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Enhanced in situ bioremediation of chlorinated solvents

机译:增强氯溶剂的原位生物修复

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Anaerobic enhancement of in Situ bioremediation of a shallow, confined, silty sand aquifer has resulted in a substantial biodegradation of a dissolved tetrachloroethene (PCE) plume at an abandoned metal finishing facility located within residential area in northern New Jersey. The injection of a proprietary time-release hydrogen compound rapidly converted ambient aquifer aerobic conditions to anaerobic. This enhancement effectively induced and facilitated the successive reductive dechlorination of PCE and daughter products. Field results confirmed this anaerobic biodegradation enhancement within the overburden aquifer resulted in substantial degradation of PCE and its daughter products in the underlying sandstone bedrock aquifer. The pre-injection dissolved PCE levels of 5 to 8 mg/1 at the source declined by 90 to 96% within 2 months of injection. Degradation rates of 96% to 100% were obtained for TCE and t-DCE, whereas the degradation rates of c-DCE were slower and smaller at 30 to 70%. The potential presence of residual product and larger adsorbed solvent mass in the source area resulted in seemingly smaller but faster PCE and TCE overall degradation rates in comparison to downgradient areas. The c-DCE mass degradation during the same period was apparently greater and faster near the source than in the downgradient area. Of interesting significance was the rapid degradation of VC, which was scarcely detected during the monitoring period. Carbon dioxide and methane levels increased by more than 10 fold indicative of VC degradation under both aerobic and anaerobic conditions. Local changes in the REDOX state and in oxygen levels coincided with preferential reduction of competing species (e.g., sulfate), and apparently facilitated the degradation of VC.
机译:厌氧性提高了浅层,密闭粉质砂质含水层的原位生物修复能力,导致新泽西州北部居民区内一个废弃的金属精加工设施中溶解的四氯乙烯(PCE)羽流大量生物降解。专有的缓释氢化合物的注入将含水层的有氧条件迅速转化为厌氧条件。这种增强有效地诱导并促进了PCE及其子产物的连续还原脱氯。现场结果证实,上覆含水层中的厌氧生物降解作用增强,导致下层砂岩基岩含水层中的PCE及其子产物大量降解。注射前2个月内,注射前的溶解PCE水平为5至8 mg / 1,下降了90至96%。 TCE和t-DCE的降解率达到96%至100%,而c-DCE的降解率则更低,在30%至70%时较小。与降级区域相比,源区域中可能存在残留产物和较大的吸附溶剂质量,从而导致PCE和TCE总体降解率似乎较小,但速度更快。显然,在同一时期,源附近的c-DCE质量下降比下降区域更大,并且更快。有趣的意义是VC的快速降解,在监测期间几乎未检测到。在有氧和厌氧条件下,二氧化碳和甲烷的含量增加了10倍以上,表明VC降解。 REDOX状态和氧水平的局部变化与竞争性物质(例如硫酸盐)的优先减少相吻合,并且显然促进了VC的降解。

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