Retardation of [sup 238]U and [sup 232]Th decay chain radionuclides in Long Island and Connecticut aquifers
Knowledge of the ability of an aquifer to retard the groundwater transport of toxic or radioactive ions can be inferred from the analysis of groundwater for the radionuclides of the [sup 238]U- and [sup 232]Th-decay chains. Groundwaters of varying chemical composition were analyzed from wells in Lon...
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creator | Copenhaver, S.A. Krishnaswami, S. Turekian, K.K. Epler, N. Cochran, J.K. |
description | Knowledge of the ability of an aquifer to retard the groundwater transport of toxic or radioactive ions can be inferred from the analysis of groundwater for the radionuclides of the [sup 238]U- and [sup 232]Th-decay chains. Groundwaters of varying chemical composition were analyzed from wells in Long Island, New York, and Connecticut. Aquifer lithologies are arkose, quartz sandstone, granite, and glacial drift. Adsorption (k[sub 1]) and desorption (k[sub 2]) coefficients for Ra and Pb were calculated using [sup 222]Rn activity as a measure of the supply of other [alpha]-recoil nuclides. Laboratory tests of the validity of this assumption were made by measuring the flux of [sup 224]Ra and [sup 222]Rn from aquifer solids. The ratio k[sub 1]/k[sub 2] is the distribution coefficient, K, which is effective equal to R[sub f], the retardation factor. The average value of K for Ra is 6 [times] 10[sup 2] in Long Island aquifers and 5 [times] 10[sup 4] in Connecticut. The distribution coefficient for Pb is 10[sup 4] in Long Island and 10[sup 5] in Connecticut. Results from this and other studies reveal a strong dependence of retardation on pH, f[sub o[sub 2]], and ionic strength that tends to overwhelm any dependence of retardation on lithology. 21 refs., 2 figs., 7 tabs. |
doi_str_mv | 10.1016/0016-7037(93)90370-C |
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Groundwaters of varying chemical composition were analyzed from wells in Long Island, New York, and Connecticut. Aquifer lithologies are arkose, quartz sandstone, granite, and glacial drift. Adsorption (k[sub 1]) and desorption (k[sub 2]) coefficients for Ra and Pb were calculated using [sup 222]Rn activity as a measure of the supply of other [alpha]-recoil nuclides. Laboratory tests of the validity of this assumption were made by measuring the flux of [sup 224]Ra and [sup 222]Rn from aquifer solids. The ratio k[sub 1]/k[sub 2] is the distribution coefficient, K, which is effective equal to R[sub f], the retardation factor. The average value of K for Ra is 6 [times] 10[sup 2] in Long Island aquifers and 5 [times] 10[sup 4] in Connecticut. The distribution coefficient for Pb is 10[sup 4] in Long Island and 10[sup 5] in Connecticut. Results from this and other studies reveal a strong dependence of retardation on pH, f[sub o[sub 2]], and ionic strength that tends to overwhelm any dependence of retardation on lithology. 21 refs., 2 figs., 7 tabs.</description><identifier>ISSN: 0016-7037</identifier><identifier>EISSN: 1872-9533</identifier><identifier>DOI: 10.1016/0016-7037(93)90370-C</identifier><language>eng</language><publisher>United States</publisher><subject>ACTINIDE ISOTOPES ; ACTINIDE NUCLEI ; ADSORPTION ; ALPHA DECAY RADIOISOTOPES ; AQUIFERS ; CHAINS ; CHARGED PARTICLES ; CHEMICAL COMPOSITION ; CONNECTICUT ; DECAY ; DESORPTION ; DEVELOPED COUNTRIES ; DISTRIBUTION ; ENVIRONMENTAL SCIENCES ; ENVIRONMENTAL TRANSPORT ; EVEN-EVEN NUCLEI ; GEOLOGY ; GROUND WATER ; HEAVY NUCLEI ; HYDROGEN COMPOUNDS ; IONS ; ISOTOPES ; LITHOLOGY ; MASS TRANSFER ; MINERALS ; NEW YORK ; NORTH AMERICA ; NUCLEI ; OXIDE MINERALS ; OXYGEN COMPOUNDS ; PETROLOGY ; QUARTZ ; RADIOISOTOPES ; RADIONUCLIDE MIGRATION ; SOLIDS ; SORPTION ; SPONTANEOUS FISSION RADIOISOTOPES ; THORIUM 232 ; THORIUM ISOTOPES ; TRANSPORT ; URANIUM 238 ; URANIUM ISOTOPES ; USA ; WATER ; WELLS ; YEARS LIVING RADIOISOTOPES 540330 -- Environment, Aquatic-- Radioactive Materials Monitoring & Transport-- (1990-)</subject><ispartof>Geochimica et cosmochimica acta, 1993-03, Vol.57:3</ispartof><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>230,315,781,785,886,27928,27929</link.rule.ids><backlink>$$Uhttps://www.osti.gov/biblio/6659713$$D View this record in Osti.gov$$Hfree_for_read</backlink></links><search><creatorcontrib>Copenhaver, S.A.</creatorcontrib><creatorcontrib>Krishnaswami, S.</creatorcontrib><creatorcontrib>Turekian, K.K.</creatorcontrib><creatorcontrib>Epler, N.</creatorcontrib><creatorcontrib>Cochran, J.K.</creatorcontrib><title>Retardation of [sup 238]U and [sup 232]Th decay chain radionuclides in Long Island and Connecticut aquifers</title><title>Geochimica et cosmochimica acta</title><description>Knowledge of the ability of an aquifer to retard the groundwater transport of toxic or radioactive ions can be inferred from the analysis of groundwater for the radionuclides of the [sup 238]U- and [sup 232]Th-decay chains. Groundwaters of varying chemical composition were analyzed from wells in Long Island, New York, and Connecticut. Aquifer lithologies are arkose, quartz sandstone, granite, and glacial drift. Adsorption (k[sub 1]) and desorption (k[sub 2]) coefficients for Ra and Pb were calculated using [sup 222]Rn activity as a measure of the supply of other [alpha]-recoil nuclides. Laboratory tests of the validity of this assumption were made by measuring the flux of [sup 224]Ra and [sup 222]Rn from aquifer solids. The ratio k[sub 1]/k[sub 2] is the distribution coefficient, K, which is effective equal to R[sub f], the retardation factor. The average value of K for Ra is 6 [times] 10[sup 2] in Long Island aquifers and 5 [times] 10[sup 4] in Connecticut. The distribution coefficient for Pb is 10[sup 4] in Long Island and 10[sup 5] in Connecticut. Results from this and other studies reveal a strong dependence of retardation on pH, f[sub o[sub 2]], and ionic strength that tends to overwhelm any dependence of retardation on lithology. 21 refs., 2 figs., 7 tabs.</description><subject>ACTINIDE ISOTOPES</subject><subject>ACTINIDE NUCLEI</subject><subject>ADSORPTION</subject><subject>ALPHA DECAY RADIOISOTOPES</subject><subject>AQUIFERS</subject><subject>CHAINS</subject><subject>CHARGED PARTICLES</subject><subject>CHEMICAL COMPOSITION</subject><subject>CONNECTICUT</subject><subject>DECAY</subject><subject>DESORPTION</subject><subject>DEVELOPED COUNTRIES</subject><subject>DISTRIBUTION</subject><subject>ENVIRONMENTAL SCIENCES</subject><subject>ENVIRONMENTAL TRANSPORT</subject><subject>EVEN-EVEN NUCLEI</subject><subject>GEOLOGY</subject><subject>GROUND WATER</subject><subject>HEAVY NUCLEI</subject><subject>HYDROGEN COMPOUNDS</subject><subject>IONS</subject><subject>ISOTOPES</subject><subject>LITHOLOGY</subject><subject>MASS TRANSFER</subject><subject>MINERALS</subject><subject>NEW YORK</subject><subject>NORTH AMERICA</subject><subject>NUCLEI</subject><subject>OXIDE MINERALS</subject><subject>OXYGEN COMPOUNDS</subject><subject>PETROLOGY</subject><subject>QUARTZ</subject><subject>RADIOISOTOPES</subject><subject>RADIONUCLIDE MIGRATION</subject><subject>SOLIDS</subject><subject>SORPTION</subject><subject>SPONTANEOUS FISSION RADIOISOTOPES</subject><subject>THORIUM 232</subject><subject>THORIUM ISOTOPES</subject><subject>TRANSPORT</subject><subject>URANIUM 238</subject><subject>URANIUM ISOTOPES</subject><subject>USA</subject><subject>WATER</subject><subject>WELLS</subject><subject>YEARS LIVING RADIOISOTOPES 540330 -- Environment, Aquatic-- Radioactive Materials Monitoring & Transport-- (1990-)</subject><issn>0016-7037</issn><issn>1872-9533</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1993</creationdate><recordtype>article</recordtype><recordid>eNo9TsFKxDAUDKLguvoHHoInPVRfkqZNjlJcXSgIsnuSZXl9TW20tLpJD_69XVY9vBlmmBkeY5cCbgWI7A4mSHJQ-bVVN3ZiSIojNhMml4nVSh2z2X_klJ2F8A4AudYwYx8vLuKuxuiHng8Nfw3jJ5fKbNYc-_pPys2q5bUj_ObUou_5DuupMFLnaxf4ZJRD_8aXoduX9lcMfe8oehojx6_RN24XztlJg11wF788Z-vFw6p4Ssrnx2VxXyYohImJNbaC1CmAmoyVSJmQWqUVptpglQtFEhxkDpXScrLSxqY2MxJIa0GiUnN2ddgdQvTbQD46aunw0DbLtJ021A_ADVjr</recordid><startdate>199303</startdate><enddate>199303</enddate><creator>Copenhaver, S.A.</creator><creator>Krishnaswami, S.</creator><creator>Turekian, K.K.</creator><creator>Epler, N.</creator><creator>Cochran, J.K.</creator><scope>OTOTI</scope></search><sort><creationdate>199303</creationdate><title>Retardation of [sup 238]U and [sup 232]Th decay chain radionuclides in Long Island and Connecticut aquifers</title><author>Copenhaver, S.A. ; Krishnaswami, S. ; Turekian, K.K. ; Epler, N. ; Cochran, J.K.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-a118t-989b04e300dc892ac612534ba458ab713c20e06ea335258a4f9496820c551c1b3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1993</creationdate><topic>ACTINIDE ISOTOPES</topic><topic>ACTINIDE NUCLEI</topic><topic>ADSORPTION</topic><topic>ALPHA DECAY RADIOISOTOPES</topic><topic>AQUIFERS</topic><topic>CHAINS</topic><topic>CHARGED PARTICLES</topic><topic>CHEMICAL COMPOSITION</topic><topic>CONNECTICUT</topic><topic>DECAY</topic><topic>DESORPTION</topic><topic>DEVELOPED COUNTRIES</topic><topic>DISTRIBUTION</topic><topic>ENVIRONMENTAL SCIENCES</topic><topic>ENVIRONMENTAL TRANSPORT</topic><topic>EVEN-EVEN NUCLEI</topic><topic>GEOLOGY</topic><topic>GROUND WATER</topic><topic>HEAVY NUCLEI</topic><topic>HYDROGEN COMPOUNDS</topic><topic>IONS</topic><topic>ISOTOPES</topic><topic>LITHOLOGY</topic><topic>MASS TRANSFER</topic><topic>MINERALS</topic><topic>NEW YORK</topic><topic>NORTH AMERICA</topic><topic>NUCLEI</topic><topic>OXIDE MINERALS</topic><topic>OXYGEN COMPOUNDS</topic><topic>PETROLOGY</topic><topic>QUARTZ</topic><topic>RADIOISOTOPES</topic><topic>RADIONUCLIDE MIGRATION</topic><topic>SOLIDS</topic><topic>SORPTION</topic><topic>SPONTANEOUS FISSION RADIOISOTOPES</topic><topic>THORIUM 232</topic><topic>THORIUM ISOTOPES</topic><topic>TRANSPORT</topic><topic>URANIUM 238</topic><topic>URANIUM ISOTOPES</topic><topic>USA</topic><topic>WATER</topic><topic>WELLS</topic><topic>YEARS LIVING RADIOISOTOPES 540330 -- Environment, Aquatic-- Radioactive Materials Monitoring & Transport-- (1990-)</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Copenhaver, S.A.</creatorcontrib><creatorcontrib>Krishnaswami, S.</creatorcontrib><creatorcontrib>Turekian, K.K.</creatorcontrib><creatorcontrib>Epler, N.</creatorcontrib><creatorcontrib>Cochran, J.K.</creatorcontrib><collection>OSTI.GOV</collection><jtitle>Geochimica et cosmochimica acta</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Copenhaver, S.A.</au><au>Krishnaswami, S.</au><au>Turekian, K.K.</au><au>Epler, N.</au><au>Cochran, J.K.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Retardation of [sup 238]U and [sup 232]Th decay chain radionuclides in Long Island and Connecticut aquifers</atitle><jtitle>Geochimica et cosmochimica acta</jtitle><date>1993-03</date><risdate>1993</risdate><volume>57:3</volume><issn>0016-7037</issn><eissn>1872-9533</eissn><abstract>Knowledge of the ability of an aquifer to retard the groundwater transport of toxic or radioactive ions can be inferred from the analysis of groundwater for the radionuclides of the [sup 238]U- and [sup 232]Th-decay chains. Groundwaters of varying chemical composition were analyzed from wells in Long Island, New York, and Connecticut. Aquifer lithologies are arkose, quartz sandstone, granite, and glacial drift. Adsorption (k[sub 1]) and desorption (k[sub 2]) coefficients for Ra and Pb were calculated using [sup 222]Rn activity as a measure of the supply of other [alpha]-recoil nuclides. Laboratory tests of the validity of this assumption were made by measuring the flux of [sup 224]Ra and [sup 222]Rn from aquifer solids. The ratio k[sub 1]/k[sub 2] is the distribution coefficient, K, which is effective equal to R[sub f], the retardation factor. The average value of K for Ra is 6 [times] 10[sup 2] in Long Island aquifers and 5 [times] 10[sup 4] in Connecticut. The distribution coefficient for Pb is 10[sup 4] in Long Island and 10[sup 5] in Connecticut. Results from this and other studies reveal a strong dependence of retardation on pH, f[sub o[sub 2]], and ionic strength that tends to overwhelm any dependence of retardation on lithology. 21 refs., 2 figs., 7 tabs.</abstract><cop>United States</cop><doi>10.1016/0016-7037(93)90370-C</doi></addata></record> |
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subjects | ACTINIDE ISOTOPES ACTINIDE NUCLEI ADSORPTION ALPHA DECAY RADIOISOTOPES AQUIFERS CHAINS CHARGED PARTICLES CHEMICAL COMPOSITION CONNECTICUT DECAY DESORPTION DEVELOPED COUNTRIES DISTRIBUTION ENVIRONMENTAL SCIENCES ENVIRONMENTAL TRANSPORT EVEN-EVEN NUCLEI GEOLOGY GROUND WATER HEAVY NUCLEI HYDROGEN COMPOUNDS IONS ISOTOPES LITHOLOGY MASS TRANSFER MINERALS NEW YORK NORTH AMERICA NUCLEI OXIDE MINERALS OXYGEN COMPOUNDS PETROLOGY QUARTZ RADIOISOTOPES RADIONUCLIDE MIGRATION SOLIDS SORPTION SPONTANEOUS FISSION RADIOISOTOPES THORIUM 232 THORIUM ISOTOPES TRANSPORT URANIUM 238 URANIUM ISOTOPES USA WATER WELLS YEARS LIVING RADIOISOTOPES 540330 -- Environment, Aquatic-- Radioactive Materials Monitoring & Transport-- (1990-) |
title | Retardation of [sup 238]U and [sup 232]Th decay chain radionuclides in Long Island and Connecticut aquifers |
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