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Nitrogen, Phosphorus, and Potassium Flows through the Manure Management Chain in China

机译:中国肥料管理链中的氮,磷和钾流

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摘要

The largest livestock production and greatest fertilizer use in the world occurs in China. However, quantification of the nutrient flows through the manure management chain and their interactions with management-related measures is lacking. Herein, we present a detailed analysis of the nutrient flows and losses in the "feed intake—excretion—housing—storage—treatment—application" manure chain, while considering differences among livestock production systems. We estimated the environmental loss from the manure chain in 2010 to be up to 78% of the excreted nitrogen and over 50% of the excreted phosphorus and potassium. The greatest losses occurred from housing and storage stages through NH3 emissions (39% of total nitrogen losses) and direct discharge of manure into water bodies or landfill (30—73% of total nutrient losses). There are large differences among animal production systems, where the landless system has the lowest manure recycling. Scenario analyses for the year 2020 suggest that significant reductions of fertilizer use (27—100%) and nutrient losses (27—56%) can be achieved through a combination of prohibiting manure discharge, improving manure collection and storages infrastructures, and improving manure application to cropland. We recommend that current policies and subsidies targeted at the fertilizer industry should shift to reduce the costs of manure storage, transport, and application.
机译:世界上最大的畜牧生产和最大的肥料使用发生在中国。但是,缺乏对肥料管理链中养分流及其与管理相关措施之间相互作用的量化。在此,我们在考虑牲畜生产系统之间的差异的同时,对“饲料摄入-排泄-存储-存储-处理-施用”肥料链中的营养流和损失进行了详细分析。我们估计2010年粪肥链造成的环境损失将高达排泄的氮的78%,以及排泄的磷和钾的50%以上。最大的损失发生在房屋和储存阶段,主要是通过排放NH3(占总氮损失的39%)和将粪便直接排入水体或垃圾填埋场(占营养总损失的30-73%)。畜牧生产系统之间存在很大差异,其中无地系统的粪便回收率最低。 2020年的情景分析表明,通过结合禁止粪便排放,改善粪便收集和存储基础设施以及改善粪便应用,可以实现肥料使用量的大幅减少(27-100%)和养分流失(27-56%)的减少。到农田。我们建议,针对化肥行业的现行政策和补贴应改变以减少肥料存储,运输和施用的成本。

著录项

  • 来源
    《Environmental Science & Technology》 |2016年第24期|13409-13418|共10页
  • 作者单位

    Key Laboratory of Agricultural Water Resources, Center for Agricultural Resources Research, Institute of Genetic and Developmental Biology, The Chinese Academy of Sciences, 286 Huaizhong Road, Shijiazhuang, 050021 Hebei, China,Department of Soil Quality;

    Key Laboratory of Agricultural Water Resources, Center for Agricultural Resources Research, Institute of Genetic and Developmental Biology, The Chinese Academy of Sciences, 286 Huaizhong Road, Shijiazhuang, 050021 Hebei, China;

    Research Center for Rural Economy Ministry of Agriculture, No. 56, Xisizhuanta Hutong, Beijing 100810, China;

    College of Resources & Environmental Sciences, Agricultural University of Hebei, Baoding 071001, China;

    Department of Soil Quality,Department of Environmental Sciences, Wageningen University & Research, P.O. Box 47, 6700 AA Wageningen, The Netherlands;

    Department of Soil Quality,Department of Environmental Sciences, Wageningen University & Research, P.O. Box 47, 6700 AA Wageningen, The Netherlands;

    Key Laboratory of Agricultural Water Resources, Center for Agricultural Resources Research, Institute of Genetic and Developmental Biology, The Chinese Academy of Sciences, 286 Huaizhong Road, Shijiazhuang, 050021 Hebei, China;

    School of Environment, Natural Resources and Geography, Bangor University, Bangor LL57 2UW, U.K.;

    College of Resources and Environmental Sciences, China Agriculture University, Beijing 100193, China;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);美国《生物学医学文摘》(MEDLINE);美国《化学文摘》(CA);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
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  • 入库时间 2022-08-17 13:59:20

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