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Insights into the biodegradation of weathered hydrocarbons in contaminated soils by bioaugmentation and nutrient stimulation

机译:通过生物强化和养分刺激对风化烃在污染土壤中的生物降解的认识

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摘要

The potential for biotransformation of weathered hydrocarbon residues in soils collected from two commercial oil refinery sites (Soil A and B) was studied in microcosm experiments. Soil A has previously been subjected to on-site bioremediation and it was believed that no further degradation was possible while soil B has not been subjected to any treatment. A number of amendment strategies including bioaugmentation with hydrocarbon degrader, biostimulation with nutrients and soil grinding, were applied to the microcosms as putative biodegradation improvement strategies. The hydrocarbon concentrations in each amendment group were monitored throughout 112 days incubation. Microcosms treated with biostimulation (BS) and biostimulation/bioaugmentation (BS + BA) showed the most significant reductions in the aliphatic and aromatic hydrocarbon fractions. However, soil grinding was shown to reduce the effectiveness of a nutrient treatment on the extent of biotransformation by up to 25% and 20% for the aliphatic and aromatic hydrocarbon fractions, respectively. This is likely due to the disruption to the indigenous microbial community in the soil caused by grinding. Further, ecotoxicological responses (mustard seed germination and Microtox assays) showed that a reduction of total petroleum hydrocarbon (TPH) concentration in soil was not directly correlable to reduction in toxicity; thus monitoring TPH alone is not sufficient for assessing the environmental risk of a contaminated site after remediation.
机译:在微观实验中研究了从两个商业炼油厂站点(土壤A和B)收集的土壤中风化烃残留物生物转化的潜力。先前已经对土壤A进行了现场生物修复,并且认为对土壤B进行任何处理都无法进一步降解。许多修正策略,包括用烃降解剂进行生物强化,用养分进行生物刺激和土壤研磨,都被认为是改善生物降解的策略。在整个112天的温育过程中监测每个修正组中的烃浓度。经生物刺激(BS)和生物刺激/生物强化(BS + BA)处理的缩影显示出脂族和芳族烃馏分的减少幅度最大。但是,对于脂肪族和芳香族烃馏分,土壤研磨显示出在生物转化程度上降低了养分处理的效率,分别降低了25%和20%。这很可能是由于研磨导致土壤中土著微生物群落的破坏。此外,生态毒理反应(芥菜种子发芽和Microtox分析)表明,土壤中总石油烃(TPH)浓度的降低与毒性的降低没有直接关系;因此,仅监测TPH不足以评估修复后污染场地的环境风险。

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