The episodic acidification of Adirondack Lakes during snowmelt
Maximum values of acid neutralizing capacity (ANC) in Adirondack, New York lake outlets generally occur during summer and autumn. During spring snowmelt, transport of acidic water through acid-sensitive watersheds causes depression of upper lake water ANC. In some systems lake outlet ANC reaches neg...
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Veröffentlicht in: | Water resources research 1990-07, Vol.26 (7), p.1639-1647 |
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description | Maximum values of acid neutralizing capacity (ANC) in Adirondack, New York lake outlets generally occur during summer and autumn. During spring snowmelt, transport of acidic water through acid-sensitive watersheds causes depression of upper lake water ANC. In some systems lake outlet ANC reaches negative values. We examined outlet water chemistry from 11 Adirondack lakes during 1986 and 1987 snowmelts. In these lakes, SO4(2-) concentrations were diluted during snowmelt and did not depress ANC. For lakes with high baseline ANC values, springtime ANC depressions were primarily accompanied by basic cation dilution. For lakes with low baseline ANC, NO3- increases dominated ANC depressions. Lakes with intermediate baseline ANC were affected by both processes and exhibited larger ANC depressions. Ammonium dilution only affected wetland systems. A model predicting a linear relationship between outlet water ANC minima and autumn ANC was inappropriate. To assess watershed response to episodic acidification, hydrologic flow, paths must be considered |
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(Syracuse University, Syracuse, NY) ; Driscoll, C.T. Jr ; Van Dreason, R ; Yatsko, C.P</creator><creatorcontrib>Schaefer, D.A. (Syracuse University, Syracuse, NY) ; Driscoll, C.T. Jr ; Van Dreason, R ; Yatsko, C.P</creatorcontrib><description>Maximum values of acid neutralizing capacity (ANC) in Adirondack, New York lake outlets generally occur during summer and autumn. During spring snowmelt, transport of acidic water through acid-sensitive watersheds causes depression of upper lake water ANC. In some systems lake outlet ANC reaches negative values. We examined outlet water chemistry from 11 Adirondack lakes during 1986 and 1987 snowmelts. In these lakes, SO4(2-) concentrations were diluted during snowmelt and did not depress ANC. For lakes with high baseline ANC values, springtime ANC depressions were primarily accompanied by basic cation dilution. For lakes with low baseline ANC, NO3- increases dominated ANC depressions. Lakes with intermediate baseline ANC were affected by both processes and exhibited larger ANC depressions. Ammonium dilution only affected wetland systems. A model predicting a linear relationship between outlet water ANC minima and autumn ANC was inappropriate. 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(Syracuse University, Syracuse, NY)</creatorcontrib><creatorcontrib>Driscoll, C.T. Jr</creatorcontrib><creatorcontrib>Van Dreason, R</creatorcontrib><creatorcontrib>Yatsko, C.P</creatorcontrib><title>The episodic acidification of Adirondack Lakes during snowmelt</title><title>Water resources research</title><addtitle>Water Resour. Res</addtitle><description>Maximum values of acid neutralizing capacity (ANC) in Adirondack, New York lake outlets generally occur during summer and autumn. During spring snowmelt, transport of acidic water through acid-sensitive watersheds causes depression of upper lake water ANC. In some systems lake outlet ANC reaches negative values. We examined outlet water chemistry from 11 Adirondack lakes during 1986 and 1987 snowmelts. In these lakes, SO4(2-) concentrations were diluted during snowmelt and did not depress ANC. For lakes with high baseline ANC values, springtime ANC depressions were primarily accompanied by basic cation dilution. For lakes with low baseline ANC, NO3- increases dominated ANC depressions. Lakes with intermediate baseline ANC were affected by both processes and exhibited larger ANC depressions. Ammonium dilution only affected wetland systems. A model predicting a linear relationship between outlet water ANC minima and autumn ANC was inappropriate. To assess watershed response to episodic acidification, hydrologic flow, paths must be considered</description><subject>01 COAL, LIGNITE, AND PEAT</subject><subject>010900 - Coal, Lignite, & Peat- Environmental Aspects</subject><subject>540320 - Environment, Aquatic- Chemicals Monitoring & Transport- (1990-)</subject><subject>ACID NEUTRALIZING CAPACITY</subject><subject>ACID RAIN</subject><subject>ACIDEZ</subject><subject>ACIDIFICATION</subject><subject>ACIDITE</subject><subject>ADIRONDACK MOUNTAINS</subject><subject>AGUA</subject><subject>AIR POLLUTION</subject><subject>APPALACHIAN MOUNTAINS</subject><subject>ATMOSPHERIC PRECIPITATIONS</subject><subject>CALIDAD DEL AGUA</subject><subject>CHEMISTRY</subject><subject>COMPOSICION</subject><subject>COMPOSITION</subject><subject>DESARROLLO ESTACIONAL</subject><subject>DEVELOPED COUNTRIES</subject><subject>DEVELOPPEMENT SAISONNIER</subject><subject>EAU</subject><subject>ECOLOGICAL CONCENTRATION</subject><subject>ENVIRONMENTAL EFFECTS</subject><subject>ENVIRONMENTAL SCIENCES</subject><subject>FEDERAL REGION II</subject><subject>HYDROLOGY</subject><subject>LAC</subject><subject>LAGOS</subject><subject>LAKES</subject><subject>MELTING</subject><subject>MONITORING</subject><subject>MOUNTAINS</subject><subject>NEW YORK</subject><subject>NITRATES</subject><subject>NITROGEN COMPOUNDS</subject><subject>NORTH AMERICA</subject><subject>NUEVA YORK</subject><subject>OXYGEN COMPOUNDS</subject><subject>PHASE TRANSFORMATIONS</subject><subject>POLLUTION</subject><subject>QUALITE DE L'EAU</subject><subject>RAIN</subject><subject>SEASONAL VARIATIONS</subject><subject>SNOW</subject><subject>SULFATES</subject><subject>SULFUR COMPOUNDS</subject><subject>SURFACE WATERS</subject><subject>USA</subject><subject>VARIATIONS</subject><subject>WATER CHEMISTRY</subject><subject>WATER POLLUTION</subject><subject>WATERSHEDS</subject><issn>0043-1397</issn><issn>1944-7973</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1990</creationdate><recordtype>article</recordtype><recordid>eNqFkU1LxDAQhoMouK6eBU_Fg7fqJGmTzUXQ9ZtFUVc9hjQfGrfbrEkX9d9bqXjw4mkYeJ6Z4R2EtjHsYyDi4OkOCPMAfAGYUbGCBlgURc4Fp6toAFDQHFPB19FGSq8AuCgZH6DD6YvN7MKnYLzOlPbGO69V60OTBZcdGR9DY5SeZRM1sykzy-ib5yw14X1u63YTrTlVJ7v1U4fo4ex0Or7IJzfnl-OjSa4LxkROGWclo0SAMhWpMBcEOOOFM8YZwBVo4UbVyFhNR5hXQHTJROH0iBnOaOnoEO32c0NqvUzat1a_6NA0VreypKRghHTQXg8tYnhb2tTKuU_a1rVqbFgmiSmnpFvbgQc9qGNIKVonF9HPVfyUGOR3mPJPmJ1R9sa7r-3nf3jXj-9KDN9e3ns-tfbj11NxJrs7eCmfrs_lyfT4eHzFH-Vtx-_0vFNBqufok3y4F93vBMb0CzPDjZo</recordid><startdate>199007</startdate><enddate>199007</enddate><creator>Schaefer, D.A. 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Jr ; Van Dreason, R ; Yatsko, C.P</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4669-3676563290adb2b179207674fddfd01b0c9f8b8dec3817b02c5694fc86d7635f3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1990</creationdate><topic>01 COAL, LIGNITE, AND PEAT</topic><topic>010900 - Coal, Lignite, & Peat- Environmental Aspects</topic><topic>540320 - Environment, Aquatic- Chemicals Monitoring & Transport- (1990-)</topic><topic>ACID NEUTRALIZING CAPACITY</topic><topic>ACID RAIN</topic><topic>ACIDEZ</topic><topic>ACIDIFICATION</topic><topic>ACIDITE</topic><topic>ADIRONDACK MOUNTAINS</topic><topic>AGUA</topic><topic>AIR POLLUTION</topic><topic>APPALACHIAN MOUNTAINS</topic><topic>ATMOSPHERIC PRECIPITATIONS</topic><topic>CALIDAD DEL AGUA</topic><topic>CHEMISTRY</topic><topic>COMPOSICION</topic><topic>COMPOSITION</topic><topic>DESARROLLO ESTACIONAL</topic><topic>DEVELOPED COUNTRIES</topic><topic>DEVELOPPEMENT SAISONNIER</topic><topic>EAU</topic><topic>ECOLOGICAL CONCENTRATION</topic><topic>ENVIRONMENTAL EFFECTS</topic><topic>ENVIRONMENTAL SCIENCES</topic><topic>FEDERAL REGION II</topic><topic>HYDROLOGY</topic><topic>LAC</topic><topic>LAGOS</topic><topic>LAKES</topic><topic>MELTING</topic><topic>MONITORING</topic><topic>MOUNTAINS</topic><topic>NEW YORK</topic><topic>NITRATES</topic><topic>NITROGEN COMPOUNDS</topic><topic>NORTH AMERICA</topic><topic>NUEVA YORK</topic><topic>OXYGEN COMPOUNDS</topic><topic>PHASE TRANSFORMATIONS</topic><topic>POLLUTION</topic><topic>QUALITE DE L'EAU</topic><topic>RAIN</topic><topic>SEASONAL VARIATIONS</topic><topic>SNOW</topic><topic>SULFATES</topic><topic>SULFUR COMPOUNDS</topic><topic>SURFACE WATERS</topic><topic>USA</topic><topic>VARIATIONS</topic><topic>WATER CHEMISTRY</topic><topic>WATER POLLUTION</topic><topic>WATERSHEDS</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Schaefer, D.A. (Syracuse University, Syracuse, NY)</creatorcontrib><creatorcontrib>Driscoll, C.T. Jr</creatorcontrib><creatorcontrib>Van Dreason, R</creatorcontrib><creatorcontrib>Yatsko, C.P</creatorcontrib><collection>AGRIS</collection><collection>Istex</collection><collection>CrossRef</collection><collection>Aqualine</collection><collection>OSTI.GOV</collection><jtitle>Water resources research</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Schaefer, D.A. (Syracuse University, Syracuse, NY)</au><au>Driscoll, C.T. Jr</au><au>Van Dreason, R</au><au>Yatsko, C.P</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>The episodic acidification of Adirondack Lakes during snowmelt</atitle><jtitle>Water resources research</jtitle><addtitle>Water Resour. Res</addtitle><date>1990-07</date><risdate>1990</risdate><volume>26</volume><issue>7</issue><spage>1639</spage><epage>1647</epage><pages>1639-1647</pages><issn>0043-1397</issn><eissn>1944-7973</eissn><abstract>Maximum values of acid neutralizing capacity (ANC) in Adirondack, New York lake outlets generally occur during summer and autumn. During spring snowmelt, transport of acidic water through acid-sensitive watersheds causes depression of upper lake water ANC. In some systems lake outlet ANC reaches negative values. We examined outlet water chemistry from 11 Adirondack lakes during 1986 and 1987 snowmelts. In these lakes, SO4(2-) concentrations were diluted during snowmelt and did not depress ANC. For lakes with high baseline ANC values, springtime ANC depressions were primarily accompanied by basic cation dilution. For lakes with low baseline ANC, NO3- increases dominated ANC depressions. Lakes with intermediate baseline ANC were affected by both processes and exhibited larger ANC depressions. Ammonium dilution only affected wetland systems. A model predicting a linear relationship between outlet water ANC minima and autumn ANC was inappropriate. To assess watershed response to episodic acidification, hydrologic flow, paths must be considered</abstract><cop>United States</cop><pub>Blackwell Publishing Ltd</pub><doi>10.1029/WR026i007p01639</doi><tpages>9</tpages></addata></record> |
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subjects | 01 COAL, LIGNITE, AND PEAT 010900 - Coal, Lignite, & Peat- Environmental Aspects 540320 - Environment, Aquatic- Chemicals Monitoring & Transport- (1990-) ACID NEUTRALIZING CAPACITY ACID RAIN ACIDEZ ACIDIFICATION ACIDITE ADIRONDACK MOUNTAINS AGUA AIR POLLUTION APPALACHIAN MOUNTAINS ATMOSPHERIC PRECIPITATIONS CALIDAD DEL AGUA CHEMISTRY COMPOSICION COMPOSITION DESARROLLO ESTACIONAL DEVELOPED COUNTRIES DEVELOPPEMENT SAISONNIER EAU ECOLOGICAL CONCENTRATION ENVIRONMENTAL EFFECTS ENVIRONMENTAL SCIENCES FEDERAL REGION II HYDROLOGY LAC LAGOS LAKES MELTING MONITORING MOUNTAINS NEW YORK NITRATES NITROGEN COMPOUNDS NORTH AMERICA NUEVA YORK OXYGEN COMPOUNDS PHASE TRANSFORMATIONS POLLUTION QUALITE DE L'EAU RAIN SEASONAL VARIATIONS SNOW SULFATES SULFUR COMPOUNDS SURFACE WATERS USA VARIATIONS WATER CHEMISTRY WATER POLLUTION WATERSHEDS |
title | The episodic acidification of Adirondack Lakes during snowmelt |
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