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Effects of Road Salts on Heavy Metal Mobility in Two Eastern Washington Soils

机译:道路盐分对华盛顿州东部两种土壤中重金属迁移率的影响

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Heavy metals deposited on road surfaces and transferred to roadside environments by rainfall and snowmelt runoff can have serious impacts on receiving ecosystems. Infiltration is an effective best management practice for controlling metal contamination in runoff, although metals retention within infiltration facilities depends on a number of factors, including metal species, soil characteristics, and influent water quality concentrations. In cold climates, deicing compounds have been shown to mobilize heavy metals putting receiving waters at risk. This study ascertains the effects of two widely used road salts NaCl and MgCl2 on heavy metal mobility in two eastern Washington soils. Infiltration experiments were conducted using a basic soil, exhibiting a soil pH of 8.3, taken from a highway infiltration pond site in Spokane Washington and an acidic soil, exhibiting a soil pH of 5.9, taken from an infiltration pond site in Richland Washington. Three concentrations of each salt were percolated through both soils using continuous flow soil columns. Leachate samples were collected and analyzed for dissolved metals, organic matter, and pH. Experiments were also performed without salt and used as controls. Results indicate that metal mobilization can occur by a number of mechanisms including cation exchange, chloride complex formation, and colloid dispersion release of organic matter and/or clay that can complex metal species. Sodium chloride resulted in the largest release of copper and lead via indirect mobilization of organic matter. The magnesium salt had less of an effect on lead and copper but had a much greater effect on the mobilization of cadmium. Releases of metals during or immediately following salt application produced concentrations that ranged from 50% to 1000% greater than the concentrations released from the control experiments.
机译:沉积在路面上的重金属会由于降雨和融雪径流而转移到路边环境,会对接收生态系统产生严重影响。渗透是控制径流中金属污染的有效的最佳管理方法,尽管渗透设施中的金属滞留取决于许多因素,包括金属种类,土壤特性和进水水质浓度。在寒冷的气候中,除冰化合物已被证明能动员重金属,使接收水的风险增大。这项研究确定了两种广泛使用的道路盐NaCl和MgCl2对华盛顿州东部两种土壤中重金属迁移率的影响。使用从Spokane Washington的公路渗透池场地获取的pH值为8.3的碱性土壤和从Richland Washington的渗透池场地获取的pH值为5.9的酸性土壤进行渗透实验。使用连续流动的土壤柱,每种盐的三种浓度都渗透到两种土壤中。收集渗滤液样品并分析其溶解的金属,有机物和pH。还进行了无盐实验并用作对照。结果表明,金属动员可以通过多种机理发生,包括阳离子交换,氯化物络合物的形成以及有机物和/或粘土的胶体分散体的释放,这些物质可以使金属种类复杂化。氯化钠通过间接转移有机物导致铜和铅的最大释放。镁盐对铅和铜的影响较小,但对镉的迁移影响较大。在施用盐期间或之后立即释放的金属,其浓度比对照实验所释放的浓度高50%至1000%。

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