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Development of bioreactors for comparative study of natural attenuation, biostimulation, and bioaugmentation of petroleum-hydrocarbon contaminated soil

机译:开发用于比较研究石油-烃污染土壤的自然衰减,生物刺激和生物强化的生物反应器

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Bioremediation of soil and groundwater sites contaminated by petroleum hydrocarbons is known as a technically viable, cost-effective, and environmentally sustainable technology. The purpose of this study is to investigate laboratory-scale bioremediation of petroleum-hydrocarbon contaminated soil through development of eight bioreactors, two bioreactors for each bioremediation mode. The modes were: (1) natural attenuation (NA); (2) biostimulation (BS) with oxygen and nutrients; (3) bioaugmentation (BA) with hydrocarbon degrading isolates; (4) a combination of biostimulation and bioaugmentation (BS BA). Total petroleum hydrocarbons (TPH) mass balance over the bioreactors showed about 2% of initial 20,000 mg kg-soil(-1) TPH was removed by advection due to synthetic groundwater which was flowing through the soil, and the rest of decrease in TPH was caused by biodegradation. The BS-BA mode showed the highest TPH biodegradation percentage (89.7 +/- 0.3%) compared to the NA (51.4 +/- 0.6%), BS (81.9 +/- 0.3%) and BA (62.9 +/- 0.5%) modes. Furthermore, an increase in microbial population was another evidence of TPH biodegradation by microorganism. Reaction rate data from each bioremediation mode were fitted with a first-order reaction rate model. The Monod kinetic constants including maximum specific growth rate of microorganisms (mu(max)) and substrate concentration at half-velocity constant (K-s) were estimated for each bioremediation modes. (C) 2017 Elsevier B.V. All rights reserved.
机译:对石油和碳氢化合物污染的土壤和地下水位进行生物修复是一种技术上可行,具有成本效益且对环境可持续的技术。这项研究的目的是通过开发八个生物反应器来研究实验室规模的石油-烃污染土壤的生物修复,每种生物修复模式都使用两个生物反应器。这些模式是:(1)自然衰减(NA); (2)用氧气和营养物质进行生物刺激(BS); (3)具有烃降解分离物的生物强化(BA); (4)生物刺激和生物增强相结合(BS BA)。生物反应器上的总石油烃(TPH)质量平衡表明,由于合成地下水流经土壤,平流除去了最初20,000 mg kg-土(-1)TPH中的约2%,其余的TPH下降为由生物降解引起。与NA(51.4 +/- 0.6%),BS(81.9 +/- 0.3%)和BA(62.9 +/- 0.5%)相比,BS-BA模式显示出最高的TPH生物降解率(89.7 +/- 0.3%) )模式。此外,微生物种群的增加是微生物对TPH进行生物降解的另一个证据。将来自每个生物修复模式的反应速率数据与一阶反应速率模型进行拟合。针对每种生物修复模式,估计了Monod动力学常数,包括微生物的最大比生长速率(mu(max))和半速度常数(K-s)下的底物浓度。 (C)2017 Elsevier B.V.保留所有权利。

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