首页> 外文期刊>Environmental Science & Technology >Influence of Arsenate Adsorption to Ferrihydrite, Goethite, and Boehmite on the Kinetics of Arsenate Reduction by Shewanella putrefaciens strain CN-32
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Influence of Arsenate Adsorption to Ferrihydrite, Goethite, and Boehmite on the Kinetics of Arsenate Reduction by Shewanella putrefaciens strain CN-32

机译:砷吸附到水铁矿,针铁矿和勃姆石上对腐烂希瓦氏菌菌株CN-32还原砷的动力学的影响

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摘要

The kinetics of As(V) reduction by Shewanella putrefaciens strain CN-32 was investigated in suspensions of 0.2, 2, or 20 g L~(-1)ferrihydrite, goethite, or boehmite at low As (10 μM) and lactate (25 μM) concentrations. Experimental data were compared with model predictions based on independently determined sorption isotherms and rates of As(V) desorption, As(Ⅲ) adsorption, and microbial reduction of dissolved As(V), respectively. The low lactate concentration was chosen to prevent significant Fe(Ⅲ) reduction, but still allowing complete As(V) reduction. Reduction of dissolved As(V) followed first-order kinetics with a 3 h half-life of As(V). Addition of mineral sorbents resulted in pronounced decreases in reduction rates (32-1540 h As(V) half-life). The magnitude of this effect increased with increasing sorbent concentration and sorption capacity (goethite < boehmite < ferrihydrite). The model consistently underestimated the concentrations of dissolved As(V) and the rates of microbial As(V) reduction after addition of S. putrefaciens (~5 x 10~9 cells mL~(-1)), suggesting that attachment of S. putrefaciens cells to oxide mineral surfaces promoted As(V) desorption and thereby facilitated As(V) reduction. The interplay between As(V) sorption to mineral surfaces and bacterially induced desorption may thus be critical in controlling the kinetics of As reduction and release in reducing soils and sediments.
机译:在0.2、2或20 g L〜(-1)铁水铁矿,针铁矿或勃姆石悬浮液中以低砷(10μM)和乳酸(25 μM)浓度。将实验数据与基于独立确定的吸附等温线和As(V)解吸速率,As(Ⅲ)吸附速率以及溶解的As(V)的微生物还原速率进行的模型预测进行了比较。选择低乳酸浓度可以防止Fe(Ⅲ)显着还原,但仍可以使As(V)完全还原。溶解的As(V)的还原遵循一级动力学,As(V)的半衰期为3小时。矿物吸附剂的加入导致还原速率显着降低(32-1540 h As(V)半衰期)。随着吸附剂浓度和吸附容量(针铁矿<勃姆石<水铁矿)的增加,这种影响的程度也随之增加。该模型一致低估了腐烂链球菌(〜5 x 10〜9个细胞mL〜(-1))加入后的溶解As(V)浓度和微生物As(V)还原速率,表明S.附着。腐殖质细胞氧化矿物表面促进了As(V)的解吸,从而促进了As(V)的还原。因此,As(V)吸附到矿物表面和细菌引起的解吸之间的相互作用可能对控制As还原和释放还原土壤和沉积物中的动力学至关重要。

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  • 来源
    《Environmental Science & Technology》 |2011年第18期|p.7701-7709|共9页
  • 作者单位

    Soil Chemistry Group, Institute of Biogeochemistry and Pollutant Dynamics, ETH Zurich, CHN, CH-8092 Zurich, Switzerland;

    Soil Chemistry Group, Institute of Biogeochemistry and Pollutant Dynamics, ETH Zurich, CHN, CH-8092 Zurich, Switzerland Eawag, Swiss Federal Institute of Aquatic Science and Technology, Ueberlandstrasse 133, CH-8600 Duebendorf, Switzerland;

    Soil Chemistry Group, Institute of Biogeochemistry and Pollutant Dynamics, ETH Zurich, CHN, CH-8092 Zurich, Switzerland;

    Environmental Microbiology Group, Institute of Biogeochemistry and Pollutant Dynamics, ETH Zurich, CH-8092 Zurich, Switzerland;

    Environmental Microbiology Group, Institute of Biogeochemistry and Pollutant Dynamics, ETH Zurich, CH-8092 Zurich, Switzerland;

    Soil Chemistry Group, Institute of Biogeochemistry and Pollutant Dynamics, ETH Zurich, CHN, CH-8092 Zurich, Switzerland;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);美国《生物学医学文摘》(MEDLINE);美国《化学文摘》(CA);
  • 原文格式 PDF
  • 正文语种 eng
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  • 入库时间 2022-08-17 14:03:45

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