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Chemical Treatment of a Contaminated Aquifer: Impact of Different Oxidants and Reductants on CAHs and Post-Chemical Biodegradation

机译:污染含水层的化学处理:不同氧化剂和还原剂对CAHS和化学生物降解的影响

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Here we report on a lab-scale experiment where a homogenized contaminated aquifer slurry from a Flemish site was subjected to three reducing (nano-, micro-, and granular zero-valent iron) and 3 oxidizing agents (permanganate, cold and activated persulphate), each in three different concentrations. Over time the evolution of the contaminants and breakdown products (PCE, TCE, cDCE, vinylchloride, dichloromethane, 1,2-dichloroethane, toluene, ethylbenzene, ethene, ethane, acetylene) was followed, and samples for characterisation of the soil matrix have been taken. The results showed that, for the tested aquifer, chemical reduction had a much higher impact on the chlorinated contaminant concentration than chemical oxidants. Even repeated applications of the chemical oxidants did not lead to a total removal of the pollution, while a single application of zerovalent iron did remove most of the chlorinated contaminants. The very high matrix demand that was observed may be part of the explanation here. This emphasizes the importance of considering the redox state of the aquifer during the selection of the chemical reagent. BTEX-compounds were not degraded by chemical reduction as expected. After three months of incubation, when the chemical oxidants were no longer reactive, lactate was added to evaluate the remaining biodegradation potential of soils after chemical treatments. In the original aquifer material, without chemical treatment, an anaerobic biodegradation potential for a number of the chlorinated compounds was observed. The chemical treatments, however, did impact the biodegradation in most of the chemical oxidation cases. While in the test conditions with the lowest oxidant concentration biodegradation activity was observed after a lag phase, no activity was seen in the test conditions where higher doses were applied. The highest negative impact was observed with permanganate. The redox potential seems to be a crucial parameter. In the presence of chemical reductants, elevated concentrations of vinyl chloride (only a major degradation product of biodegradation and not of chemical reduction) suggests simultaneous occurrence of biodegradation and chemical reduction.
机译:在这里,我们报告了一种实验室规模实验,其中来自佛兰芒位点的均质污染的含水层浆料进行三次还原(纳米,微型和颗粒零价铁)和3个氧化剂(高锰酸盐,冷和活化的过硫酸盐) ,每次三种不同的浓度。随着时间的推移,污染物和击穿产物的演变(PCE,TCE,CDCE,亚乙氯化物,二氯甲烷,1,2-二氯乙烷,甲苯,乙基苯,乙烯,乙烷,乙炔),并呈现土壤基质的表征样品采取。结果表明,对于测试的含水层,化学还原对氯化污染物浓度的影响大得多,而不是化学氧化剂。甚至反复应用化学氧化剂的应用并没有导致总去除污染,而单价铁的单一施用成分去除大部分氯化污染物。观察到的非常高的矩阵需求可能是这里解释的一部分。这强调了在选择化学试剂期间考虑含水层的氧化还原状态的重要性。 BTEX-化合物没有通过预期的化学还原而降解。孵育三个月后,当化学氧化剂不再反应时,加入乳酸,以评估化学处理后土壤的剩余生物降解潜力。在原始含水层材料中,没有化学处理,观察到许多氯化化合物的厌氧生物降解电位。然而,化学处理确实影响了大多数化学氧化病例中的生物降解。虽然在滞后阶段后观察到具有最低氧化浓度生物降解活性的试验条件,但在施加较高剂量的试验条件下没有观察到任何活性。用高锰酸盐观察到最大的负面影响。氧化还原潜力似乎是一个关键参数。在化学化还原剂存在下,升高的氯乙烯浓度(只有生物降解的主要降解产物,也不是化学降低)表明了生物降解和化学降低的同时发生。

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