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Arsenic pathways in leachate plumes at five landfill sites in central Massachusetts.

机译:马萨诸塞州中部五个垃圾掩埋场渗滤液羽流中的砷途径。

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Arsenic concentrations in soil and groundwater have recently become an issue of global importance. Central Massachusetts is a geologic zone known to have elevated natural arsenic concentrations in the soil and bedrock. Landfills within Central Massachusetts locally inadvertently mobilize arsenic in ground water downgradient from landfills.; This thesis critically evaluates database methodologies and designs to recommend sound management tools for environmental data management at landfills. Spacial, temporal, and geochemical arsenic trend analyses were utilized to determine possible arsenic sources and migration pathways. Several distinct observable trends with regards to arsenic, iron, manganese, and sulfate concentrations were seen repeat ably indicating close interaction between sulfate, iron, and arsenic at distinct reducing conditions. Dissolution of ferric oxyhydroxide coatings liberate arsenic in reducing conditions initiated by microbial degradation of organic constituents within the migrating leachate plume.
机译:土壤和地下水中的砷浓度最近已成为具有全球重要性的问题。马萨诸塞州中部是一个地质区,已知其土壤和基岩中的天然砷浓度升高。马萨诸塞州中部地区的垃圾填埋场在不经意间将砷从地下垃圾中转移到地下水中。本文对数据库的方法论进行了严格的评估,并对其设计进行了推荐,以推荐用于垃圾填埋场环境数据管理的完善的管理工具。利用空间,时间和地球化学砷趋势分析来确定可能的砷来源和迁移途径。关于砷,铁,锰和硫酸盐浓度的几个不同的可观察趋势被重复观察到,表明在不同的还原条件下硫酸盐,铁和砷之间的紧密相互作用。羟基氧化铁涂层的溶解在还原条件下释放了砷,该条件是由于迁移的沥出液羽流中有机成分的微生物降解所致。

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