首页> 外文期刊>The Science of the Total Environment >Remediation of chlorinated ethenes in fractured sandstone by natural and enhanced biotic and abiotic processes: A crushed rock microcosm study
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Remediation of chlorinated ethenes in fractured sandstone by natural and enhanced biotic and abiotic processes: A crushed rock microcosm study

机译:自然和增强的生物和非生物过程修复裂缝性砂岩中的氯乙烯的研究:碎石微观研究

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Biostimulation was identified as a potential technology to treat a fractured sandstone aquifer contaminated with trichloroethene (TCE) andcis-1,2-dichloroethene (cis-DCE). Most of the mass of TCE andcis-DCE resides within the rock matrix and strategies to restore groundwater to pre-existing conditions are severely limited by back diffusion. A microcosm study using crushed rock and groundwater from the site was performed to assess biostimulation and natural attenuation. Lactate, hydrogen release compound® (HRC), and emulsified vegetable oil (EVO) significantly increased the rate of TCE reduction tocis-DCE. Lactate also stimulated dechlorination ofcis-DCE to vinyl chloride (VC) and ethene, suggesting the presence of indigenousDehalococcoides. Illumina sequencing and qPCR analyses suggest that reductive dechlorination of TCE tocis-DCE is mediated byGeobacterspp. whileDehalococcoidesspp. perform reduction ofcis-DCE to VC and ethene. The rate of VC reduction to ethene was much slower than the reduction of TCE tocis-DCE andcis-DCE to VC, indicating the indigenousDehalococcoidesperform the final step co-metabolically. This was confirmed in enrichment cultures fed with only VC. Consequently, biostimulation may create an elevated risk due to transient accumulation of VC. Abiotic transformation of TCE andcis-DCE was observed based on accumulation of14C-labeled products from14C-TCE and14C-cis-DCE, as well as enrichment in δ13C-cis-DCE in the absence of reductive dechlorination. Based on accumulation rates for14C-products in unamended microcosms, pseudo-first-order rates for abiotic transformation were 0.038 yr−1for TCE and 0.044 yr−1forcis-DCE. These rates within the rock matrix may be sufficient to support natural attenuation in this diffusion controlled system.
机译:生物刺激被认为是处理被三氯乙烯(TCE)和顺式1,2-二氯乙烯(cis-DCE)污染的破裂砂岩含水层的潜在技术。 TCE和顺式DCE的大部分质量都位于岩石基质中,而将地下水恢复到既有条件的策略受到反向扩散的严重限制。使用现场的碎石和地下水进行了缩影研究,以评估生物刺激和自然衰减。乳酸,氢释放化合物(HRC)和乳化植物油(EVO)显着提高了TCE还原为顺式DCE的速率。乳酸还刺激顺式-DCE脱氯成氯乙烯(VC)和乙烯,表明存在本土的Dehalococcoides。 Illumina测序和qPCR分析表明,TCE tocis-DCE的还原性脱氯是由Geobacterspp介导的。而Dehalococcoidesdespp。进行顺式-DCE还原为VC和乙烯。 VC还原为乙烯的速率比TCE tocis-DCE和cis-DCE还原为VC的速率要慢得多,这表明本地的Dehalococcoides通过代谢共同完成了最后一步。仅用VC喂养的富集培养证实了这一点。因此,由于VC的短暂积累,生物刺激可能会增加风险。基于14C-TCE和14C-cis-DCE中14C标记产物的积累以及在不存在还原性脱氯的情况下δ13C-cis-DCE中的富集,观察到TCE和顺式DCE的非生物转化。根据未经修改的微观世界中14 C产品的积累速率,非生物转化的拟一级反应速率为TCE为0.038 yr-1,顺式DCE为0.044 yr-1。岩石矩阵内的这些速率可能足以支持该扩散控制系统中的自然衰减。

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