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Degradation of tetrachloroethylene and trichloroethylene under thermal remediation conditions.

机译:在热修复条件下降解四氯乙烯和三氯乙烯。

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Thermal remediation involves heating subsurface environments and collecting fluids in order to recover contaminants such as tetrachloroethylene (PCE) and trichloroethylene (TCE). While increasing subsurface temperature can lead to changes in the distribution of contaminants between the solid, liquid, and gas phases, there is also an increased potential for PCE and TCE to degrade. This work was performed to determine the rate of PCE and TCE degradation and products formed in laboratory-scale experiments designed to simulate thermal remediation conditions.; The conditions during transport of gas-phase TCE were simulated using flow-through experiments in the temperature range from 60 to 800°C. Degradation of TCE was not evident at temperatures of less than 240°C; however, chloroacetic acids, which comprised less than 0.1% of the influent TCE on a carbon basis, were detected. At temperatures greater than 300°C, TCE readily degraded where the identities of the degradation products were a function of oxygen and water content. With oxygen present, TCE degraded to form CO, phosgene, CO2 with minor amounts of hexachloroethane, PCE, and carbon tetrachloride. Increasing the amount of water vapor was found to decrease the amount of TCE degraded. Vapor recovery systems used during thermal treatments are anticipated to capture these TCE degradation products. However, the amount of missing carbon (∼17%) in experiments completed at 800°C makes the prospect of recovering all TCE degradation products doubtful.; Experiments were conducted using hermetically sealed ampules to simulate heating dissolved phase PCE and TCE over periods of up to 75 days. At 120°C, the first-order TCE degradation half-life was 330 days and the degradation products included CO and CO2, glycolate, formate, and chloride. The rate of TCE disappearance was increased with the addition of 1% (wt.) goethite, which suggests that the presence of iron bearing soil minerals can increase rates of TCE degradation during thermal treatment. In contaminated field samples, TCE was found to degrade to form cis-1,2-dichloroethylene at 95°C coincident with the formation of hydrogen gas. Degradation of PCE was not evident in field samples or in deionized water and is not expected to degrade during thermal remediation at temperatures below 95°C.
机译:热修复涉及加热地下环境并收集流体,以回收污染物,例如四氯乙烯(PCE)和三氯乙烯(TCE)。虽然增加地下温度会导致固相,液相和气相之间污染物分布的变化,但PCE和TCE降解的可能性也增加了。进行这项工作是为了确定PCE和TCE降解的速率以及在实验室规模的实验中形成的产物,这些实验旨在模拟热修复条件。使用流通实验在60至800°C的温度范围内模拟了气相三氯乙烯的运输过程中的条件。在低于240°C的温度下,三氯乙烯的降解不明显。但是,检测到的氯乙酸占进水三氯乙烯的碳含量不到0.1%。在高于300°C的温度下,TCE易于降解,而降解产物的特性是氧和水含量的函数。在存在氧气的情况下,TCE降解以形成CO,光气,CO2和少量的六氯乙烷,PCE和四氯化碳。发现增加水蒸气的量减少了降解的TCE的量。预计在热处理过程中使用的蒸汽回收系统将捕获这些TCE降解产物。但是,在800°C下完成的实验中,碳的丢失量(约17%)使得回收所有TCE降解产物的前景令人怀疑。使用密封的安瓿瓶进行实验,以模拟长达75天的加热溶解相PCE和TCE。在120°C下,一阶TCE降解半衰期为330天,降解产物包括CO和CO2,乙醇酸,甲酸和氯。加入1%(wt。)针铁矿,TCE消失的速率增加了,这表明含铁土壤矿物的存在可以提高热处理过程中TCE的降解速率。在受污染的野外样品中,发现TCE在95°C降解,形成顺式1,2-二氯乙烯,同时形成氢气。在野外样品或去离子水中,PCE的降解不明显,并且在低于95°C的温度下进行热修复时,PCE不会降解。

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