Department of Civil and Environmental Engineering, University of California at Davis, Davis, California 95616, USA.
Environ Sci Technol. 2010 Apr 1;44(7):2309-14. doi: 10.1021/es902864u.
The San Joaquin Valley (SJV) in California currently experiences some of the highest surface ozone (O(3)) concentrations in the United States even though it has a population density that is an order of magnitude lower than many urban areas with similar ozone problems. Previously unrecognized agricultural emissions may explain why O(3) concentrations in the SJV have not responded to traditional emissions control programs. In the present study, the ozone formation potentials (OFP) of livestock feed emissions were measured on representative field samples using a transportable smog chamber. Seven feeds were considered: cereal silage (wheat grain and oat grain), alfalfa silage, corn silage, high moisture ground corn (HMGC), almond shells, almond hulls, and total mixed ration (TMR = 55% corn silage, 16% corn grain, 8% almond hulls, 7% hay, 7% bran + seeds, and 5% protein + vitamins + minerals). The measured short-term OFP for each gram of reactive organic gas (ROG) emissions from all livestock feed was 0.17-0.41 g-O(3) per g-ROG. For reference, OFP of exhaust from light duty gasoline powered cars under the same conditions is 0.69 +/- 0.15 g-O(3) per g-ROG. Model calculations were able to reproduce the ozone formation from animal feeds indicating that the measured ROG compounds account for the observed ozone formation (i.e., ozone closure was achieved). Ethanol and other alcohol species accounted for more than 50% of the ozone formation for most types of feed. Aldehydes were also significant contributors for cereal silage, high moisture ground corn, and total mixed ration. Ozone production calculations based on feed consumption rates, ROG emissions rates, and OFP predict that animal feed emissions dominate the ROG contributions to ozone formation in the SJV with total production of 25 +/- 10 t O(3) day(-1). The next most significant ROG source of ozone production in the SJV is estimated to be light duty vehicles with total production of 14.3 +/- 1.4 t O(3) day(-1). The majority of the animal feed ozone formation is attributed to corn silage. Future work should be conducted to reduce the uncertainty of ROG emissions from animal feeds in the SJV and to include this significant source of ozone formation in regional airshed models.
加利福尼亚州的圣华金谷(SJV)目前经历着美国一些最高的地表臭氧(O3)浓度,尽管其人口密度比许多具有类似臭氧问题的城市低一个数量级。以前未被认识到的农业排放可能解释了为什么 SJV 的 O3 浓度没有对传统的排放控制计划做出反应。在本研究中,使用可运输的烟雾箱对代表性田间样本中的牲畜饲料排放物的臭氧形成潜力(OFP)进行了测量。考虑了七种饲料:谷物青贮料(小麦谷物和燕麦谷物)、紫花苜蓿青贮料、玉米青贮料、高水分地面玉米(HMGC)、杏仁壳、杏仁皮和全混合日粮(TMR = 55%玉米青贮料、16%玉米谷物、8%杏仁皮、7%干草、7%麸皮+种子、5%蛋白质+维生素+矿物质)。从所有牲畜饲料每克反应性有机气体(ROG)排放物中测量到的短期 OFP 为 0.17-0.41 g-O3 每克-ROG。作为参考,在相同条件下,轻型汽油动力汽车尾气的 OFP 为 0.69 +/- 0.15 g-O3 每克-ROG。模型计算能够再现动物饲料的臭氧形成,表明所测量的 ROG 化合物解释了观察到的臭氧形成(即实现了臭氧闭合)。对于大多数类型的饲料,乙醇和其他醇类物质占臭氧形成的 50%以上。对于谷物青贮料、高水分地面玉米和全混合日粮,醛类也是重要的贡献者。基于饲料消耗量、ROG 排放率和 OFP 的臭氧生成计算预测,动物饲料排放物主导着 SJV 中 O3 形成的 ROG 贡献,总生成量为 25 +/- 10 t O3 天-1。SJV 中估计第二大臭氧生成 ROG 源是轻型车辆,总生成量为 14.3 +/- 1.4 t O3 天-1。动物饲料臭氧形成的大部分归因于玉米青贮料。未来的工作应进行以减少 SJV 中动物饲料 ROG 排放的不确定性,并将这一重要的臭氧形成源纳入区域空气流域模型中。