Bioremediation of Uranium- and Nitrate-Contaminated Groundwater after the In Situ Leach Mining of Uranium

Uranium and nitrate are common groundwater pollutants near in situ leach uranium mines. However, we still lack techniques that can simultaneously immobilize uranium and reduce nitrate using a single bacterial species. In this study, the potential of simultaneous uranium immobilization and nitrate re...

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Autores principales: Rehemanjiang Wufuer, Jia Duo, Wenfeng Li, Jinglong Fan, Xiangliang Pan
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Publicado: MDPI AG 2021
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spelling oai:doaj.org-article:ad09cd8e12e44fb686dcd6df201c4c682021-11-25T19:15:18ZBioremediation of Uranium- and Nitrate-Contaminated Groundwater after the In Situ Leach Mining of Uranium10.3390/w132231882073-4441https://doaj.org/article/ad09cd8e12e44fb686dcd6df201c4c682021-11-01T00:00:00Zhttps://www.mdpi.com/2073-4441/13/22/3188https://doaj.org/toc/2073-4441Uranium and nitrate are common groundwater pollutants near in situ leach uranium mines. However, we still lack techniques that can simultaneously immobilize uranium and reduce nitrate using a single bacterial species. In this study, the potential of simultaneous uranium immobilization and nitrate reduction by a single AFODN (anaerobic Fe(II) oxidizing denitrifier), <i>Clostridium</i> sp. PXL2, was investigated. <i>Clostridium</i> sp. PXL2 showed tolerance to U(VI) concentrations varying from 4.2 µM to 42 µM. The U(VI) immobilization and nitrate reduction rates in groundwater samples inoculated with this bacterium reached up to 75.1% and 55.7%, respectively, under neutral conditions. Exposure to oxidation conditions led to further U(VI) removal but did not show any noticeable effect on nitrate reduction. The U(VI) immobilization rate reached up to 85% with an increased Fe(II) initial concentration, but this inhibited nitrate reduction. SEM (scanning electron microscopy) coupled with EDS (energy dispersive spectroscopy) showed that the U(VI) immobilization was mainly due to sorption to amorphous ferric oxides. U(VI) and nitrate bioremediation by AFODNs, including <i>Clostridium</i> sp. PXL2, may provide a promising method for the treatment of uranium- and nitrate-contaminated groundwater after the in situ leach mining of uranium.Rehemanjiang WufuerJia DuoWenfeng LiJinglong FanXiangliang PanMDPI AGarticle<i>Clostridium</i> sp. PXL2immobilizationreductionHydraulic engineeringTC1-978Water supply for domestic and industrial purposesTD201-500ENWater, Vol 13, Iss 3188, p 3188 (2021)
institution DOAJ
collection DOAJ
language EN
topic <i>Clostridium</i> sp. PXL2
immobilization
reduction
Hydraulic engineering
TC1-978
Water supply for domestic and industrial purposes
TD201-500
spellingShingle <i>Clostridium</i> sp. PXL2
immobilization
reduction
Hydraulic engineering
TC1-978
Water supply for domestic and industrial purposes
TD201-500
Rehemanjiang Wufuer
Jia Duo
Wenfeng Li
Jinglong Fan
Xiangliang Pan
Bioremediation of Uranium- and Nitrate-Contaminated Groundwater after the In Situ Leach Mining of Uranium
description Uranium and nitrate are common groundwater pollutants near in situ leach uranium mines. However, we still lack techniques that can simultaneously immobilize uranium and reduce nitrate using a single bacterial species. In this study, the potential of simultaneous uranium immobilization and nitrate reduction by a single AFODN (anaerobic Fe(II) oxidizing denitrifier), <i>Clostridium</i> sp. PXL2, was investigated. <i>Clostridium</i> sp. PXL2 showed tolerance to U(VI) concentrations varying from 4.2 µM to 42 µM. The U(VI) immobilization and nitrate reduction rates in groundwater samples inoculated with this bacterium reached up to 75.1% and 55.7%, respectively, under neutral conditions. Exposure to oxidation conditions led to further U(VI) removal but did not show any noticeable effect on nitrate reduction. The U(VI) immobilization rate reached up to 85% with an increased Fe(II) initial concentration, but this inhibited nitrate reduction. SEM (scanning electron microscopy) coupled with EDS (energy dispersive spectroscopy) showed that the U(VI) immobilization was mainly due to sorption to amorphous ferric oxides. U(VI) and nitrate bioremediation by AFODNs, including <i>Clostridium</i> sp. PXL2, may provide a promising method for the treatment of uranium- and nitrate-contaminated groundwater after the in situ leach mining of uranium.
format article
author Rehemanjiang Wufuer
Jia Duo
Wenfeng Li
Jinglong Fan
Xiangliang Pan
author_facet Rehemanjiang Wufuer
Jia Duo
Wenfeng Li
Jinglong Fan
Xiangliang Pan
author_sort Rehemanjiang Wufuer
title Bioremediation of Uranium- and Nitrate-Contaminated Groundwater after the In Situ Leach Mining of Uranium
title_short Bioremediation of Uranium- and Nitrate-Contaminated Groundwater after the In Situ Leach Mining of Uranium
title_full Bioremediation of Uranium- and Nitrate-Contaminated Groundwater after the In Situ Leach Mining of Uranium
title_fullStr Bioremediation of Uranium- and Nitrate-Contaminated Groundwater after the In Situ Leach Mining of Uranium
title_full_unstemmed Bioremediation of Uranium- and Nitrate-Contaminated Groundwater after the In Situ Leach Mining of Uranium
title_sort bioremediation of uranium- and nitrate-contaminated groundwater after the in situ leach mining of uranium
publisher MDPI AG
publishDate 2021
url https://doaj.org/article/ad09cd8e12e44fb686dcd6df201c4c68
work_keys_str_mv AT rehemanjiangwufuer bioremediationofuraniumandnitratecontaminatedgroundwateraftertheinsituleachminingofuranium
AT jiaduo bioremediationofuraniumandnitratecontaminatedgroundwateraftertheinsituleachminingofuranium
AT wenfengli bioremediationofuraniumandnitratecontaminatedgroundwateraftertheinsituleachminingofuranium
AT jinglongfan bioremediationofuraniumandnitratecontaminatedgroundwateraftertheinsituleachminingofuranium
AT xiangliangpan bioremediationofuraniumandnitratecontaminatedgroundwateraftertheinsituleachminingofuranium
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