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Residual soil nitrate content and profitability of five cropping systems in northwest Iowa

机译:爱荷华州西北部五种耕作制度的土壤硝态氮残留量和获利能力

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摘要

Many communities in the Midwestern United States obtain their drinking water from shallow alluvial wells that are vulnerable to contamination by NO3-N from the surrounding agricultural landscape. The objective of this research was to assess cropping systems with the potential to produce a reasonable return for farmers while simultaneously reducing the risk of NO3-N movement into these shallow aquifers. From 2009 to 2013 we conducted a field experiment in northwest Iowa in which we evaluated five cropping systems for residual (late fall) soil NO3-N content and profitability. Soil samples were taken annually from the top 30 cm of the soil profile in June and August, and from the top 180 cm in November (late fall). The November samples were divided into 30 cm increments for analysis. Average residual NO3-N content in the top 180 cm of the soil profile following the 2010 to 2013 cropping years was 134 kg ha-1 for continuous maize (Zea mays L.) with a cereal rye (Secale cereale L.) cover crop, 18 kg ha-1 for perennial grass, 60 kg ha-1 for a three year oat (Avena sativa L.)-alfalfa (Medicago sativa L.)-maize rotation, 85 kg ha-1 for a two year oat/red clover (Trifolium pratense L.)-maize rotation, and 90 kg ha-1 for a three year soybean (Glycine max (L.) Merr.)-winter wheat (Triticum aestivum L.)-maize rotation. However, residual NO3-N in the 90 to 180 cm increment of the soil profile was not significantly higher in the oat-alfalfa-maize cropping system than the perennial grass system. For 2010 to 2013, average profit ($ ha-1 yr-1) was 531 for continuous corn, 347 for soybean-winter wheat-maize, 264 for oat-alfalfa-maize, 140 for oat/red clover-maize, and -384 (loss) for perennial grass. Considering both residual soil NO3-N and profitability data, the oat-alfalfa-maize rotation performed the best in this setting. However, given current economic pressures widespread adoption is likely to require changes in public policy.
机译:美国中西部的许多社区都是从浅冲积井中获取饮用水的,这些冲积井很容易受到周围农业景观中NO3-N的污染。这项研究的目的是评估能够为农民带来合理回报的种植系统,同时降低NO3-N运入这些浅层含水层的风险。从2009年到2013年,我们在爱荷华州西北部进行了田间试验,其中评估了五种耕作系统的残留(落秋)土壤NO3-N含量和获利能力。每年6月和8月从土壤剖面的顶部30厘米处采集土壤样品,11月(秋末)从180厘米的顶部采集土壤样品。将11月的样品分成30 cm增量进行分析。在连续种植玉米(Seaale)的玉米(Zea mays L.)之后,2010年至2013年的种植年之后,土壤剖面顶部180 cm的平均残留NO3-N含量为134 kg ha -1 谷类作物,多年生禾草18 kg ha -1 ,三年燕麦(Avena sativa L。)-苜蓿(Medicago)60 kg ha -1 玉米轮作,85 kg ha -1 两年的燕麦/红三叶草(Trifolium pratense L.)玉米轮作和90 kg ha -1 对于三年大豆(Glycine max(L.)Merr。)-冬小麦(Triticum aestivum L。)-玉米轮作。但是,在燕麦-苜蓿-玉米种植系统中,土壤剖面中90至180厘米增量处的残留NO3-N并不显着高于多年生禾草系统。从2010年到2013年,连续玉米的平均利润($ ha -1 yr -1 )为连续玉米,大豆-冬小麦-玉米347,燕麦-紫花苜蓿264 -玉米,燕麦/红三叶草玉米为140,多年生草为-384(损失)。考虑到残留的土壤NO3-N和获利能力数据,燕麦-苜蓿-玉米轮作在这种情况下表现最佳。但是,鉴于当前的经济压力,广泛采用可能需要改变公共政策。

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