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Arsenic bioavailability in soils before and after soil washing: the use of Escherichia coli whole-cell bioreporters

机译:土壤洗涤前后土壤中的砷生物利用度:使用大肠杆菌全细胞生物投手

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We investigated the quantification of bioavailable arsenic in contaminated soils and evaluation of soil-washing processes in the aspect of bioavailability using a novel bacterial bioreporter developed in present study. The whole-cell bioreporter (WCB) was genetically engineered by fusing the promoter of nik operon from Escherichia coli and green fluorescent protein as a sensing domain and reporter domain. Among eight well-known hazardous heavy metals and metalloid, this system responded specifically to arsenic, thereby inferring association of As(III) with NikR inhibits the repression. Moreover, the response was proportional to the concentration of As(III), thereby it was capable to determine the amount of bioavailable arsenic quantitatively in contaminated soils. The bioavailable portion of arsenic was 5.9 (3.46-10.96) and 0.9 (0.27-1.74) % of total from amended and site soils, respectively, suggesting the bioavailability of arsenic in soils was related to the soil properties and duration of aging. On the other hand, only 1.37 (0.21-2.97) % of total arsenic was extracted into soil solutions and 19.88 (11.86-28.27) % of arsenic in soil solution was bioavailable. This result showed that the soluble arsenic is not all bioavailable and most of bioavailable arsenic in soils is water non-extractable. In addition, the bioavailable arsenic was increased after soil-washing while total amount was decreased, thereby suggesting the soil-washing processes release arsenic associated with soil materials to be bioavailable. Therefore, it would be valuable to have a tool to assess bioavailability and the bioavailability should be taken into consideration for soil remediation plans.
机译:我们研究了在本研究中开发的新细菌生物投发器在生物利用度方面的污染土壤中生物可利用砷的定量和土壤洗涤过程的评价。通过将Nik操纵从大肠杆菌和绿色荧光蛋白作为传感结构域和报告结构域融合,通过将Nik操纵子的启动子进行遗传设计的全细胞生物投资者(WCB)。在八个众所周知的危险性重金属和金属体中,该系统特异性地对砷进行响应,从而推断为(III)与尼克尔的关联抑制抑制。此外,响应与AS(III)的浓度成比例,从而能够定量地在受污染的土壤中定量测定生物可利用的砷量。砷的生物可利用部分分别为5.9(3.46-10.96)和0.9(0.27-1.74)总量的修正和现场土壤,表明砷在土壤中的生物利用度与土壤性质和老化持续时间有关。另一方面,仅将总砷的1.37(0.21-2.97)%提取到土壤溶液中,19.88(11.86-28.27)%的土壤溶液中的砷得到生物可利用。该结果表明,可溶性砷并非所有生物可利用,土壤中的大部分生物可利用砷都是防水。此外,在土壤洗涤后,生物可利用的砷在整个金额减少后增加,从而表明土壤洗涤过程释放与土壤材料相关的砷是生物可利用的。因此,具有评估生物利用度的工具是有价值的,并且应考虑到土壤修复计划的生物利用度。

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