首页> 外文期刊>Journal of Enviromental Quality >Landfill Cover Soil, Soil Solution, and Vegetation Responses to Municipal Landfill Leachate Applications
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Landfill Cover Soil, Soil Solution, and Vegetation Responses to Municipal Landfill Leachate Applications

机译:垃圾填埋场覆盖土壤,土壤溶液和植被对市政垃圾渗滤液应用的响应

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摘要

Municipal solid waste landfill leachate must be removed and treated to maintain landfill cover integrity and to prevent contamination of surface and ground waters. From 2003 to 2007, we studied an onsite disposal system in Ottawa County, Michigan, where leachate was spray irrigated on the vegetated landfill cover. We established six 20-m-diameter circular experimental plots on the landfill; three were spray irrigated as part of the operational system, and three remained as untreated control plots. We quantified the effects of leachate application on soil properties, soil solution chemistry, vegetative growth, and estimated solute leaching. The leachate had high mean levels of electrical conductivity (0.6–0.7 S m–1), Cl (760–900 mg L–1), and NH4–N (290–390 mg L–1) but was low in metals and volatile organic compounds. High rates of leachate application in 2003 (32 cm) increased soil electrical conductivity and NO3–N leaching, so a sequential rotation of spray areas was implemented to limit total leachate application to <9.6 cm yr–1 per spray area. Concentrations of NO3–N and leaching losses remained higher on irrigated plots in subsequent years but were substantially reduced by spray area rotation. Leachate irrigation increased plant biomass but did not significantly affect soil metal concentrations, and plant metal concentrations remained within normal ranges. Rotating spray areas and timing irrigation to conform to seasonal capacities for evapotranspiration reduced the localized impacts of leachate application observed in 2003. Careful monitoring of undiluted leachate applications is required to avoid adverse impacts to vegetation or soils and elevated solute leaching losses.
机译:必须清除并处理市政固体垃圾填埋场渗滤液,以保持垃圾掩埋场的完整性并防止对地表水和地下水的污染。从2003年到2007年,我们研究了密歇根州渥太华县的现场处置系统,将渗滤液喷洒到植被覆盖的垃圾填埋场上。我们在垃圾填埋场上建立了六个直径20米的圆形实验区;作为操作系统的一部分,对其中的三处进行了喷灌,其余三处作为未处理的对照样地。我们量化了渗滤液施用对土壤性质,土壤溶液化学,营养生长和溶质淋溶的影响。渗滤液的平均电导率较高(0.6-0.7 S m-1),氯(760-900 mg L-1)和氨氮(290-390 mg L-1)低,但金属和挥发性低有机化合物。 2003年高渗滤液施用量(32厘米)提高了土壤电导率和NO3-N淋溶,因此,对喷施区域进行了连续轮换,以将总渗滤液施用量限制在每个喷洒区域<9.6 cm yr-1。在随后的几年中,灌溉区的NO3-N浓度和淋失损失仍然较高,但由于喷洒面积的旋转而大大降低了。渗滤液灌溉增加了植物的生物量,但并未显着影响土壤金属的浓度,植物金属的浓度仍保持在正常范围内。旋转喷雾区域和定时灌溉以适应季节性蒸散量,减少了2003年观察到的渗滤液施用的局部影响。需要仔细监测未稀释渗滤液的施用,以避免对植被或土壤的不利影响以及溶质淋溶损失的增加。

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