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GROUNDWATER CONTAMINATION DOWNSTREAM OF A CONTAMINANT PENETRATION SITE. I. EXTENSION-EXPANSION OF THE CONTAMINANT PLUME
This study concerns the possible use of boundary layer (BL) approach for the analysis and evaluation of contaminant transport in groundwater due to contaminant penetration into the groundwater aquifer through a site of limited size. The contaminant penetration may occur through either the upper (sur...
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Published in: | Journal of environmental science and health. Part A, Toxic/hazardous substances & environmental engineering Toxic/hazardous substances & environmental engineering, 2002-11, Vol.37 (10), p.1781-1812 |
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container_end_page | 1812 |
container_issue | 10 |
container_start_page | 1781 |
container_title | Journal of environmental science and health. Part A, Toxic/hazardous substances & environmental engineering |
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creator | Rubin, Hillel Buddemeier, Robert W. |
description | This study concerns the possible use of boundary layer (BL) approach for the analysis and evaluation of contaminant transport in groundwater due to contaminant penetration into the groundwater aquifer through a site of limited size. The contaminant penetration may occur through either the upper (surface) or lower (bedrock) boundary of the aquifer. Two general cases of contaminant penetration mechanisms are considered: (1) the contaminant is transferred through an interface between a contaminating and freshwater fluid phases, and (2) the contaminant arrives at groundwater by leakage and percolation. For the purpose of BL evaluation the contaminant plume is divided into three different sections: (1) the penetration section, (2) the extension-expansion section, and (3) the spearhead section. In each section a different BL method approach yields simple analytical expressions for the description of the contaminant plume migration and contaminant transport. Previous studies of the BL method can be directly applied to the evaluation of contaminant transport at the contaminant penetration section. The present study extends those studies and concerns the contaminant transport in the two other sections, which are located downstream of the penetration section. This study shows that the contaminant concentration profiles in sections
1
and
2
incorporate two BLs: (1) an inner BL adjacent to the aquifer bottom or surface boundary, and (2) an outer BL, which develops above or below the inner one. The method developed in the present study has been applied to practical issues concerning salinity penetration into groundwater in south central Kansas. |
doi_str_mv | 10.1081/ESE-120015461 |
format | article |
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1
and
2
incorporate two BLs: (1) an inner BL adjacent to the aquifer bottom or surface boundary, and (2) an outer BL, which develops above or below the inner one. The method developed in the present study has been applied to practical issues concerning salinity penetration into groundwater in south central Kansas.</description><identifier>ISSN: 1093-4529</identifier><identifier>EISSN: 1532-4117</identifier><identifier>DOI: 10.1081/ESE-120015461</identifier><identifier>PMID: 12413210</identifier><language>eng</language><publisher>England: Taylor & Francis Group</publisher><subject>Aquifer contamination ; Aquifers ; Boundaries ; Boundary layers ; Contaminant penetration site ; Contaminant plume ; Contaminant plume expansion ; Contaminant plume extension ; Contaminant transport ; Contaminants ; Contamination ; Contamination approximate analysis ; Exact solutions ; Geological Phenomena ; Geology ; Groundwater ; Models, Theoretical ; Particle Size ; Penetration ; Plumes ; Soil Pollutants - analysis ; Transport ; USA, Kansas ; Water Movements ; Water Pollutants - analysis ; Water Supply</subject><ispartof>Journal of environmental science and health. Part A, Toxic/hazardous substances & environmental engineering, 2002-11, Vol.37 (10), p.1781-1812</ispartof><rights>Copyright Taylor & Francis Group, LLC 2002</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c496t-a5639f1bdbf6861985d597808b6800f9ce272f54c5c041c1de5c76ad8d916bae3</citedby><cites>FETCH-LOGICAL-c496t-a5639f1bdbf6861985d597808b6800f9ce272f54c5c041c1de5c76ad8d916bae3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27901,27902</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/12413210$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Rubin, Hillel</creatorcontrib><creatorcontrib>Buddemeier, Robert W.</creatorcontrib><title>GROUNDWATER CONTAMINATION DOWNSTREAM OF A CONTAMINANT PENETRATION SITE. I. EXTENSION-EXPANSION OF THE CONTAMINANT PLUME</title><title>Journal of environmental science and health. Part A, Toxic/hazardous substances & environmental engineering</title><addtitle>J Environ Sci Health A Tox Hazard Subst Environ Eng</addtitle><description>This study concerns the possible use of boundary layer (BL) approach for the analysis and evaluation of contaminant transport in groundwater due to contaminant penetration into the groundwater aquifer through a site of limited size. The contaminant penetration may occur through either the upper (surface) or lower (bedrock) boundary of the aquifer. Two general cases of contaminant penetration mechanisms are considered: (1) the contaminant is transferred through an interface between a contaminating and freshwater fluid phases, and (2) the contaminant arrives at groundwater by leakage and percolation. For the purpose of BL evaluation the contaminant plume is divided into three different sections: (1) the penetration section, (2) the extension-expansion section, and (3) the spearhead section. In each section a different BL method approach yields simple analytical expressions for the description of the contaminant plume migration and contaminant transport. Previous studies of the BL method can be directly applied to the evaluation of contaminant transport at the contaminant penetration section. The present study extends those studies and concerns the contaminant transport in the two other sections, which are located downstream of the penetration section. This study shows that the contaminant concentration profiles in sections
1
and
2
incorporate two BLs: (1) an inner BL adjacent to the aquifer bottom or surface boundary, and (2) an outer BL, which develops above or below the inner one. The method developed in the present study has been applied to practical issues concerning salinity penetration into groundwater in south central Kansas.</description><subject>Aquifer contamination</subject><subject>Aquifers</subject><subject>Boundaries</subject><subject>Boundary layers</subject><subject>Contaminant penetration site</subject><subject>Contaminant plume</subject><subject>Contaminant plume expansion</subject><subject>Contaminant plume extension</subject><subject>Contaminant transport</subject><subject>Contaminants</subject><subject>Contamination</subject><subject>Contamination approximate analysis</subject><subject>Exact solutions</subject><subject>Geological Phenomena</subject><subject>Geology</subject><subject>Groundwater</subject><subject>Models, Theoretical</subject><subject>Particle Size</subject><subject>Penetration</subject><subject>Plumes</subject><subject>Soil Pollutants - analysis</subject><subject>Transport</subject><subject>USA, Kansas</subject><subject>Water Movements</subject><subject>Water Pollutants - analysis</subject><subject>Water Supply</subject><issn>1093-4529</issn><issn>1532-4117</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2002</creationdate><recordtype>article</recordtype><recordid>eNqFkk1r20AQhpfS0qRpj70Wndpe5O7st47C2SQCWwr2muS26GMFLrKV7tqE_Puua9NQKMlphpln3hmGF6HPgCeAFfzQS50CwRg4E_AGnQOnJGUA8m3McUZTxkl2hj6E8DNCigJ_j86AMKAE8Dl6vF5Uq_LyLjd6kUyr0uTzosxNUZXJZXVXLs1C5_Okukry525pkltdarM4csvC6ElSTBJ9b3S5jKVU39_mf7LDpLnR_87OVnP9Eb3r6yG4T6d4gVZX2kxv0ll1XUzzWdqyTOzSmgua9dB0TS-UgEzxjmdSYdUIhXGftY5I0nPW8hYzaKFzvJWi7lSXgWhqRy_Qt6Pugx9_7V3Y2c06tG4Y6q0b98EqLIlUgvNIfn2RJBKoIgpH8PuLIEgp4-NpPP01TRDAMKGvLwcmGFP0sDw9gq0fQ_Cutw9-van9kwVsD4aw0RD2ryEi_-UkvG82rnumTw6IgDoC620_-k39OPqhs7v6aRh97-ttuw6W_l_7N76AtyA</recordid><startdate>200211</startdate><enddate>200211</enddate><creator>Rubin, Hillel</creator><creator>Buddemeier, Robert W.</creator><general>Taylor & Francis Group</general><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>7ST</scope><scope>C1K</scope><scope>SOI</scope><scope>7TV</scope><scope>7UA</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope><scope>7SU</scope><scope>8FD</scope><scope>FR3</scope><scope>KR7</scope></search><sort><creationdate>200211</creationdate><title>GROUNDWATER CONTAMINATION DOWNSTREAM OF A CONTAMINANT PENETRATION SITE. I. EXTENSION-EXPANSION OF THE CONTAMINANT PLUME</title><author>Rubin, Hillel ; Buddemeier, Robert W.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c496t-a5639f1bdbf6861985d597808b6800f9ce272f54c5c041c1de5c76ad8d916bae3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2002</creationdate><topic>Aquifer contamination</topic><topic>Aquifers</topic><topic>Boundaries</topic><topic>Boundary layers</topic><topic>Contaminant penetration site</topic><topic>Contaminant plume</topic><topic>Contaminant plume expansion</topic><topic>Contaminant plume extension</topic><topic>Contaminant transport</topic><topic>Contaminants</topic><topic>Contamination</topic><topic>Contamination approximate analysis</topic><topic>Exact solutions</topic><topic>Geological Phenomena</topic><topic>Geology</topic><topic>Groundwater</topic><topic>Models, Theoretical</topic><topic>Particle Size</topic><topic>Penetration</topic><topic>Plumes</topic><topic>Soil Pollutants - analysis</topic><topic>Transport</topic><topic>USA, Kansas</topic><topic>Water Movements</topic><topic>Water Pollutants - analysis</topic><topic>Water Supply</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Rubin, Hillel</creatorcontrib><creatorcontrib>Buddemeier, Robert W.</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Environment Abstracts</collection><collection>Pollution Abstracts</collection><collection>Water Resources Abstracts</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Environmental Engineering Abstracts</collection><collection>Technology Research Database</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><jtitle>Journal of environmental science and health. 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Part A, Toxic/hazardous substances & environmental engineering</jtitle><addtitle>J Environ Sci Health A Tox Hazard Subst Environ Eng</addtitle><date>2002-11</date><risdate>2002</risdate><volume>37</volume><issue>10</issue><spage>1781</spage><epage>1812</epage><pages>1781-1812</pages><issn>1093-4529</issn><eissn>1532-4117</eissn><abstract>This study concerns the possible use of boundary layer (BL) approach for the analysis and evaluation of contaminant transport in groundwater due to contaminant penetration into the groundwater aquifer through a site of limited size. The contaminant penetration may occur through either the upper (surface) or lower (bedrock) boundary of the aquifer. Two general cases of contaminant penetration mechanisms are considered: (1) the contaminant is transferred through an interface between a contaminating and freshwater fluid phases, and (2) the contaminant arrives at groundwater by leakage and percolation. For the purpose of BL evaluation the contaminant plume is divided into three different sections: (1) the penetration section, (2) the extension-expansion section, and (3) the spearhead section. In each section a different BL method approach yields simple analytical expressions for the description of the contaminant plume migration and contaminant transport. Previous studies of the BL method can be directly applied to the evaluation of contaminant transport at the contaminant penetration section. The present study extends those studies and concerns the contaminant transport in the two other sections, which are located downstream of the penetration section. This study shows that the contaminant concentration profiles in sections
1
and
2
incorporate two BLs: (1) an inner BL adjacent to the aquifer bottom or surface boundary, and (2) an outer BL, which develops above or below the inner one. The method developed in the present study has been applied to practical issues concerning salinity penetration into groundwater in south central Kansas.</abstract><cop>England</cop><pub>Taylor & Francis Group</pub><pmid>12413210</pmid><doi>10.1081/ESE-120015461</doi><tpages>32</tpages></addata></record> |
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subjects | Aquifer contamination Aquifers Boundaries Boundary layers Contaminant penetration site Contaminant plume Contaminant plume expansion Contaminant plume extension Contaminant transport Contaminants Contamination Contamination approximate analysis Exact solutions Geological Phenomena Geology Groundwater Models, Theoretical Particle Size Penetration Plumes Soil Pollutants - analysis Transport USA, Kansas Water Movements Water Pollutants - analysis Water Supply |
title | GROUNDWATER CONTAMINATION DOWNSTREAM OF A CONTAMINANT PENETRATION SITE. I. EXTENSION-EXPANSION OF THE CONTAMINANT PLUME |
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