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Managing erosion and water quality in agricultural watersheds by small detention ponds.

机译:通过小型滞留池管理农业流域的侵蚀和水质。

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摘要

Terrace-contouring systems with on-site water detention cannot be installed in areas of complex topography, small parceling and multi-blade moldboard plow use. However, field borders at the downslope end may be raised at the deepest part where runoff overtops to create detention ponds, which can be drained by subsurface tile outlets and act similar to terrace-contouring systems. Four of such detention ponds were monitored over 8 years. Monitored effects included the prevention of linear erosion down slope, the sediment trapping from upslope, the enrichment of major nutrients in the trapped and delivered sediments, the amount of runoff retained temporarily, the amount of runoff reduced by infiltration, the decrease in peak runoff rate and the decrease in peak concentrations of agrochemicals due to the mixing of different volumes of water within the detention ponds. The detention ponds had a volume of 30-260 m3 ha-1 and trapped 54-85% of the incoming sediment, which was insignificantly to slightly depleted (5-25%) in organic carbon, phosphorus, nitrogen and clay as compared to the eroding topsoil, while the delivered sediment was strongly enriched (+70-270%) but part of this enrichment already resulted from the enrichment of soil loss. The detention ponds temporarily stored 200-500 m3 of runoff. A failure was never experienced. Due to the siltation of the pond bottom, the short filled time (1-5 days) and the small water covered area, infiltration and evaporation reduced runoff by less than 10% for large events. Peak runoff during heavy rains was lowered by a factor of three. Peak concentrations of agrochemicals (Terbutylazin) were lowered by a factor of two. The detention ponds created by raising the downslope field borders at the pour point efficiently reduced adverse erosion effects downslope the eroding site. They are cheap and can easily be created with on-farm machinery. Their efficiency is improved where they are combined with an on-site erosion control like mulch tillage because sediment and runoff input are reduced. Ponds had to be dredged only after the first year when on-site erosion control was not fully effective..
机译:带有现场保水功能的露台轮廓系统不能安装在地形复杂,小包裹和使用多刃刮土机犁的地区。但是,下坡末端的田野边界可能会在径流顶部形成的最深处升高,从而形成滞留池,该滞留池可以被地下瓷砖出口排干,其作用类似于露台轮廓系统。在8年中对四个此类滞留池进行了监测。监测到的影响包括防止线性侵蚀下坡,上坡沉积物的截留,所捕获和输送的沉积物中主要养分的富集,临时保留的径流量,渗透减少的径流量,峰值径流量降低以及由于滞留池中混合了不同体积的水而导致的农药峰值浓度降低。滞留池的体积为30-260 m3 ha-1,捕获的进入沉积物占54-85%,相比之下,有机碳,磷,氮和黏土的微不足道(5-25%)略有减少。侵蚀的表层土壤,虽然输送的沉积物被强烈富集(+ 70-270%),但是这种富集的一部分已经由土壤流失的富集引起。滞留池暂时储存了200-500立方米的径流。从未经历过失败。由于池塘底部的淤积,较短的填充时间(1-5天)和较小的水覆盖面积,渗透和蒸发作用,对于大型活动而言,径流减少了不到10%。大雨期间的高峰径流降低了三倍。农用化学品(Terbutylazin)的峰值浓度降低了两倍。通过在倾泻点升高下坡场边界而创建的滞留池有效地减少了对侵蚀点下坡的不利侵蚀作用。它们很便宜,并且可以通过农场机械轻松创建。将其与覆盖耕作等现场侵蚀控制相结合可提高其效率,因为可减少沉积物和径流的输入。仅在现场侵蚀控制不能完全有效的第一年之后才需要挖池塘。

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