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Effectiveness of stimulating PCE reductive dechlorination: A step-wise approach

机译:刺激PCE还原脱氯的有效性:逐步方法

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Reductive dechlorination of tetrachloroethene (PCE) and its daughter products in aquifers is often hampered by Fe(Ⅲ) reducing conditions. Rigorous treatment to adjust the redox potential and stimulate dechlorination may be costly and potentially have negative effects on other aquifer functions. A step-wise experimental strategy was applied to investigate the effectiveness of various adjustment scenarios. Batch experiments with ascorbic acid (AA) and sodium lactate (SL) showed that 75 μmol electron equivalents per gram dry mass of aquifer material was required to reach a sufficiently low redox potential for the onset of PCE dechlorination. Similar effects of either AA or SL on the measured redox potential suggest electron donors are not specific However, the relative rates of Fe(Ⅲ) and sulphate reduction appeared to be specific to the electron donor applied. While redox potential stabilised around -450 mV after titration and sulphate was reduced to zero in both treatments, in the AA treatment a faster production of Fe~(2+) was observed with a final concentration of 0.46 mM compared to only 0.07 mM in the SL treatment In subsequent batch experiments with aquifer material that was pre-treated with AA or SL, PCE reductive dechlorination occurred within 30 days. Further stimulation tests with extra electron donor or inoculum revealed that adding electron donor can accelerate the initiation of PCE biodegradation. However, bioaugmentation with dechlorinating bacteria is required to achieve complete reductive dechlorination to ethene. The findings from step-wise approaches are relevant for improving the cost-effectiveness of the design and operation of in-situ bioremediation at initially unfavourable environmental conditions.
机译:Fe(Ⅲ)的还原条件常常阻碍了含水层中四氯乙烯(PCE)及其子产物的还原脱氯。严格的调节氧化还原电位和刺激脱氯的处理可能成本高昂,并可能对其他含水层功能产生负面影响。采用逐步实验策略来研究各种调整方案的有效性。用抗坏血酸(AA)和乳酸钠(SL)进行的分批实验表明,每克干物质含水层材料需要75μmol电子当量,才能使PCE脱氯反应达到足够低的氧化还原电位。 AA或SL对测得的氧化还原电势的相似影响表明电子给体不是特定的。但是,Fe(Ⅲ)和硫酸盐还原的相对速率似乎对所应用的电子给体是特定的。虽然在两种处理中滴定后氧化还原电势稳定在-450 mV附近,并且硫酸盐均降低为零,但在AA处理中,观察到Fe〜(2+)的生成更快,最终浓度为0.46 mM,而在最终浓度仅为0.07 mM。 SL处理在随后的使用AA或SL预处理的含水层材料的分批实验中,在30天内发生PCE还原脱氯。用额外的电子供体或接种物进行的进一步刺激试验表明,添加电子供体可以加速PCE生物降解的开始。然而,需要用脱氯细菌进行生物强化以实现完全还原性脱氯为乙烯。逐步方法的发现与提高在最初不利的环境条件下进行原位生物修复的设计和操作的成本效益有关。

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