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Chemical Degradation of Dichloroethylenes by Pyrite

机译:黄铁矿化学降解二氯乙烯

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Chlorinated ethylenes have been recognized for their environmental persistence and risk. Main initial environmental contaminants are tetrachloroethylene and trichloroethylene but dichloroethylenes persist as a by-product of them, because the dechlorination rate of dichloroethylenes is inferior to initial chemicals in general chemical degradation or bioremediation. They protract the absolute remediation of soil and groundwater. This paper describes the dechlorination ability of pyrite, which can degradate the dichloroethylenes at the grater than or equal to the rate of tetra- or tri- chlorothylenes. In our previous research, the chemical reductive ability of natural sulfide for trichloroethylene was clarified and the reaction process differs completely from that with transitional metals. As same as the reaction of trichloroethylene with sulfide, the dichloroethylenes are entirely dechlorinated and change into to non-contaminated hydrocarbone or sulfur compounds. These reaction products adsorb on hydrophobic pyrite surface in this system. The chemical dechlorination is caused by electron sourced from the dissolution of pyrite at normal temperature and pressure condition. The remediation is easy to proceed in the natural environment.
机译:氯化乙烯已被认可为其环境持久性和风险。主要初始环境污染物是四氯乙烯和三氯乙烯,但二氯乙烯作为它们的副产物持续存在,因为二氯乙烯的脱氯率差于一般化学降解或生物化的初始化学品。他们伸出了土壤和地下水的绝对修复。本文描述了黄铁矿的脱氯能力,其可以使刨叶的二氯乙烯降解而不是四分之一或三氟化液的速率。在我们以前的研究中,澄清了三氯乙烯的天然硫化物的化学还原能力,并且反应过程与过渡金属完全不同。与三氯乙烯与硫化物的反应相同,二氯乙烯完全脱氯并变为非污染的烃或硫化合物。这些反应产物在该系统中吸附疏水性硫铁矿表面。化学脱氯是由普通温度和压力条件下溶解硫铁矿的电子引起的。修复很容易在自然环境中进行。

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