中,这些排放转化为二氧化碳后,几乎是抽水能源产生的温室气体排放量的三倍。然而,目前从深层钻孔抽水灌溉产生的温室气体排放量几乎是使用地表水灌溉的三倍。在典型的农场中,使用拖拉机排放的温室气体约为抽水排放的三分之一。农场管理技术可用于增加土壤碳和减少温室气体排放。如果目前焚烧残茬的农场实施残茬合并,那么在供应链没有其他变化的情况下,他们将从“摇篮到农场门口”减少30%的排放量。从绝对意义上说,当土壤二氧化碳被包括在内时(即使在这种情况下土壤二氧化碳在国家和国际温室气体清单中不被算作温室气体),我们的测量表明,使用秸秆混合生产玉米的农场的二氧化碳和温室气体排放量比燃烧秸秆的农场的排放量低56%。农场前和农场内的操作每排放一公斤二氧化碳温室气体增加0.40美元的价值。农场后加工每排放一公斤二氧化碳-e温室气体增加2美元的价值。将玉米加工成玉米片比将同等数量的玉米加工成淀粉或乙醇排放更多的温室气体。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Life cycle assessment of greenhouse gas emissions from irrigated maize and their significance in the value chain.
The life cycle assessment component of this multi-institutional project determined greenhouse gas emissions in pre-farm, on-farm and post-farm activities involved in the use of maize for the manufacture of corn chips. When the emissions were expressed in terms of carbon dioxide-equivalents (CO2-e), pre-farm emissions comprised ~6% of the life cycle emissions, on-farm activities comprised ~36% and post-farm activities accounted for ~58% of life cycle greenhouse gas emissions. We used one 400 g packet of corn chips as the functional unit. The single largest source of greenhouse emissions was the emission of nitrous oxide on the farm as a result of fertiliser application (0.126 kg CO2-e per packet). The next largest was electricity used during the manufacture of the corn chips (0.086 kg CO2-e per packet). The manufacture of the packaging (box plus packet, being 0.06 kg CO2-e) was the next largest source and then the oil for frying the corn chips (0.048 kg CO2-e per packet). Greenhouse gas emissions from fertiliser application were primarily nitrous oxide (N2O), which has a global warming potential of 310 kg CO2-e/kg N2O. In typical irrigated farm systems, these emissions, when converted to CO2-e, are almost three times more than the greenhouse gas emissions that result from energy used to pump water. However, pumping irrigation water from deep bores currently produces greenhouse gas emissions that are almost three times those from irrigation using surface waters. Greenhouse gas emissions from the use of tractors on typical farms are about one-third of the emissions from pumping water. Farm management techniques can be used to increase soil carbon and reduce greenhouse gas emissions. If farms that currently burn stubble were to implement stubble incorporation then, in the absence of other changes to the supply chain, they will achieve a 30% reduction in emissions from ‘cradle to farm-gate’. In absolute terms, when the soil carbon dioxide is included (even though soil carbon dioxide in this instance is not counted as a greenhouse gas in national and international greenhouse gas inventories), our measurements indicate that carbon dioxide and greenhouse gas emissions from farms that produce maize using stubble incorporation are 56% lower than emissions from farms that burn their stubble. The pre-farm and on-farm operations add $0.40 value per kg of CO2-e greenhouse gas emitted. Post-farm processing added $2 value per kg of CO2-e greenhouse gas emitted. Processing maize for corn chips emitted more greenhouse gases than processing the same amount of corn for starch or ethanol.
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