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Conceptual and numerical model of uranium(VI) reductive immobilization in fractured subsurface sediments
A conceptual model and numerical simulations of bacterial U(VI) reduction in fractured subsurface sediments were developed to assess the potential feasibility of biomineralization at the fracture/matrix interface as a mechanism for immobilization of uranium in structured subsurface media. The model...
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Published in: | Chemosphere (Oxford) 2005-04, Vol.59 (5), p.617-628 |
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description | A conceptual model and numerical simulations of bacterial U(VI) reduction in fractured subsurface sediments were developed to assess the potential feasibility of biomineralization at the fracture/matrix interface as a mechanism for immobilization of uranium in structured subsurface media. The model envisions flow of anaerobic groundwater, with or without acetate as an electron donor for stimulation of U(VI) reduction by dissimilatory metal-reducing bacteria (DMRB), within mobile macropores along a one-dimensional flow path. As the groundwater moves along the flow path, U(VI) trapped in the immobile mesopore and micropore domains (the sediment matrix) becomes desorbed and transferred to the mobile macropores (fractures) via a first-order exchange mechanism. By allowing bacterial U(VI) reduction to occur in the mesopore domain (assumed to account for 12% of total sediment pore volume) according to experimentally-determined kinetic parameters and an assumed DMRB abundance of 10
7 cells per cm
3 bulk sediment (equivalent to 4 mg of cells per dm
3 bulk sediment), the concentration of U(VI) in the macropore domain was reduced ca. 10-fold compared to that predicted in the absence of mesopore DMRB activity after a 6-month simulation period. The results suggest that input of soluble electron donors over a period of years could lead to a major redistribution of uranium in fractured subsurface sediments, converting potentially mobile sorbed U(VI) to an insoluble reduced phase (i.e. uraninite) in the mesopore domain that is expected to be permanently immobile under sustained anaerobic conditions. |
doi_str_mv | 10.1016/j.chemosphere.2004.11.007 |
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7 cells per cm
3 bulk sediment (equivalent to 4 mg of cells per dm
3 bulk sediment), the concentration of U(VI) in the macropore domain was reduced ca. 10-fold compared to that predicted in the absence of mesopore DMRB activity after a 6-month simulation period. The results suggest that input of soluble electron donors over a period of years could lead to a major redistribution of uranium in fractured subsurface sediments, converting potentially mobile sorbed U(VI) to an insoluble reduced phase (i.e. uraninite) in the mesopore domain that is expected to be permanently immobile under sustained anaerobic conditions.</description><identifier>ISSN: 0045-6535</identifier><identifier>EISSN: 1879-1298</identifier><identifier>DOI: 10.1016/j.chemosphere.2004.11.007</identifier><identifier>PMID: 15792659</identifier><identifier>CODEN: CMSHAF</identifier><language>eng</language><publisher>Oxford: Elsevier Ltd</publisher><subject>Adsorption ; Applied sciences ; Biodegradation, Environmental ; Biological and medical sciences ; Bioremediation ; Biotechnology ; Computer Simulation ; Decontamination. Miscellaneous ; Earth sciences ; Earth, ocean, space ; Engineering and environment geology. Geothermics ; Environment and pollution ; Exact sciences and technology ; Fractured ; Fresh Water ; Fundamental and applied biological sciences. Psychology ; Geobacter - metabolism ; Immobilization ; Industrial applications and implications. Economical aspects ; Iron ; Miscellaneous ; Models, Theoretical ; Oxidation-Reduction ; Pollution ; Pollution, environment geology ; Porosity ; Reduction ; Sediments ; Soil and sediments pollution ; Soil Pollutants, Radioactive - metabolism ; Uranium ; Uranium - chemistry ; Uranium - metabolism ; Uranium Compounds - metabolism ; Water Movements ; Water Pollutants, Radioactive - metabolism</subject><ispartof>Chemosphere (Oxford), 2005-04, Vol.59 (5), p.617-628</ispartof><rights>2004 Elsevier Ltd</rights><rights>2005 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c530t-114c40c2b2d9d82fcffe2585bfba3b29163f3d2bbbefba5e26559d3b2df3e9ec3</citedby><cites>FETCH-LOGICAL-c530t-114c40c2b2d9d82fcffe2585bfba3b29163f3d2bbbefba5e26559d3b2df3e9ec3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=16712445$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/15792659$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Roden, Eric E.</creatorcontrib><creatorcontrib>Scheibe, Timothy D.</creatorcontrib><title>Conceptual and numerical model of uranium(VI) reductive immobilization in fractured subsurface sediments</title><title>Chemosphere (Oxford)</title><addtitle>Chemosphere</addtitle><description>A conceptual model and numerical simulations of bacterial U(VI) reduction in fractured subsurface sediments were developed to assess the potential feasibility of biomineralization at the fracture/matrix interface as a mechanism for immobilization of uranium in structured subsurface media. The model envisions flow of anaerobic groundwater, with or without acetate as an electron donor for stimulation of U(VI) reduction by dissimilatory metal-reducing bacteria (DMRB), within mobile macropores along a one-dimensional flow path. As the groundwater moves along the flow path, U(VI) trapped in the immobile mesopore and micropore domains (the sediment matrix) becomes desorbed and transferred to the mobile macropores (fractures) via a first-order exchange mechanism. By allowing bacterial U(VI) reduction to occur in the mesopore domain (assumed to account for 12% of total sediment pore volume) according to experimentally-determined kinetic parameters and an assumed DMRB abundance of 10
7 cells per cm
3 bulk sediment (equivalent to 4 mg of cells per dm
3 bulk sediment), the concentration of U(VI) in the macropore domain was reduced ca. 10-fold compared to that predicted in the absence of mesopore DMRB activity after a 6-month simulation period. The results suggest that input of soluble electron donors over a period of years could lead to a major redistribution of uranium in fractured subsurface sediments, converting potentially mobile sorbed U(VI) to an insoluble reduced phase (i.e. uraninite) in the mesopore domain that is expected to be permanently immobile under sustained anaerobic conditions.</description><subject>Adsorption</subject><subject>Applied sciences</subject><subject>Biodegradation, Environmental</subject><subject>Biological and medical sciences</subject><subject>Bioremediation</subject><subject>Biotechnology</subject><subject>Computer Simulation</subject><subject>Decontamination. Miscellaneous</subject><subject>Earth sciences</subject><subject>Earth, ocean, space</subject><subject>Engineering and environment geology. Geothermics</subject><subject>Environment and pollution</subject><subject>Exact sciences and technology</subject><subject>Fractured</subject><subject>Fresh Water</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Geobacter - metabolism</subject><subject>Immobilization</subject><subject>Industrial applications and implications. Economical aspects</subject><subject>Iron</subject><subject>Miscellaneous</subject><subject>Models, Theoretical</subject><subject>Oxidation-Reduction</subject><subject>Pollution</subject><subject>Pollution, environment geology</subject><subject>Porosity</subject><subject>Reduction</subject><subject>Sediments</subject><subject>Soil and sediments pollution</subject><subject>Soil Pollutants, Radioactive - metabolism</subject><subject>Uranium</subject><subject>Uranium - chemistry</subject><subject>Uranium - metabolism</subject><subject>Uranium Compounds - metabolism</subject><subject>Water Movements</subject><subject>Water Pollutants, Radioactive - metabolism</subject><issn>0045-6535</issn><issn>1879-1298</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2005</creationdate><recordtype>article</recordtype><recordid>eNqNkUtvGyEURlGVqnHT_oWILBK1i5kCM4zNMrL6iBSpm7ZbxOMiYw3gwBCp_fUhsqVk2RWPe74LHBC6oqSnhE5f9r3ZQUjlsIMMPSNk7CntCVm_QSu6WYuOMrE5Q6tW4N3EB36O3peyJ6SFuXiHzilfC9amK7TbpmjgsFQ1YxUtjjVA9qatQrIw4-RwzSr6Gj79ufuMM9hqFv8I2IeQtJ_9P7X4FLGP2GVlltoIXKouNTtlABewPkBcygf01qm5wMfTeIF-f_v6a_uju__5_W57e98ZPpClo3Q0IzFMMyvshjnjHDC-4dppNWgm6DS4wTKtNbQdDu0VXNhWsW4AAWa4QDfHvoecHiqURQZfDMyzipBqkVQIJiZGGiiOoMmplAxOHrIPKv-VlMhnzXIvX2mWz5olpbJpbtnL0yFVB7AvyZPXBlyfAFWazKYmGl9euGlN2Tjyxm2PHDQljx6yLMZD-xHrM5hF2uT_4zpPU8ek7Q</recordid><startdate>20050401</startdate><enddate>20050401</enddate><creator>Roden, Eric E.</creator><creator>Scheibe, Timothy D.</creator><general>Elsevier Ltd</general><general>Elsevier</general><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QH</scope><scope>7T7</scope><scope>7TV</scope><scope>7UA</scope><scope>8FD</scope><scope>C1K</scope><scope>F1W</scope><scope>FR3</scope><scope>H96</scope><scope>H97</scope><scope>L.G</scope><scope>P64</scope></search><sort><creationdate>20050401</creationdate><title>Conceptual and numerical model of uranium(VI) reductive immobilization in fractured subsurface sediments</title><author>Roden, Eric E. ; Scheibe, Timothy D.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c530t-114c40c2b2d9d82fcffe2585bfba3b29163f3d2bbbefba5e26559d3b2df3e9ec3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2005</creationdate><topic>Adsorption</topic><topic>Applied sciences</topic><topic>Biodegradation, Environmental</topic><topic>Biological and medical sciences</topic><topic>Bioremediation</topic><topic>Biotechnology</topic><topic>Computer Simulation</topic><topic>Decontamination. Miscellaneous</topic><topic>Earth sciences</topic><topic>Earth, ocean, space</topic><topic>Engineering and environment geology. Geothermics</topic><topic>Environment and pollution</topic><topic>Exact sciences and technology</topic><topic>Fractured</topic><topic>Fresh Water</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Geobacter - metabolism</topic><topic>Immobilization</topic><topic>Industrial applications and implications. Economical aspects</topic><topic>Iron</topic><topic>Miscellaneous</topic><topic>Models, Theoretical</topic><topic>Oxidation-Reduction</topic><topic>Pollution</topic><topic>Pollution, environment geology</topic><topic>Porosity</topic><topic>Reduction</topic><topic>Sediments</topic><topic>Soil and sediments pollution</topic><topic>Soil Pollutants, Radioactive - metabolism</topic><topic>Uranium</topic><topic>Uranium - chemistry</topic><topic>Uranium - metabolism</topic><topic>Uranium Compounds - metabolism</topic><topic>Water Movements</topic><topic>Water Pollutants, Radioactive - metabolism</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Roden, Eric E.</creatorcontrib><creatorcontrib>Scheibe, Timothy D.</creatorcontrib><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Aqualine</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Pollution Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Engineering Research Database</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 2: Ocean Technology, Policy & Non-Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Biotechnology and BioEngineering Abstracts</collection><jtitle>Chemosphere (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Roden, Eric E.</au><au>Scheibe, Timothy D.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Conceptual and numerical model of uranium(VI) reductive immobilization in fractured subsurface sediments</atitle><jtitle>Chemosphere (Oxford)</jtitle><addtitle>Chemosphere</addtitle><date>2005-04-01</date><risdate>2005</risdate><volume>59</volume><issue>5</issue><spage>617</spage><epage>628</epage><pages>617-628</pages><issn>0045-6535</issn><eissn>1879-1298</eissn><coden>CMSHAF</coden><abstract>A conceptual model and numerical simulations of bacterial U(VI) reduction in fractured subsurface sediments were developed to assess the potential feasibility of biomineralization at the fracture/matrix interface as a mechanism for immobilization of uranium in structured subsurface media. The model envisions flow of anaerobic groundwater, with or without acetate as an electron donor for stimulation of U(VI) reduction by dissimilatory metal-reducing bacteria (DMRB), within mobile macropores along a one-dimensional flow path. As the groundwater moves along the flow path, U(VI) trapped in the immobile mesopore and micropore domains (the sediment matrix) becomes desorbed and transferred to the mobile macropores (fractures) via a first-order exchange mechanism. By allowing bacterial U(VI) reduction to occur in the mesopore domain (assumed to account for 12% of total sediment pore volume) according to experimentally-determined kinetic parameters and an assumed DMRB abundance of 10
7 cells per cm
3 bulk sediment (equivalent to 4 mg of cells per dm
3 bulk sediment), the concentration of U(VI) in the macropore domain was reduced ca. 10-fold compared to that predicted in the absence of mesopore DMRB activity after a 6-month simulation period. The results suggest that input of soluble electron donors over a period of years could lead to a major redistribution of uranium in fractured subsurface sediments, converting potentially mobile sorbed U(VI) to an insoluble reduced phase (i.e. uraninite) in the mesopore domain that is expected to be permanently immobile under sustained anaerobic conditions.</abstract><cop>Oxford</cop><pub>Elsevier Ltd</pub><pmid>15792659</pmid><doi>10.1016/j.chemosphere.2004.11.007</doi><tpages>12</tpages></addata></record> |
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subjects | Adsorption Applied sciences Biodegradation, Environmental Biological and medical sciences Bioremediation Biotechnology Computer Simulation Decontamination. Miscellaneous Earth sciences Earth, ocean, space Engineering and environment geology. Geothermics Environment and pollution Exact sciences and technology Fractured Fresh Water Fundamental and applied biological sciences. Psychology Geobacter - metabolism Immobilization Industrial applications and implications. Economical aspects Iron Miscellaneous Models, Theoretical Oxidation-Reduction Pollution Pollution, environment geology Porosity Reduction Sediments Soil and sediments pollution Soil Pollutants, Radioactive - metabolism Uranium Uranium - chemistry Uranium - metabolism Uranium Compounds - metabolism Water Movements Water Pollutants, Radioactive - metabolism |
title | Conceptual and numerical model of uranium(VI) reductive immobilization in fractured subsurface sediments |
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