五价钒在负载奥奈达希瓦氏菌(Shewanella oneidensis) MR-1生物炭柱中持留与微生物还原

Retention and Microbial Reduction of V(Ⅴ) in Biochar Column Loaded with Shewanella oneidensis MR-1

  • 摘要: 自然环境中五价钒〔V(Ⅴ)〕毒性和迁移性远高于低价钒, 易随雨水的淋滤作用迁移至地下水, 造成地表与地下水污染。微生物能够将V(Ⅴ)还原为毒性较低的V(Ⅳ), 减弱其在土壤环境中的移动性和生物可利用性。本研究选用粒径0.80 mm竹炭作为载体负载奥奈达希瓦氏菌(Shewanella oneidensis)MR-1, 通过柱淋溶试验探究竹炭对V(Ⅴ)的持留以及奥奈达希瓦氏菌MR-1对V(Ⅴ)的还原能力, 并分别研究流速、V(Ⅴ)初始浓度、溶液pH值以及腐殖酸浓度等因素对V(Ⅴ)迁移的影响。结果显示, 负载细菌显著增强V(Ⅴ)在竹炭柱中的持留。在淋溶液V(Ⅴ)质量浓度分别为5、10、20、40和80 mg·L-1条件下, 当淋溶液体积为8 PV(PV为孔隙体积, 60 mL)时, 竹炭柱中流出液V(Ⅴ)质量浓度分别为6.11、9.09、18.31、39.23和79.61 mg·L-1, 而负载细菌竹炭柱流出液V(Ⅴ)质量浓度则分别为0、1.07、4.63、3.48和12.13 mg·L-1, 表明负载奥奈达希瓦氏菌MR-1可以降低竹炭柱中V(Ⅴ)的移动性。微生物还原V(Ⅴ)过程中, 初始接菌量增加可以加快V(Ⅴ)的还原; 在溶液pH值为5.5~8.5条件下, 经7 d培养后菌株对V(Ⅴ)的还原率均超过95%, 其中, 当pH值为7.5时V(Ⅴ)还原率达到最高, 为98.30%;腐殖酸浓度增加可略微降低菌株对V(Ⅴ)的还原能力。V(Ⅴ)在竹炭柱淋溶过程中, 较低的淋溶液流速有利于竹炭对V(Ⅴ)的吸附, 并促进微生物对V(Ⅴ)的还原反应; 较高的接菌量有助于增强微生物对V(Ⅴ)的还原固定; 在淋溶体积为8 PV条件下, 当淋溶液pH值为5.5时流出液中V(Ⅴ)质量浓度为1.98 mg·L-1, 而当淋溶液pH值为8.5时流出液中V(Ⅴ)浓度增加至13.69 mg·L-1, 较低的pH值可以降低V(Ⅴ)在生物炭柱中的迁移性; 腐殖酸在低浓度时促进微生物对V(Ⅴ)的还原, 但在高浓度时可能会与V(Ⅴ)形成络合物, 降低V(Ⅴ)还原效率。研究表明, 竹炭固定化微生物能促进V(Ⅴ)的持留与还原, 可用于钒污染土壤与地下水修复。

     

    Abstract: The toxicity and environmental mobility of V(Ⅴ) in soil are significantly higher than those of low-valent forms. V(Ⅴ) exhibits high leaching potential into groundwater under rainfall conditions, leading to contamination of both surface and ground water. Specific microorganisms can catalyze the reduction of V(Ⅴ) to V(Ⅳ), weakening its mobility and bioavailability in the environment. In this study, bamboo charcoal, with a precisely controlled particle size of 0.80 mm, was employed as a carrier for the load of Shewanella oneidensis MR-1. The biochar column experiments were subsequently conducted to investigate the retention and microbial reduction of V(Ⅴ). The impacts of elution rate, initial V(Ⅴ) concentration, solution pH, and humic acid concentration on vanadium migration were systematically examined. The results demonstrate that the retention of V(Ⅴ) within the biochar column was significantly enhanced by the presence of the loaded bacteria. When the injection volume was eight times of pore volume (PV, 60 mL) and the initial V(Ⅴ) concentrations were 5, 10, 20, 40 and 80 mg·L-1, the V(Ⅴ) concentrations in the effluent from the biochar column were 6.11, 9.09, 18.31, 39.23 and 79.61 mg·L-1, respectively. In contrast, the V(Ⅴ) concentrations in the effluent from the bacteria-loaded biochar column were 0, 1.07, 4.63, 3.48 and 12.13 mg·L-1, respectively. These results indicate that S. oneidensis MR-1 significantly reduced the mobility of V(Ⅴ) within the column. During the microbial V(Ⅴ) reduction process, increasing the bacterial inoculation amount expedited the reduction of V(Ⅴ). Under conditions with a solution pH ranging from 5.5 to 8.5, the reduction rate of V(Ⅴ) by the strains exceeded 95% after a 7-day incubation period, with the highest reduction rate of 98.30% achieved at pH 7.5. Conversely, an increase in humic acid concentration slightly diminished the reduction of V(Ⅴ). In the column leaching test, a lower elution rate facilitated the adsorption of V(Ⅴ) by biochar and promoted the microbial reduction reaction of V(Ⅴ). Higher bacteria density contributed to enhancing the microbial reduction of V(Ⅴ). When the inject volume reached 8 PV, the concentration of V(Ⅴ) in the effluent was 1.98 mg·L-1 at a pH of 5.5. In contrast, the concentration of V(Ⅴ) in the effluent increased to 13.69 mg·L-1 at a pH of 8.5. A lower pH reduced the mobility of V(Ⅴ) in the biochar column. Humic acid promoted microbial V(Ⅴ) reduction at low concentrations, whereas it formed complexes with V(Ⅴ) at high concentrations, thereby decreasing V(Ⅴ) reduction. These findings reveal that bamboo charcoal-immobilized microorganisms enhanced the retention and reduction of V(Ⅴ), and this approach holds potential for the remediation of vanadium-contaminated soil and groundwater.

     

/

返回文章
返回