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Case Study Performance of gully control measures in foothills of lower Shiwaliks

机译:下希瓦利克山麓丘陵沟壑治理措施的案例研究

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Gully erosion is most prevalent type of water erosion which dissects the fields, impedes tillage operations, damages agricultual, residential and recreational land, hinders ground water recharge, causes environmental pollution, creats safety hazards and above all contributes to downstream sedimentation resulting in siltation of dams and reservoirs. Sediment production from gullies has been reported to be at the tune of 147 per cent of that produced by inter-rill erosion (Grissinger and Merphy 1989; Poesen 1996), On marginal farmland gully erosion is major source of soil and associated nitrogen and phosphorous losses (Sharpley et al. 1996) and thus reduces the crop yields significantly. Severe gully erosion is attributed to high soil erodibility, steep and long slopes and sparse vegetation cover. Various factors controlling gully growth are catchment characteristics viz, area (Burkard and Kostaschuk 1997), slope steepness (Kukal et al. 1991), slope shape (Meyer and Martinez-Casasnovas 1999), gully dimension parameters, surface runoff, precipitation, soil moisture and piping (Stocking 1980). Also land abandonment and afforestation can increase gully erosion.
机译:沟壑侵蚀是最普遍的水蚀类型,它会破坏田野,阻碍耕作,破坏农业,住宅和休闲用地,阻碍地下水补给,造成环境污染,造成安全隐患,并且首先造成下游沉积,导致大坝淤积和水库。据报导,沟壑的沉积物产量仅占小河间侵蚀的147%(Grissinger and Merphy 1989; Poesen 1996)。在边际农田,沟壑侵蚀是土壤的主要来源,并伴随着氮和磷的流失(Sharpley et al。1996),因此大大降低了作物产量。严重的沟壑侵蚀归因于较高的土壤易蚀性,陡峭而长的坡度和稀疏的植被。控制沟壑生长的各种因素是流域特征,即流域特征,面积(Burkard和Kostaschuk 1997),坡度陡度(Kukal等人1991),坡度形状(Meyer和Martinez-Casasnovas 1999),沟壑尺度参数,地表径流,降水,土壤湿度和管道(Stocking 1980)。土地被遗弃和造林也会加剧沟壑侵蚀。

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