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首页> 外文期刊>Environmental Pollution >The impact of lead co-contamination on ecotoxicity and the bacterial community during the bioremediation of total petroleum hydrocarbon-contaminated soils
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The impact of lead co-contamination on ecotoxicity and the bacterial community during the bioremediation of total petroleum hydrocarbon-contaminated soils

机译:在全部石油烃污染土壤的生物修复过程中,铅共污染对生态毒性和细菌群落的影响

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The continued increase in the global demand for oil, which reached 4,488 Mtoe in 2018, leads to large quantities of petroleum products entering the environment posing serious risks to natural ecosystems if left untreated. In this study, we evaluated the impact of co-contamination with lead on the efficacy of two bioremediation processes, natural attenuation and biostimulation of Total Petroleum Hydrocarbons (TPH) as well as the associated toxicity and the changes in the microbial community in contaminated soils. The biostimulated treatment resulted in 96% and 84% reduction in TPH concentration in a single and a co-contamination scenario, respectively, over 28 weeks of a mesocosm study. This reduction was significantly more in comparison to natural attenuation in a single and a co-contamination scenario, which was 56% and 59% respectively. In contrast, a significantly greater reduction in the associated toxicity of in soils undergoing natural attenuation was evident compared with soils undergoing bio-stimulation despite the lower TPH degradation when bioassays were applied. The earthworm toxicity test showed a decrease of 72% in the naturally attenuated toxicity versus only 62% in the biostimulated treatment of a single contamination scenario. In a co-contamination scenario, toxicity decreased only 30% and 8% after natural attenuation and biostimulation treatments, respectively. 16s rDNA sequence analysis was used to assess the impact of both the co-contamination and the bioremediation treatment. NGS data revealed major bacterial domination by Nocardioides spp., which reached 40% in week 20 of the natural attenuation treatment. In the biostimulated soil samples, more than 50% of the bacterial community was dominated by Alcanivorax spp. in week 12. The presence of Pb in the natural attenuation treatment resulted in an increased abundance of a few Pb-resistant genera such as Sphingopyxis spp. and Thermomonas spp in addition to Nocardioides spp. In contrast, Pb co-contamination completely shifted the bacterial pattern in the stimulated treatment with Pseudomonas spp. comprising approximately 45% of the bacterial profile in week 12. This study confirms the effectiveness of biostimulation over natural attenuation in remediating TPH and TPH-Pb contaminated soils. In addition, the presence of cocontaminants (e.g. Pb) results in serious impacts on the efficacy of bioremediation of TPH in contaminated soils, which must be considered prior to designing any bioremediation strategy. (C) 2019 Elsevier Ltd. All rights reserved.
机译:全球石油需求的持续增长(2018年达到4,488 Mtoe)导致大量石油产品进入环境,如果不加以处理将对自然生态系统构成严重风险。在这项研究中,我们评估了铅共污染对两种生物修复过程(总石油烃(TPH)的自然衰减和生物刺激)以及相关毒性和受污染土壤中微生物群落变化的影响。经过生物刺激的治疗,在中膜研究的28周内,单一和共污染情况下的TPH浓度分别降低了96%和84%。与单一污染和共污染情况下的自然衰减分别为56%和59%相比,这种减少要多得多。相比之下,尽管进行生物测定时TPH降低,但与经历生物刺激的土壤相比,经过自然衰减的土壤的相关毒性明显降低了很多。 toxicity毒性试验表明,自然减毒毒性降低了72%,而单一污染情景的生物刺激处理仅降低了62%。在共同污染的情况下,自然减毒和生物刺激处理后,毒性仅分别降低了30%和8%。 16s rDNA序列分析用于评估共污染和生物修复处理的影响。 NGS数据显示,诺卡氏菌对细菌的主要控制作用在自然减毒处理的第20周达到40%。在经过生物刺激的土壤样品中,超过50%的细菌群落被Alcanivorax spp所控制。在第12周时,自然减毒处理中Pb的存在导致一些耐Pb属(例如Sphingopyxis spp)的丰度增加。除诺卡氏菌外,还有嗜热单胞菌。相反,在用假单胞菌属物种刺激处理后,Pb共污染完全改变了细菌模式。在第12周中约占细菌分布的45%。这项研究证实了生物刺激在修复TPH和TPH-Pb污染土壤方面优于自然衰减。此外,辅污染物(例如铅)的存在会严重影响TPH在受污染土壤中的生物修复效果,因此在设计任何生物修复策略之前必须考虑这一问题。 (C)2019 Elsevier Ltd.保留所有权利。

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