impacts of road deicing salt on the demography of vernal pool-breeding amphibians
Deicing agents, primarily road salt, are applied to roads in 26 states in the United States and in a number of European countries, yet the scale of impacts of road salt on aquatic organisms remains largely under-studied. The issue is germane to amphibian conservation because both adult and larval am...
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Veröffentlicht in: | Ecological applications 2008-04, Vol.18 (3), p.724-734 |
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description | Deicing agents, primarily road salt, are applied to roads in 26 states in the United States and in a number of European countries, yet the scale of impacts of road salt on aquatic organisms remains largely under-studied. The issue is germane to amphibian conservation because both adult and larval amphibians are known to be particularly sensitive to changes in their osmolar environments. In this study, we combined survey, experimental, and demographic modeling approaches to evaluate the possible effects of road salt on two common vernal-pond-breeding amphibian species, the spotted salamander (Ambystoma maculatum) and the wood frog (Rana sylvatica). We found that in the Adirondack Mountain Region of New York (USA), road salt traveled up to 172 m from the highway into wetlands. Surveys showed that egg mass densities of spotted salamanders (A. maculatum) and wood frogs (R. sylvatica) were two times higher in forest pools than roadside pools, but this pattern was better explained by road proximity than by increased salinity. Experiments demonstrated that embryonic and larval survival were reduced at moderate (500 µS) and high conductivities (3000 µS) in A. maculatum and at high conductivities in R. sylvatica. Demographic models suggest that such egg and larval stage effects of salt may have important impacts on populations near roads, particularly in the case of A. maculatum, for which salt exposure may lead to local extinction. For both species, the effect of road salt was dependent upon the strength of larval density dependence and declined rapidly with distance from the roadside, with the greatest negative effects being limited to within 50 m. Based on this evidence, we argue that efforts to protect local populations of A. maculatum and R. sylvatica in roadside wetlands should, in part, be aimed at reducing application of road salt near wetlands with high conductivity levels. |
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The issue is germane to amphibian conservation because both adult and larval amphibians are known to be particularly sensitive to changes in their osmolar environments. In this study, we combined survey, experimental, and demographic modeling approaches to evaluate the possible effects of road salt on two common vernal-pond-breeding amphibian species, the spotted salamander (Ambystoma maculatum) and the wood frog (Rana sylvatica). We found that in the Adirondack Mountain Region of New York (USA), road salt traveled up to 172 m from the highway into wetlands. Surveys showed that egg mass densities of spotted salamanders (A. maculatum) and wood frogs (R. sylvatica) were two times higher in forest pools than roadside pools, but this pattern was better explained by road proximity than by increased salinity. Experiments demonstrated that embryonic and larval survival were reduced at moderate (500 µS) and high conductivities (3000 µS) in A. maculatum and at high conductivities in R. sylvatica. Demographic models suggest that such egg and larval stage effects of salt may have important impacts on populations near roads, particularly in the case of A. maculatum, for which salt exposure may lead to local extinction. For both species, the effect of road salt was dependent upon the strength of larval density dependence and declined rapidly with distance from the roadside, with the greatest negative effects being limited to within 50 m. Based on this evidence, we argue that efforts to protect local populations of A. maculatum and R. sylvatica in roadside wetlands should, in part, be aimed at reducing application of road salt near wetlands with high conductivity levels.</description><identifier>ISSN: 1051-0761</identifier><identifier>EISSN: 1939-5582</identifier><identifier>DOI: 10.1890/07-1644.1</identifier><identifier>PMID: 18488630</identifier><language>eng</language><publisher>United States: Ecological Society of America</publisher><subject>Ambystoma ; Ambystoma - physiology ; Ambystoma maculatum ; amphibian ; Amphibians ; Animals ; aquatic habitat ; Caudata ; Deicing ; deicing agents ; deicing salt ; demography ; Egg masses ; environmental degradation ; environmental impact ; Forest roads ; Frogs ; Ice ; Larva ; Larvae ; Larval development ; limitation analysis ; Metamorphosis, Biological ; Ponds ; population ecology ; Rana ; Rana sylvatica ; Ranidae - physiology ; Reproduction - drug effects ; Reproduction - physiology ; road deicing salt ; road effect zone ; Roadside ; Salts ; Sodium Chloride - toxicity ; spotted salamander ; survival ; Time Factors ; Transportation ; vernal pool ; Water - chemistry ; Water Pollutants, Chemical - toxicity ; water pollution ; Water Pollution, Chemical - prevention & control ; wetlands ; wood frog</subject><ispartof>Ecological applications, 2008-04, Vol.18 (3), p.724-734</ispartof><rights>Copyright 2008 Ecological Society of America</rights><rights>2008 by the Ecological Society of America</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4054-dde69560b0c99c5c6d69f3b43f25a23b0ab3996da8f461a71e5b14e9a85253243</citedby><cites>FETCH-LOGICAL-c4054-dde69560b0c99c5c6d69f3b43f25a23b0ab3996da8f461a71e5b14e9a85253243</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/40062181$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/40062181$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,776,780,799,1411,27901,27902,45550,45551,57992,58225</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/18488630$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Karraker, N.E</creatorcontrib><creatorcontrib>Gibbs, J.P</creatorcontrib><creatorcontrib>Vonesh, J.R</creatorcontrib><title>impacts of road deicing salt on the demography of vernal pool-breeding amphibians</title><title>Ecological applications</title><addtitle>Ecol Appl</addtitle><description>Deicing agents, primarily road salt, are applied to roads in 26 states in the United States and in a number of European countries, yet the scale of impacts of road salt on aquatic organisms remains largely under-studied. The issue is germane to amphibian conservation because both adult and larval amphibians are known to be particularly sensitive to changes in their osmolar environments. In this study, we combined survey, experimental, and demographic modeling approaches to evaluate the possible effects of road salt on two common vernal-pond-breeding amphibian species, the spotted salamander (Ambystoma maculatum) and the wood frog (Rana sylvatica). We found that in the Adirondack Mountain Region of New York (USA), road salt traveled up to 172 m from the highway into wetlands. Surveys showed that egg mass densities of spotted salamanders (A. maculatum) and wood frogs (R. sylvatica) were two times higher in forest pools than roadside pools, but this pattern was better explained by road proximity than by increased salinity. Experiments demonstrated that embryonic and larval survival were reduced at moderate (500 µS) and high conductivities (3000 µS) in A. maculatum and at high conductivities in R. sylvatica. Demographic models suggest that such egg and larval stage effects of salt may have important impacts on populations near roads, particularly in the case of A. maculatum, for which salt exposure may lead to local extinction. For both species, the effect of road salt was dependent upon the strength of larval density dependence and declined rapidly with distance from the roadside, with the greatest negative effects being limited to within 50 m. Based on this evidence, we argue that efforts to protect local populations of A. maculatum and R. sylvatica in roadside wetlands should, in part, be aimed at reducing application of road salt near wetlands with high conductivity levels.</description><subject>Ambystoma</subject><subject>Ambystoma - physiology</subject><subject>Ambystoma maculatum</subject><subject>amphibian</subject><subject>Amphibians</subject><subject>Animals</subject><subject>aquatic habitat</subject><subject>Caudata</subject><subject>Deicing</subject><subject>deicing agents</subject><subject>deicing salt</subject><subject>demography</subject><subject>Egg masses</subject><subject>environmental degradation</subject><subject>environmental impact</subject><subject>Forest roads</subject><subject>Frogs</subject><subject>Ice</subject><subject>Larva</subject><subject>Larvae</subject><subject>Larval development</subject><subject>limitation analysis</subject><subject>Metamorphosis, Biological</subject><subject>Ponds</subject><subject>population ecology</subject><subject>Rana</subject><subject>Rana sylvatica</subject><subject>Ranidae - physiology</subject><subject>Reproduction - drug effects</subject><subject>Reproduction - physiology</subject><subject>road deicing salt</subject><subject>road effect zone</subject><subject>Roadside</subject><subject>Salts</subject><subject>Sodium Chloride - toxicity</subject><subject>spotted salamander</subject><subject>survival</subject><subject>Time Factors</subject><subject>Transportation</subject><subject>vernal pool</subject><subject>Water - chemistry</subject><subject>Water Pollutants, Chemical - toxicity</subject><subject>water pollution</subject><subject>Water Pollution, Chemical - prevention & control</subject><subject>wetlands</subject><subject>wood frog</subject><issn>1051-0761</issn><issn>1939-5582</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2008</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp1kM1u1DAUha0KREth0QcAskJikXL9G3tZVaWtVAmq0rV1kzgzrpI42JmieXscMoJVvbF1_Z1zrg4hZxTOqTbwFaqSKiHO6RE5oYabUkrNXuU3SFpCpegxeZvSE-TDGHtDjqkWWisOJ-TeDxM2cypCV8SAbdE63_hxUyTs5yKMxbx1eTaETcRpu1-wZxdH7IsphL6so3PtguMwbX3tcUzvyOsO--TeH-5T8vjt6uflTXn3_fr28uKubARIUbatU0YqqKExppGNapXpeC14xyQyXgPW3BjVou6EolhRJ2sqnEEtmeRM8FPyefWdYvi1c2m2g0-N63scXdgly0BnPdUZ_LKCTQwpRdfZKfoB495SsEt_Fiq79GdpZj8eTHf14Nr_5KGwDIgV-O17t3_ZyV5d_GAAOudXf5f9sMqe0hziP5kAUIzqJffT-t9hsLiJPtnHBwaUZwtTAef8D7Bsi5k</recordid><startdate>200804</startdate><enddate>200804</enddate><creator>Karraker, N.E</creator><creator>Gibbs, J.P</creator><creator>Vonesh, J.R</creator><general>Ecological Society of America</general><scope>FBQ</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>7SN</scope><scope>7ST</scope><scope>7U6</scope><scope>C1K</scope><scope>F1W</scope><scope>H95</scope><scope>L.G</scope></search><sort><creationdate>200804</creationdate><title>impacts of road deicing salt on the demography of vernal pool-breeding amphibians</title><author>Karraker, N.E ; Gibbs, J.P ; Vonesh, J.R</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4054-dde69560b0c99c5c6d69f3b43f25a23b0ab3996da8f461a71e5b14e9a85253243</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2008</creationdate><topic>Ambystoma</topic><topic>Ambystoma - physiology</topic><topic>Ambystoma maculatum</topic><topic>amphibian</topic><topic>Amphibians</topic><topic>Animals</topic><topic>aquatic habitat</topic><topic>Caudata</topic><topic>Deicing</topic><topic>deicing agents</topic><topic>deicing salt</topic><topic>demography</topic><topic>Egg masses</topic><topic>environmental degradation</topic><topic>environmental impact</topic><topic>Forest roads</topic><topic>Frogs</topic><topic>Ice</topic><topic>Larva</topic><topic>Larvae</topic><topic>Larval development</topic><topic>limitation analysis</topic><topic>Metamorphosis, Biological</topic><topic>Ponds</topic><topic>population ecology</topic><topic>Rana</topic><topic>Rana sylvatica</topic><topic>Ranidae - physiology</topic><topic>Reproduction - drug effects</topic><topic>Reproduction - physiology</topic><topic>road deicing salt</topic><topic>road effect zone</topic><topic>Roadside</topic><topic>Salts</topic><topic>Sodium Chloride - toxicity</topic><topic>spotted salamander</topic><topic>survival</topic><topic>Time Factors</topic><topic>Transportation</topic><topic>vernal pool</topic><topic>Water - chemistry</topic><topic>Water Pollutants, Chemical - toxicity</topic><topic>water pollution</topic><topic>Water Pollution, Chemical - prevention & control</topic><topic>wetlands</topic><topic>wood frog</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Karraker, N.E</creatorcontrib><creatorcontrib>Gibbs, J.P</creatorcontrib><creatorcontrib>Vonesh, J.R</creatorcontrib><collection>AGRIS</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Environment Abstracts</collection><collection>Sustainability Science Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 1: Biological Sciences & Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>Ecological applications</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Karraker, N.E</au><au>Gibbs, J.P</au><au>Vonesh, J.R</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>impacts of road deicing salt on the demography of vernal pool-breeding amphibians</atitle><jtitle>Ecological applications</jtitle><addtitle>Ecol Appl</addtitle><date>2008-04</date><risdate>2008</risdate><volume>18</volume><issue>3</issue><spage>724</spage><epage>734</epage><pages>724-734</pages><issn>1051-0761</issn><eissn>1939-5582</eissn><abstract>Deicing agents, primarily road salt, are applied to roads in 26 states in the United States and in a number of European countries, yet the scale of impacts of road salt on aquatic organisms remains largely under-studied. The issue is germane to amphibian conservation because both adult and larval amphibians are known to be particularly sensitive to changes in their osmolar environments. In this study, we combined survey, experimental, and demographic modeling approaches to evaluate the possible effects of road salt on two common vernal-pond-breeding amphibian species, the spotted salamander (Ambystoma maculatum) and the wood frog (Rana sylvatica). We found that in the Adirondack Mountain Region of New York (USA), road salt traveled up to 172 m from the highway into wetlands. Surveys showed that egg mass densities of spotted salamanders (A. maculatum) and wood frogs (R. sylvatica) were two times higher in forest pools than roadside pools, but this pattern was better explained by road proximity than by increased salinity. Experiments demonstrated that embryonic and larval survival were reduced at moderate (500 µS) and high conductivities (3000 µS) in A. maculatum and at high conductivities in R. sylvatica. Demographic models suggest that such egg and larval stage effects of salt may have important impacts on populations near roads, particularly in the case of A. maculatum, for which salt exposure may lead to local extinction. For both species, the effect of road salt was dependent upon the strength of larval density dependence and declined rapidly with distance from the roadside, with the greatest negative effects being limited to within 50 m. Based on this evidence, we argue that efforts to protect local populations of A. maculatum and R. sylvatica in roadside wetlands should, in part, be aimed at reducing application of road salt near wetlands with high conductivity levels.</abstract><cop>United States</cop><pub>Ecological Society of America</pub><pmid>18488630</pmid><doi>10.1890/07-1644.1</doi><tpages>11</tpages></addata></record> |
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subjects | Ambystoma Ambystoma - physiology Ambystoma maculatum amphibian Amphibians Animals aquatic habitat Caudata Deicing deicing agents deicing salt demography Egg masses environmental degradation environmental impact Forest roads Frogs Ice Larva Larvae Larval development limitation analysis Metamorphosis, Biological Ponds population ecology Rana Rana sylvatica Ranidae - physiology Reproduction - drug effects Reproduction - physiology road deicing salt road effect zone Roadside Salts Sodium Chloride - toxicity spotted salamander survival Time Factors Transportation vernal pool Water - chemistry Water Pollutants, Chemical - toxicity water pollution Water Pollution, Chemical - prevention & control wetlands wood frog |
title | impacts of road deicing salt on the demography of vernal pool-breeding amphibians |
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