Loading…
Ground water age and nitrate distribution within a glacial aquifer beneath a thick unsaturated zone
The impact on ground water quality from increasing fertilizer application rates over the past 40 years is evaluated within a glacial aquifer system beneath a thick unsaturated zone. Ground water ages within the aquifer could not be accurately determined from the measured distribution of 3H and as a...
Saved in:
Published in: | Ground water 1998-01, Vol.36 (1), p.171-180 |
---|---|
Main Authors: | , , , , , |
Format: | Article |
Language: | English |
Subjects: | |
Citations: | Items that this one cites Items that cite this one |
Online Access: | Get full text |
Tags: |
Add Tag
No Tags, Be the first to tag this record!
|
cited_by | cdi_FETCH-LOGICAL-a6621-6d772845b3a92a4d7c9ee4f993ce1ac2d42e39b26b8f7f4adf583f8ab46aa1253 |
---|---|
cites | cdi_FETCH-LOGICAL-a6621-6d772845b3a92a4d7c9ee4f993ce1ac2d42e39b26b8f7f4adf583f8ab46aa1253 |
container_end_page | 180 |
container_issue | 1 |
container_start_page | 171 |
container_title | Ground water |
container_volume | 36 |
creator | Johnston, C.T. (University of Waterloo, Waterloo, Ontario, Canada.) Cook, P.G Frape, S.K Plummer, L.N Busenberg, E Blackport, R.J |
description | The impact on ground water quality from increasing fertilizer application rates over the past 40 years is evaluated within a glacial aquifer system beneath a thick unsaturated zone. Ground water ages within the aquifer could not be accurately determined from the measured distribution of 3H and as a result, chlorofluorocarbon (CFC) and 3H/3He dating techniques were applied. Beneath a 25 m thick unsaturated zone, ground water ages based on CFC-11 concentrations were greater than 3H/3He ground water ages by 6 to 10 years, due to the time lag associated with the diffusion of CFCs through the unsaturated zone. Using the corrected CFC-11 and 3H/3He ground water ages and the estimated travel time of 3H within the unsaturated zone, the approximate position of ground water recharged since the mid-1960s was determined. Nitrate concentrations within post mid-1960s recharge were generally elevated and near or above the drinking water limit of 10 mg-N/L. In comparison, pre mid-1960s recharge had nitrate concentrations 2.5 mg-N/L. The elevated NO3- concentrations in post mid-1960s recharge are attributed mainly to increasing fertilizer application rates between 1970 and the mid- to late 1980s. Anaerobic conditions suitable for denitrification are present within pre mid-1960s recharge indicating that removal of DO is a slow process taking tens of years. Over the next 10 to 20 years, nitrate concentrations at municipal well fields that are currently capturing aerobic ground water recharged near the mid-1960s are expected to increase because of the higher fertilizer application rates beginning in the 1970s and 1980s |
doi_str_mv | 10.1111/j.1745-6584.1998.tb01078.x |
format | article |
fullrecord | <record><control><sourceid>gale_proqu</sourceid><recordid>TN_cdi_proquest_miscellaneous_743676170</recordid><sourceformat>XML</sourceformat><sourcesystem>PC</sourcesystem><galeid>A20425660</galeid><sourcerecordid>A20425660</sourcerecordid><originalsourceid>FETCH-LOGICAL-a6621-6d772845b3a92a4d7c9ee4f993ce1ac2d42e39b26b8f7f4adf583f8ab46aa1253</originalsourceid><addsrcrecordid>eNqVkk1v1DAQhiMEEsvCT0CKeoBLs_gr_uCCVhW7RRQ40Gp7syaJnXqbTVo70W759XWUqkioAmEfLM8889ozepPkCKMFjuvDdoEFyzOeS7bASslFXyCMhFwcniWzx9TzZIYQFhnj4vJl8iqELUKIKqRmSbn23dBW6R5641OoTQrx1rrex0BaudB7Vwy969p07_or16aQ1g2UDpoUbgdnY1VhWgP9VcxEoLxOhzZAP4wCVfqra83r5IWFJpg3D-c8uVh9Pj85zc5-rL-cLM8y4JzgjFdCEMnygoIiwCpRKmOYVYqWBkNJKkYMVQXhhbTCMqhsLqmVUDAOgElO58n7SffGd7eDCb3euVCapoHWdEPQglEuOBYoku_-ShLMEGXk3yDmFBOGcQSP_gC33eDb2K4mlEtJVOxjnhxPUA2N0a61XRxzWcfxeWjioKyL4SVBjOScj49nT-BxV2bnyqf4jxNf-i4Eb6y-8W4H_k5jpEe76K0ePaFHT-jRLvrBLvoQiz9NxfsoevcflXq9WZ5jgX9_N5rGHB4VwF9rLqjI9eb7Wn_dKPptdYn0KvJvJ95Cp6H2LuiLn1FbIBmlJb0H3Yrfmg</addsrcrecordid><sourcetype>Aggregation Database</sourcetype><iscdi>true</iscdi><recordtype>article</recordtype><pqid>236882999</pqid></control><display><type>article</type><title>Ground water age and nitrate distribution within a glacial aquifer beneath a thick unsaturated zone</title><source>Wiley</source><creator>Johnston, C.T. (University of Waterloo, Waterloo, Ontario, Canada.) ; Cook, P.G ; Frape, S.K ; Plummer, L.N ; Busenberg, E ; Blackport, R.J</creator><creatorcontrib>Johnston, C.T. (University of Waterloo, Waterloo, Ontario, Canada.) ; Cook, P.G ; Frape, S.K ; Plummer, L.N ; Busenberg, E ; Blackport, R.J</creatorcontrib><description>The impact on ground water quality from increasing fertilizer application rates over the past 40 years is evaluated within a glacial aquifer system beneath a thick unsaturated zone. Ground water ages within the aquifer could not be accurately determined from the measured distribution of 3H and as a result, chlorofluorocarbon (CFC) and 3H/3He dating techniques were applied. Beneath a 25 m thick unsaturated zone, ground water ages based on CFC-11 concentrations were greater than 3H/3He ground water ages by 6 to 10 years, due to the time lag associated with the diffusion of CFCs through the unsaturated zone. Using the corrected CFC-11 and 3H/3He ground water ages and the estimated travel time of 3H within the unsaturated zone, the approximate position of ground water recharged since the mid-1960s was determined. Nitrate concentrations within post mid-1960s recharge were generally elevated and near or above the drinking water limit of 10 mg-N/L. In comparison, pre mid-1960s recharge had nitrate concentrations 2.5 mg-N/L. The elevated NO3- concentrations in post mid-1960s recharge are attributed mainly to increasing fertilizer application rates between 1970 and the mid- to late 1980s. Anaerobic conditions suitable for denitrification are present within pre mid-1960s recharge indicating that removal of DO is a slow process taking tens of years. Over the next 10 to 20 years, nitrate concentrations at municipal well fields that are currently capturing aerobic ground water recharged near the mid-1960s are expected to increase because of the higher fertilizer application rates beginning in the 1970s and 1980s</description><identifier>ISSN: 0017-467X</identifier><identifier>EISSN: 1745-6584</identifier><identifier>DOI: 10.1111/j.1745-6584.1998.tb01078.x</identifier><identifier>CODEN: GRWAAP</identifier><language>eng</language><publisher>Oxford, UK: Blackwell Publishing Ltd</publisher><subject>ABONOS NITROGENADOS ; AGE DETERMINATION ; AGUAS SUBTERRANEAS ; Aquifers ; CAPA FREATICA ; CARACTERISTICAS MORFOLOGICAS SUELO ; CHLORIDES ; CHLOROFLUOROCARBONS ; CHLORURE ; CLORUROS ; COMPOSE ORGANOHALOGENE ; Composition ; COMPUESTO ORGANICO HALOGENO ; DETERMINACION DE LA EDAD ; DETERMINATION DE L'AGE ; DISSOLVED OXYGEN ; EAU SOUTERRAINE ; ENGRAIS AZOTE ; Environmental aspects ; EPAISSEUR ; ESPESOR ; Fertilizers ; FLUVIOGLACIAL SOILS ; GROUNDWATER ; GROUNDWATER RECHARGE ; GROUNDWATER TABLE ; HELIUM ; Hydrology ; LEACHING ; LESSIVAGE DU SOL ; LITHOLOGICAL SOIL TYPES ; LIXIVIACION ; METALLOIDE ; NAPPE SOUTERRAINE ; Nitrates ; NITROGEN FERTILIZERS ; NO METALES ; NONMETALS ; ONTARIO ; ORGANIC HALOGEN COMPOUNDS ; OXIGENO EN DISOLUCION ; OXYGENE EN DISSOLUTION ; POLLUTION DE L'EAU ; POLUCION DEL AGUA ; RECARGA DE AGUAS SUBTERRANEAS ; RECHARGE DE LA NAPPE ; SOIL MORPHOLOGICAL FEATURES ; SURFACE LAYERS ; THICKNESS ; TIPOS LITOLOGICOS DE SUELO ; TRAIT MORPHOLOGIQUE DU SOL ; TRITIO ; TRITIUM ; TYPE DE SOL LITHOLOGIQUE ; WATER POLLUTION ; Water, Underground</subject><ispartof>Ground water, 1998-01, Vol.36 (1), p.171-180</ispartof><rights>COPYRIGHT 1998 National Ground Water Association</rights><rights>Copyright Ground Water Publishing Company Jan/Feb 1998</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-a6621-6d772845b3a92a4d7c9ee4f993ce1ac2d42e39b26b8f7f4adf583f8ab46aa1253</citedby><cites>FETCH-LOGICAL-a6621-6d772845b3a92a4d7c9ee4f993ce1ac2d42e39b26b8f7f4adf583f8ab46aa1253</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></links><search><creatorcontrib>Johnston, C.T. (University of Waterloo, Waterloo, Ontario, Canada.)</creatorcontrib><creatorcontrib>Cook, P.G</creatorcontrib><creatorcontrib>Frape, S.K</creatorcontrib><creatorcontrib>Plummer, L.N</creatorcontrib><creatorcontrib>Busenberg, E</creatorcontrib><creatorcontrib>Blackport, R.J</creatorcontrib><title>Ground water age and nitrate distribution within a glacial aquifer beneath a thick unsaturated zone</title><title>Ground water</title><description>The impact on ground water quality from increasing fertilizer application rates over the past 40 years is evaluated within a glacial aquifer system beneath a thick unsaturated zone. Ground water ages within the aquifer could not be accurately determined from the measured distribution of 3H and as a result, chlorofluorocarbon (CFC) and 3H/3He dating techniques were applied. Beneath a 25 m thick unsaturated zone, ground water ages based on CFC-11 concentrations were greater than 3H/3He ground water ages by 6 to 10 years, due to the time lag associated with the diffusion of CFCs through the unsaturated zone. Using the corrected CFC-11 and 3H/3He ground water ages and the estimated travel time of 3H within the unsaturated zone, the approximate position of ground water recharged since the mid-1960s was determined. Nitrate concentrations within post mid-1960s recharge were generally elevated and near or above the drinking water limit of 10 mg-N/L. In comparison, pre mid-1960s recharge had nitrate concentrations 2.5 mg-N/L. The elevated NO3- concentrations in post mid-1960s recharge are attributed mainly to increasing fertilizer application rates between 1970 and the mid- to late 1980s. Anaerobic conditions suitable for denitrification are present within pre mid-1960s recharge indicating that removal of DO is a slow process taking tens of years. Over the next 10 to 20 years, nitrate concentrations at municipal well fields that are currently capturing aerobic ground water recharged near the mid-1960s are expected to increase because of the higher fertilizer application rates beginning in the 1970s and 1980s</description><subject>ABONOS NITROGENADOS</subject><subject>AGE DETERMINATION</subject><subject>AGUAS SUBTERRANEAS</subject><subject>Aquifers</subject><subject>CAPA FREATICA</subject><subject>CARACTERISTICAS MORFOLOGICAS SUELO</subject><subject>CHLORIDES</subject><subject>CHLOROFLUOROCARBONS</subject><subject>CHLORURE</subject><subject>CLORUROS</subject><subject>COMPOSE ORGANOHALOGENE</subject><subject>Composition</subject><subject>COMPUESTO ORGANICO HALOGENO</subject><subject>DETERMINACION DE LA EDAD</subject><subject>DETERMINATION DE L'AGE</subject><subject>DISSOLVED OXYGEN</subject><subject>EAU SOUTERRAINE</subject><subject>ENGRAIS AZOTE</subject><subject>Environmental aspects</subject><subject>EPAISSEUR</subject><subject>ESPESOR</subject><subject>Fertilizers</subject><subject>FLUVIOGLACIAL SOILS</subject><subject>GROUNDWATER</subject><subject>GROUNDWATER RECHARGE</subject><subject>GROUNDWATER TABLE</subject><subject>HELIUM</subject><subject>Hydrology</subject><subject>LEACHING</subject><subject>LESSIVAGE DU SOL</subject><subject>LITHOLOGICAL SOIL TYPES</subject><subject>LIXIVIACION</subject><subject>METALLOIDE</subject><subject>NAPPE SOUTERRAINE</subject><subject>Nitrates</subject><subject>NITROGEN FERTILIZERS</subject><subject>NO METALES</subject><subject>NONMETALS</subject><subject>ONTARIO</subject><subject>ORGANIC HALOGEN COMPOUNDS</subject><subject>OXIGENO EN DISOLUCION</subject><subject>OXYGENE EN DISSOLUTION</subject><subject>POLLUTION DE L'EAU</subject><subject>POLUCION DEL AGUA</subject><subject>RECARGA DE AGUAS SUBTERRANEAS</subject><subject>RECHARGE DE LA NAPPE</subject><subject>SOIL MORPHOLOGICAL FEATURES</subject><subject>SURFACE LAYERS</subject><subject>THICKNESS</subject><subject>TIPOS LITOLOGICOS DE SUELO</subject><subject>TRAIT MORPHOLOGIQUE DU SOL</subject><subject>TRITIO</subject><subject>TRITIUM</subject><subject>TYPE DE SOL LITHOLOGIQUE</subject><subject>WATER POLLUTION</subject><subject>Water, Underground</subject><issn>0017-467X</issn><issn>1745-6584</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1998</creationdate><recordtype>article</recordtype><recordid>eNqVkk1v1DAQhiMEEsvCT0CKeoBLs_gr_uCCVhW7RRQ40Gp7syaJnXqbTVo70W759XWUqkioAmEfLM8889ozepPkCKMFjuvDdoEFyzOeS7bASslFXyCMhFwcniWzx9TzZIYQFhnj4vJl8iqELUKIKqRmSbn23dBW6R5641OoTQrx1rrex0BaudB7Vwy969p07_or16aQ1g2UDpoUbgdnY1VhWgP9VcxEoLxOhzZAP4wCVfqra83r5IWFJpg3D-c8uVh9Pj85zc5-rL-cLM8y4JzgjFdCEMnygoIiwCpRKmOYVYqWBkNJKkYMVQXhhbTCMqhsLqmVUDAOgElO58n7SffGd7eDCb3euVCapoHWdEPQglEuOBYoku_-ShLMEGXk3yDmFBOGcQSP_gC33eDb2K4mlEtJVOxjnhxPUA2N0a61XRxzWcfxeWjioKyL4SVBjOScj49nT-BxV2bnyqf4jxNf-i4Eb6y-8W4H_k5jpEe76K0ePaFHT-jRLvrBLvoQiz9NxfsoevcflXq9WZ5jgX9_N5rGHB4VwF9rLqjI9eb7Wn_dKPptdYn0KvJvJ95Cp6H2LuiLn1FbIBmlJb0H3Yrfmg</recordid><startdate>199801</startdate><enddate>199801</enddate><creator>Johnston, C.T. (University of Waterloo, Waterloo, Ontario, Canada.)</creator><creator>Cook, P.G</creator><creator>Frape, S.K</creator><creator>Plummer, L.N</creator><creator>Busenberg, E</creator><creator>Blackport, R.J</creator><general>Blackwell Publishing Ltd</general><general>National Ground Water Association</general><general>Ground Water Publishing Company</general><scope>FBQ</scope><scope>BSCLL</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7QH</scope><scope>7ST</scope><scope>7UA</scope><scope>7X2</scope><scope>7X7</scope><scope>7XB</scope><scope>88E</scope><scope>88I</scope><scope>8FE</scope><scope>8FG</scope><scope>8FH</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>8G5</scope><scope>ABJCF</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BEC</scope><scope>BENPR</scope><scope>BGLVJ</scope><scope>BHPHI</scope><scope>BKSAR</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>F1W</scope><scope>FYUFA</scope><scope>GHDGH</scope><scope>GNUQQ</scope><scope>GUQSH</scope><scope>H96</scope><scope>H97</scope><scope>HCIFZ</scope><scope>K9.</scope><scope>L.G</scope><scope>L6V</scope><scope>M0K</scope><scope>M0S</scope><scope>M1P</scope><scope>M2O</scope><scope>M2P</scope><scope>M7S</scope><scope>MBDVC</scope><scope>PATMY</scope><scope>PCBAR</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PRINS</scope><scope>PTHSS</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>R05</scope><scope>S0X</scope><scope>SOI</scope><scope>7TV</scope><scope>7TG</scope><scope>KL.</scope><scope>8FD</scope><scope>FR3</scope><scope>KR7</scope></search><sort><creationdate>199801</creationdate><title>Ground water age and nitrate distribution within a glacial aquifer beneath a thick unsaturated zone</title><author>Johnston, C.T. (University of Waterloo, Waterloo, Ontario, Canada.) ; Cook, P.G ; Frape, S.K ; Plummer, L.N ; Busenberg, E ; Blackport, R.J</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-a6621-6d772845b3a92a4d7c9ee4f993ce1ac2d42e39b26b8f7f4adf583f8ab46aa1253</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1998</creationdate><topic>ABONOS NITROGENADOS</topic><topic>AGE DETERMINATION</topic><topic>AGUAS SUBTERRANEAS</topic><topic>Aquifers</topic><topic>CAPA FREATICA</topic><topic>CARACTERISTICAS MORFOLOGICAS SUELO</topic><topic>CHLORIDES</topic><topic>CHLOROFLUOROCARBONS</topic><topic>CHLORURE</topic><topic>CLORUROS</topic><topic>COMPOSE ORGANOHALOGENE</topic><topic>Composition</topic><topic>COMPUESTO ORGANICO HALOGENO</topic><topic>DETERMINACION DE LA EDAD</topic><topic>DETERMINATION DE L'AGE</topic><topic>DISSOLVED OXYGEN</topic><topic>EAU SOUTERRAINE</topic><topic>ENGRAIS AZOTE</topic><topic>Environmental aspects</topic><topic>EPAISSEUR</topic><topic>ESPESOR</topic><topic>Fertilizers</topic><topic>FLUVIOGLACIAL SOILS</topic><topic>GROUNDWATER</topic><topic>GROUNDWATER RECHARGE</topic><topic>GROUNDWATER TABLE</topic><topic>HELIUM</topic><topic>Hydrology</topic><topic>LEACHING</topic><topic>LESSIVAGE DU SOL</topic><topic>LITHOLOGICAL SOIL TYPES</topic><topic>LIXIVIACION</topic><topic>METALLOIDE</topic><topic>NAPPE SOUTERRAINE</topic><topic>Nitrates</topic><topic>NITROGEN FERTILIZERS</topic><topic>NO METALES</topic><topic>NONMETALS</topic><topic>ONTARIO</topic><topic>ORGANIC HALOGEN COMPOUNDS</topic><topic>OXIGENO EN DISOLUCION</topic><topic>OXYGENE EN DISSOLUTION</topic><topic>POLLUTION DE L'EAU</topic><topic>POLUCION DEL AGUA</topic><topic>RECARGA DE AGUAS SUBTERRANEAS</topic><topic>RECHARGE DE LA NAPPE</topic><topic>SOIL MORPHOLOGICAL FEATURES</topic><topic>SURFACE LAYERS</topic><topic>THICKNESS</topic><topic>TIPOS LITOLOGICOS DE SUELO</topic><topic>TRAIT MORPHOLOGIQUE DU SOL</topic><topic>TRITIO</topic><topic>TRITIUM</topic><topic>TYPE DE SOL LITHOLOGIQUE</topic><topic>WATER POLLUTION</topic><topic>Water, Underground</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Johnston, C.T. (University of Waterloo, Waterloo, Ontario, Canada.)</creatorcontrib><creatorcontrib>Cook, P.G</creatorcontrib><creatorcontrib>Frape, S.K</creatorcontrib><creatorcontrib>Plummer, L.N</creatorcontrib><creatorcontrib>Busenberg, E</creatorcontrib><creatorcontrib>Blackport, R.J</creatorcontrib><collection>AGRIS</collection><collection>Istex</collection><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Aqualine</collection><collection>Environment Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Agricultural Science Collection</collection><collection>Health Medical collection</collection><collection>ProQuest Central (purchase pre-March 2016)</collection><collection>Medical Database (Alumni Edition)</collection><collection>Science Database (Alumni Edition)</collection><collection>ProQuest SciTech Collection</collection><collection>ProQuest Technology Collection</collection><collection>ProQuest Natural Science Collection</collection><collection>Hospital Premium Collection</collection><collection>Hospital Premium Collection (Alumni Edition)</collection><collection>ProQuest Central (Alumni) (purchase pre-March 2016)</collection><collection>Research Library (Alumni Edition)</collection><collection>Materials Science & Engineering Collection</collection><collection>ProQuest Central (Alumni)</collection><collection>ProQuest One Sustainability</collection><collection>ProQuest Central</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>eLibrary</collection><collection>Proquest Central</collection><collection>Technology Collection</collection><collection>ProQuest Natural Science Collection</collection><collection>Earth, Atmospheric & Aquatic Science Collection</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Health Research Premium Collection</collection><collection>Health Research Premium Collection (Alumni)</collection><collection>ProQuest Central Student</collection><collection>Research Library Prep</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>SciTech Premium Collection (Proquest) (PQ_SDU_P3)</collection><collection>ProQuest Health & Medical Complete (Alumni)</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>ProQuest Engineering Collection</collection><collection>Agriculture Science Database</collection><collection>Health & Medical Collection (Alumni Edition)</collection><collection>PML(ProQuest Medical Library)</collection><collection>ProQuest research library</collection><collection>ProQuest Science Journals</collection><collection>Engineering Database</collection><collection>Research Library (Corporate)</collection><collection>Environmental Science Database</collection><collection>Earth, Atmospheric & Aquatic Science Database</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>ProQuest Central China</collection><collection>Engineering Collection</collection><collection>Environmental Science Collection</collection><collection>ProQuest Central Basic</collection><collection>University of Michigan</collection><collection>SIRS Editorial</collection><collection>Environment Abstracts</collection><collection>Pollution Abstracts</collection><collection>Meteorological & Geoastrophysical Abstracts</collection><collection>Meteorological & Geoastrophysical Abstracts - Academic</collection><collection>Technology Research Database</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><jtitle>Ground water</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Johnston, C.T. (University of Waterloo, Waterloo, Ontario, Canada.)</au><au>Cook, P.G</au><au>Frape, S.K</au><au>Plummer, L.N</au><au>Busenberg, E</au><au>Blackport, R.J</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Ground water age and nitrate distribution within a glacial aquifer beneath a thick unsaturated zone</atitle><jtitle>Ground water</jtitle><date>1998-01</date><risdate>1998</risdate><volume>36</volume><issue>1</issue><spage>171</spage><epage>180</epage><pages>171-180</pages><issn>0017-467X</issn><eissn>1745-6584</eissn><coden>GRWAAP</coden><abstract>The impact on ground water quality from increasing fertilizer application rates over the past 40 years is evaluated within a glacial aquifer system beneath a thick unsaturated zone. Ground water ages within the aquifer could not be accurately determined from the measured distribution of 3H and as a result, chlorofluorocarbon (CFC) and 3H/3He dating techniques were applied. Beneath a 25 m thick unsaturated zone, ground water ages based on CFC-11 concentrations were greater than 3H/3He ground water ages by 6 to 10 years, due to the time lag associated with the diffusion of CFCs through the unsaturated zone. Using the corrected CFC-11 and 3H/3He ground water ages and the estimated travel time of 3H within the unsaturated zone, the approximate position of ground water recharged since the mid-1960s was determined. Nitrate concentrations within post mid-1960s recharge were generally elevated and near or above the drinking water limit of 10 mg-N/L. In comparison, pre mid-1960s recharge had nitrate concentrations 2.5 mg-N/L. The elevated NO3- concentrations in post mid-1960s recharge are attributed mainly to increasing fertilizer application rates between 1970 and the mid- to late 1980s. Anaerobic conditions suitable for denitrification are present within pre mid-1960s recharge indicating that removal of DO is a slow process taking tens of years. Over the next 10 to 20 years, nitrate concentrations at municipal well fields that are currently capturing aerobic ground water recharged near the mid-1960s are expected to increase because of the higher fertilizer application rates beginning in the 1970s and 1980s</abstract><cop>Oxford, UK</cop><pub>Blackwell Publishing Ltd</pub><doi>10.1111/j.1745-6584.1998.tb01078.x</doi><tpages>10</tpages></addata></record> |
fulltext | fulltext |
identifier | ISSN: 0017-467X |
ispartof | Ground water, 1998-01, Vol.36 (1), p.171-180 |
issn | 0017-467X 1745-6584 |
language | eng |
recordid | cdi_proquest_miscellaneous_743676170 |
source | Wiley |
subjects | ABONOS NITROGENADOS AGE DETERMINATION AGUAS SUBTERRANEAS Aquifers CAPA FREATICA CARACTERISTICAS MORFOLOGICAS SUELO CHLORIDES CHLOROFLUOROCARBONS CHLORURE CLORUROS COMPOSE ORGANOHALOGENE Composition COMPUESTO ORGANICO HALOGENO DETERMINACION DE LA EDAD DETERMINATION DE L'AGE DISSOLVED OXYGEN EAU SOUTERRAINE ENGRAIS AZOTE Environmental aspects EPAISSEUR ESPESOR Fertilizers FLUVIOGLACIAL SOILS GROUNDWATER GROUNDWATER RECHARGE GROUNDWATER TABLE HELIUM Hydrology LEACHING LESSIVAGE DU SOL LITHOLOGICAL SOIL TYPES LIXIVIACION METALLOIDE NAPPE SOUTERRAINE Nitrates NITROGEN FERTILIZERS NO METALES NONMETALS ONTARIO ORGANIC HALOGEN COMPOUNDS OXIGENO EN DISOLUCION OXYGENE EN DISSOLUTION POLLUTION DE L'EAU POLUCION DEL AGUA RECARGA DE AGUAS SUBTERRANEAS RECHARGE DE LA NAPPE SOIL MORPHOLOGICAL FEATURES SURFACE LAYERS THICKNESS TIPOS LITOLOGICOS DE SUELO TRAIT MORPHOLOGIQUE DU SOL TRITIO TRITIUM TYPE DE SOL LITHOLOGIQUE WATER POLLUTION Water, Underground |
title | Ground water age and nitrate distribution within a glacial aquifer beneath a thick unsaturated zone |
url | http://sfxeu10.hosted.exlibrisgroup.com/loughborough?ctx_ver=Z39.88-2004&ctx_enc=info:ofi/enc:UTF-8&ctx_tim=2025-01-07T11%3A05%3A55IST&url_ver=Z39.88-2004&url_ctx_fmt=infofi/fmt:kev:mtx:ctx&rfr_id=info:sid/primo.exlibrisgroup.com:primo3-Article-gale_proqu&rft_val_fmt=info:ofi/fmt:kev:mtx:journal&rft.genre=article&rft.atitle=Ground%20water%20age%20and%20nitrate%20distribution%20within%20a%20glacial%20aquifer%20beneath%20a%20thick%20unsaturated%20zone&rft.jtitle=Ground%20water&rft.au=Johnston,%20C.T.%20(University%20of%20Waterloo,%20Waterloo,%20Ontario,%20Canada.)&rft.date=1998-01&rft.volume=36&rft.issue=1&rft.spage=171&rft.epage=180&rft.pages=171-180&rft.issn=0017-467X&rft.eissn=1745-6584&rft.coden=GRWAAP&rft_id=info:doi/10.1111/j.1745-6584.1998.tb01078.x&rft_dat=%3Cgale_proqu%3EA20425660%3C/gale_proqu%3E%3Cgrp_id%3Ecdi_FETCH-LOGICAL-a6621-6d772845b3a92a4d7c9ee4f993ce1ac2d42e39b26b8f7f4adf583f8ab46aa1253%3C/grp_id%3E%3Coa%3E%3C/oa%3E%3Curl%3E%3C/url%3E&rft_id=info:oai/&rft_pqid=236882999&rft_id=info:pmid/&rft_galeid=A20425660&rfr_iscdi=true |