Department of Animal Science, Texas A&M University, College Station, TX 77843-2471, USA.
Center for Nuclear Energy in Agriculture, University of Sao Paulo, Piracicaba CEP 13416.000, Brazil.
J Anim Sci. 2022 Jul 1;100(7). doi: 10.1093/jas/skac197.
The contribution of greenhouse gas (GHG) emissions from ruminant production systems varies between countries and between regions within individual countries. The appropriate quantification of GHG emissions, specifically methane (CH4), has raised questions about the correct reporting of GHG inventories and, perhaps more importantly, how best to mitigate CH4 emissions. This review documents existing methods and methodologies to measure and estimate CH4 emissions from ruminant animals and the manure produced therein over various scales and conditions. Measurements of CH4 have frequently been conducted in research settings using classical methodologies developed for bioenergetic purposes, such as gas exchange techniques (respiration chambers, headboxes). While very precise, these techniques are limited to research settings as they are expensive, labor-intensive, and applicable only to a few animals. Head-stalls, such as the GreenFeed system, have been used to measure expired CH4 for individual animals housed alone or in groups in confinement or grazing. This technique requires frequent animal visitation over the diurnal measurement period and an adequate number of collection days. The tracer gas technique can be used to measure CH4 from individual animals housed outdoors, as there is a need to ensure low background concentrations. Micrometeorological techniques (e.g., open-path lasers) can measure CH4 emissions over larger areas and many animals, but limitations exist, including the need to measure over more extended periods. Measurement of CH4 emissions from manure depends on the type of storage, animal housing, CH4 concentration inside and outside the boundaries of the area of interest, and ventilation rate, which is likely the variable that contributes the greatest to measurement uncertainty. For large-scale areas, aircraft, drones, and satellites have been used in association with the tracer flux method, inverse modeling, imagery, and LiDAR (Light Detection and Ranging), but research is lagging in validating these methods. Bottom-up approaches to estimating CH4 emissions rely on empirical or mechanistic modeling to quantify the contribution of individual sources (enteric and manure). In contrast, top-down approaches estimate the amount of CH4 in the atmosphere using spatial and temporal models to account for transportation from an emitter to an observation point. While these two estimation approaches rarely agree, they help identify knowledge gaps and research requirements in practice.
反刍动物生产系统的温室气体(GHG)排放贡献因国家和国家内部的地区而异。GHG 排放的准确量化,特别是甲烷(CH4),引发了关于 GHG 清单正确报告的问题,也许更重要的是,如何最好地减少 CH4 排放。本综述记录了现有的方法和方法,以测量和估计各种规模和条件下反刍动物及其粪便产生的 CH4 排放。CH4 的测量经常在研究环境中使用为生物能量目的而开发的经典方法进行,例如气体交换技术(呼吸室、头箱)。虽然非常精确,但这些技术仅限于研究环境,因为它们昂贵、劳动密集且仅适用于少数动物。像 GreenFeed 系统这样的头架已经被用于测量单独或成群圈养或放牧的动物呼出的 CH4。这种技术需要在白天测量期间频繁访问动物,并需要足够数量的采集天数。示踪气体技术可用于测量户外饲养的单个动物的 CH4,因为需要确保背景浓度低。微气象技术(例如,开路激光器)可以测量较大面积和许多动物的 CH4 排放,但存在局限性,包括需要在更长的时间段内进行测量。粪肥 CH4 排放的测量取决于储存类型、动物饲养、感兴趣区域边界内外的 CH4 浓度和通风率,这可能是对测量不确定性贡献最大的变量。对于大面积区域,已经使用飞机、无人机和卫星与示踪通量法、反演模型、图像和 LiDAR(光探测和测距)结合使用,但在验证这些方法方面的研究滞后。估算 CH4 排放的自下而上方法依赖于经验或机械建模来量化单个源(肠道和粪肥)的贡献。相比之下,自上而下的方法使用时空模型来估计大气中的 CH4 量,以说明从排放源到观测点的运输。尽管这两种估算方法很少一致,但它们有助于确定实践中的知识差距和研究需求。