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Nutrient loss pathways from grazed grasslands and the effects of decreasing inputs: experimental results for three soil types

机译:放牧草地的养分流失路径和投入减少的影响:三种土壤类型的实验结果

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Agriculture is a main contributor of diffuse emissions of N and P to the environment. For N the main loss pathways are NH3-volatilization, leaching to ground and surface water and N2(O) emissions. Currently, imposing restraints on farm inputs are used as policy tool to decrease N and P leaching to ground water and to surface water, and the same measure is suggested to combat emissions of N2O. The response, however, to these measures largely depends on the soil type. In this study nutrient flows of three dairy farms in The Netherlands with comparable intensity on sand, peat and clay soils were monitored for at least 2 years. The first aim was to provide quantitative data on current nutrient loss pathways. The second aim was to explore the responses in partitioning of the nutrient loss pathways when farm inputs were altered. Mean denitrification rates ranged from 103 kg N ha?1 year?1 for the sandy soil to 170 kg N ha?1 year?1 for the peat soil and leaching to surface water was about 73 kg N ha?1 year?1 for the sandy soil, 15 kg N ha?1 year?1 for the clay soil and 38 kg N ha?1 year?1 for the peat soil. For P, leaching to surface water ranged from 2 kg P ha?1 year?1 for the sandy site to 5 kg P ha?1 year?1 for the peat site. The sandy soil was most responsive to changes in N surpluses on leaching to surface water, followed by the peat soil and least responsive was the clay soil. For P, a similar sequence was found. This article demonstrates that similar reductions of N and P inputs result in different responses in N and P loss pathways for different soil types. These differences should be taken into account when evaluating measures to improve environmental performance of (dairy) farms.
机译:农业是氮和磷扩散排放到环境中的主要贡献者。对于N而言,主要的损失途径是NH 3挥发,淋溶至地下水和地表水以及N 2(O)排放。目前,对农业投入物施加限制是减少氮和磷向地下水和地表水中淋失的政策工具,并建议采取相同措施来减少N2O的排放。但是,对这些措施的反应很大程度上取决于土壤类型。在这项研究中,对荷兰三个奶牛场(在沙子,泥炭和黏土上具有类似强度)的养分流量进行了至少两年的监测。第一个目的是提供有关当前养分流失途径的定量数据。第二个目的是探索改变农场投入时营养流失路径分配的响应。平均反硝化率范围从沙土的103 kg N ha?1 年?1 到泥炭土和浸出的170 kg N ha?1 年?1 。沙质土壤的地表水大约为73 kg N ha?1 年?1 ,黏土为15 kg N ha?1 年?1 。 kg N ha?1 年?1 用于泥炭土。对于磷,淋溶到地表水的范围从沙地的2 kg P ha?1 年?1 到5 kg P ha?1 年?1 。泥炭站点。沙质土壤淋溶到地表水时对氮过剩的变化反应最快,其次是泥炭土,而对粘土的反应最少。对于P,发现了相似的序列。本文表明,氮和磷输入量的相似减少会导致不同土壤类型的氮和磷损失途径的响应不同。在评估改善(奶牛场)环境绩效的措施时,应考虑这些差异。

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