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Scale-specific land cover thresholds for conservation of stream invertebrate communities in agricultural landscapes
Context In agricultural landscapes, riparian forests are used as a management tool to protect stream ecosystems from agricultural activities. However, the ability of managers to target stream protection actions is limited by incomplete knowledge of scale-specific effects of agriculture in riparian c...
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Published in: | Landscape ecology 2018-12, Vol.33 (12), p.2239-2252 |
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container_title | Landscape ecology |
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creator | Grimstead, Jeremy P. Krynak, Edward M. Yates, Adam G. |
description | Context
In agricultural landscapes, riparian forests are used as a management tool to protect stream ecosystems from agricultural activities. However, the ability of managers to target stream protection actions is limited by incomplete knowledge of scale-specific effects of agriculture in riparian corridor and catchment areas.
Objectives
We evaluated scale-specific effects of agricultural cover in riparian corridor and catchment areas on stream benthic macroinvertebrate (BMI) communities to develop cover targets for agricultural landscapes.
Methods
Sixty-eight streams assigned to three experimental treatments (Forested Riparian, Agricultural Riparian, Agricultural Catchment) were sampled for BMIs. Ordination and segmented regression were used to assess impacts of agriculture on BMI communities and detect thresholds for BMI community metrics.
Results
BMI communities were not associated with catchment agricultural cover where the riparian corridor was forested, but were associated with variation in catchment agriculture where riparian forests had been converted to agriculture. Trait-based metrics showed threshold responses at greater than 70% agricultural cover in the catchment. Increasing agriculture in the riparian corridor was associated with less diverse and more tolerant BMI communities. Eight metrics exhibited threshold responses ranging from 45 to 75% agriculture in the riparian corridor.
Conclusions
Riparian forest effectively buffered streams from agricultural activity even where catchment agriculture exceeds 80%. We recommend managers prioritize protection of forested riparian corridors and that restore riparian corridors where agricultural cover is near identified thresholds be a secondary priority. Adoption of catchment management actions should be effective where the riparian corridor has been converted to agriculture. |
doi_str_mv | 10.1007/s10980-018-0738-5 |
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In agricultural landscapes, riparian forests are used as a management tool to protect stream ecosystems from agricultural activities. However, the ability of managers to target stream protection actions is limited by incomplete knowledge of scale-specific effects of agriculture in riparian corridor and catchment areas.
Objectives
We evaluated scale-specific effects of agricultural cover in riparian corridor and catchment areas on stream benthic macroinvertebrate (BMI) communities to develop cover targets for agricultural landscapes.
Methods
Sixty-eight streams assigned to three experimental treatments (Forested Riparian, Agricultural Riparian, Agricultural Catchment) were sampled for BMIs. Ordination and segmented regression were used to assess impacts of agriculture on BMI communities and detect thresholds for BMI community metrics.
Results
BMI communities were not associated with catchment agricultural cover where the riparian corridor was forested, but were associated with variation in catchment agriculture where riparian forests had been converted to agriculture. Trait-based metrics showed threshold responses at greater than 70% agricultural cover in the catchment. Increasing agriculture in the riparian corridor was associated with less diverse and more tolerant BMI communities. Eight metrics exhibited threshold responses ranging from 45 to 75% agriculture in the riparian corridor.
Conclusions
Riparian forest effectively buffered streams from agricultural activity even where catchment agriculture exceeds 80%. We recommend managers prioritize protection of forested riparian corridors and that restore riparian corridors where agricultural cover is near identified thresholds be a secondary priority. Adoption of catchment management actions should be effective where the riparian corridor has been converted to agriculture.</description><identifier>ISSN: 0921-2973</identifier><identifier>EISSN: 1572-9761</identifier><identifier>DOI: 10.1007/s10980-018-0738-5</identifier><language>eng</language><publisher>Dordrecht: Springer Netherlands</publisher><subject>Agricultural ecosystems ; Agricultural land ; Agricultural practices ; Agricultural watersheds ; Agriculture ; Biomedical and Life Sciences ; Catchment areas ; Communities ; Corridors ; Ecology ; Ecosystem management ; Environmental Management ; Forest management ; Forest protection ; Land conservation ; Land cover ; Landscape Ecology ; Landscape preservation ; Landscape/Regional and Urban Planning ; Life Sciences ; Macroinvertebrates ; Nature Conservation ; Ordination ; Research Article ; Riparian forests ; Strategic management ; Streams ; Sustainable Development ; Thresholds</subject><ispartof>Landscape ecology, 2018-12, Vol.33 (12), p.2239-2252</ispartof><rights>Springer Nature B.V. 2018</rights><rights>Landscape Ecology is a copyright of Springer, (2018). All Rights Reserved.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c316t-f51c2857fe32cfa27bc9062ccbb5c30e984ca0027051ba4b5fd375a3408e0b6b3</citedby><cites>FETCH-LOGICAL-c316t-f51c2857fe32cfa27bc9062ccbb5c30e984ca0027051ba4b5fd375a3408e0b6b3</cites><orcidid>0000-0002-2239-9046</orcidid></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>Grimstead, Jeremy P.</creatorcontrib><creatorcontrib>Krynak, Edward M.</creatorcontrib><creatorcontrib>Yates, Adam G.</creatorcontrib><title>Scale-specific land cover thresholds for conservation of stream invertebrate communities in agricultural landscapes</title><title>Landscape ecology</title><addtitle>Landscape Ecol</addtitle><description>Context
In agricultural landscapes, riparian forests are used as a management tool to protect stream ecosystems from agricultural activities. However, the ability of managers to target stream protection actions is limited by incomplete knowledge of scale-specific effects of agriculture in riparian corridor and catchment areas.
Objectives
We evaluated scale-specific effects of agricultural cover in riparian corridor and catchment areas on stream benthic macroinvertebrate (BMI) communities to develop cover targets for agricultural landscapes.
Methods
Sixty-eight streams assigned to three experimental treatments (Forested Riparian, Agricultural Riparian, Agricultural Catchment) were sampled for BMIs. Ordination and segmented regression were used to assess impacts of agriculture on BMI communities and detect thresholds for BMI community metrics.
Results
BMI communities were not associated with catchment agricultural cover where the riparian corridor was forested, but were associated with variation in catchment agriculture where riparian forests had been converted to agriculture. Trait-based metrics showed threshold responses at greater than 70% agricultural cover in the catchment. Increasing agriculture in the riparian corridor was associated with less diverse and more tolerant BMI communities. Eight metrics exhibited threshold responses ranging from 45 to 75% agriculture in the riparian corridor.
Conclusions
Riparian forest effectively buffered streams from agricultural activity even where catchment agriculture exceeds 80%. We recommend managers prioritize protection of forested riparian corridors and that restore riparian corridors where agricultural cover is near identified thresholds be a secondary priority. Adoption of catchment management actions should be effective where the riparian corridor has been converted to agriculture.</description><subject>Agricultural ecosystems</subject><subject>Agricultural land</subject><subject>Agricultural practices</subject><subject>Agricultural watersheds</subject><subject>Agriculture</subject><subject>Biomedical and Life Sciences</subject><subject>Catchment areas</subject><subject>Communities</subject><subject>Corridors</subject><subject>Ecology</subject><subject>Ecosystem management</subject><subject>Environmental Management</subject><subject>Forest management</subject><subject>Forest protection</subject><subject>Land conservation</subject><subject>Land cover</subject><subject>Landscape Ecology</subject><subject>Landscape preservation</subject><subject>Landscape/Regional and Urban Planning</subject><subject>Life Sciences</subject><subject>Macroinvertebrates</subject><subject>Nature Conservation</subject><subject>Ordination</subject><subject>Research Article</subject><subject>Riparian forests</subject><subject>Strategic management</subject><subject>Streams</subject><subject>Sustainable Development</subject><subject>Thresholds</subject><issn>0921-2973</issn><issn>1572-9761</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2018</creationdate><recordtype>article</recordtype><recordid>eNp1kE1LAzEQhoMoWKs_wNuC5-gkaTa7Ryl-QcGDeg7ZdNJu2e7WTLbgvze1gidPAzPP-w48jF0LuBUA5o4E1BVwEBUHoyquT9hEaCN5bUpxyiZQS8FlbdQ5uyDaAIBSABNGb951yGmHvg2tLzrXLws_7DEWaR2R1kO3pCIMMS97wrh3qR36YggFpYhuW7R9ZhM20SXMzHY79m1qkfKhcKvY-rFLY3TdTzN5t0O6ZGfBdYRXv3PKPh4f3ufPfPH69DK_X3CvRJl40MLLSpuASvrgpGl8DaX0vmm0V4B1NfMOQBrQonGzRoelMtqpGVQITdmoKbs59u7i8DkiJbsZxtjnl1aK_EKVdbYwZeJI-TgQRQx2F9uti19WgD24tUe3Nru1B7dW54w8Ziiz_QrjX_P_oW_6aH8X</recordid><startdate>20181201</startdate><enddate>20181201</enddate><creator>Grimstead, Jeremy P.</creator><creator>Krynak, Edward M.</creator><creator>Yates, Adam G.</creator><general>Springer Netherlands</general><general>Springer Nature B.V</general><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7SN</scope><scope>7ST</scope><scope>7XB</scope><scope>88I</scope><scope>8FE</scope><scope>8FH</scope><scope>8FK</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BBNVY</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>BKSAR</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>GNUQQ</scope><scope>HCIFZ</scope><scope>LK8</scope><scope>M2P</scope><scope>M7P</scope><scope>PATMY</scope><scope>PCBAR</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>SOI</scope><orcidid>https://orcid.org/0000-0002-2239-9046</orcidid></search><sort><creationdate>20181201</creationdate><title>Scale-specific land cover thresholds for conservation of stream invertebrate communities in agricultural landscapes</title><author>Grimstead, Jeremy P. ; Krynak, Edward M. ; Yates, Adam G.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c316t-f51c2857fe32cfa27bc9062ccbb5c30e984ca0027051ba4b5fd375a3408e0b6b3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2018</creationdate><topic>Agricultural ecosystems</topic><topic>Agricultural land</topic><topic>Agricultural practices</topic><topic>Agricultural watersheds</topic><topic>Agriculture</topic><topic>Biomedical and Life Sciences</topic><topic>Catchment areas</topic><topic>Communities</topic><topic>Corridors</topic><topic>Ecology</topic><topic>Ecosystem management</topic><topic>Environmental Management</topic><topic>Forest management</topic><topic>Forest protection</topic><topic>Land conservation</topic><topic>Land cover</topic><topic>Landscape Ecology</topic><topic>Landscape preservation</topic><topic>Landscape/Regional and Urban Planning</topic><topic>Life Sciences</topic><topic>Macroinvertebrates</topic><topic>Nature Conservation</topic><topic>Ordination</topic><topic>Research Article</topic><topic>Riparian forests</topic><topic>Strategic management</topic><topic>Streams</topic><topic>Sustainable Development</topic><topic>Thresholds</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Grimstead, Jeremy P.</creatorcontrib><creatorcontrib>Krynak, Edward M.</creatorcontrib><creatorcontrib>Yates, Adam G.</creatorcontrib><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Ecology Abstracts</collection><collection>Environment Abstracts</collection><collection>ProQuest Central (purchase pre-March 2016)</collection><collection>Science Database (Alumni Edition)</collection><collection>ProQuest SciTech Collection</collection><collection>ProQuest Natural Science Collection</collection><collection>ProQuest Central (Alumni) (purchase pre-March 2016)</collection><collection>ProQuest Central (Alumni)</collection><collection>ProQuest Central</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>Biological Science Collection</collection><collection>ProQuest Central</collection><collection>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>ProQuest Central Student</collection><collection>SciTech Premium Collection</collection><collection>ProQuest Biological Science Collection</collection><collection>Science Database (ProQuest)</collection><collection>Biological Science Database</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>Environmental Science Collection</collection><collection>ProQuest Central Basic</collection><collection>Environment Abstracts</collection><jtitle>Landscape ecology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Grimstead, Jeremy P.</au><au>Krynak, Edward M.</au><au>Yates, Adam G.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Scale-specific land cover thresholds for conservation of stream invertebrate communities in agricultural landscapes</atitle><jtitle>Landscape ecology</jtitle><stitle>Landscape Ecol</stitle><date>2018-12-01</date><risdate>2018</risdate><volume>33</volume><issue>12</issue><spage>2239</spage><epage>2252</epage><pages>2239-2252</pages><issn>0921-2973</issn><eissn>1572-9761</eissn><abstract>Context
In agricultural landscapes, riparian forests are used as a management tool to protect stream ecosystems from agricultural activities. However, the ability of managers to target stream protection actions is limited by incomplete knowledge of scale-specific effects of agriculture in riparian corridor and catchment areas.
Objectives
We evaluated scale-specific effects of agricultural cover in riparian corridor and catchment areas on stream benthic macroinvertebrate (BMI) communities to develop cover targets for agricultural landscapes.
Methods
Sixty-eight streams assigned to three experimental treatments (Forested Riparian, Agricultural Riparian, Agricultural Catchment) were sampled for BMIs. Ordination and segmented regression were used to assess impacts of agriculture on BMI communities and detect thresholds for BMI community metrics.
Results
BMI communities were not associated with catchment agricultural cover where the riparian corridor was forested, but were associated with variation in catchment agriculture where riparian forests had been converted to agriculture. Trait-based metrics showed threshold responses at greater than 70% agricultural cover in the catchment. Increasing agriculture in the riparian corridor was associated with less diverse and more tolerant BMI communities. Eight metrics exhibited threshold responses ranging from 45 to 75% agriculture in the riparian corridor.
Conclusions
Riparian forest effectively buffered streams from agricultural activity even where catchment agriculture exceeds 80%. We recommend managers prioritize protection of forested riparian corridors and that restore riparian corridors where agricultural cover is near identified thresholds be a secondary priority. Adoption of catchment management actions should be effective where the riparian corridor has been converted to agriculture.</abstract><cop>Dordrecht</cop><pub>Springer Netherlands</pub><doi>10.1007/s10980-018-0738-5</doi><tpages>14</tpages><orcidid>https://orcid.org/0000-0002-2239-9046</orcidid></addata></record> |
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subjects | Agricultural ecosystems Agricultural land Agricultural practices Agricultural watersheds Agriculture Biomedical and Life Sciences Catchment areas Communities Corridors Ecology Ecosystem management Environmental Management Forest management Forest protection Land conservation Land cover Landscape Ecology Landscape preservation Landscape/Regional and Urban Planning Life Sciences Macroinvertebrates Nature Conservation Ordination Research Article Riparian forests Strategic management Streams Sustainable Development Thresholds |
title | Scale-specific land cover thresholds for conservation of stream invertebrate communities in agricultural landscapes |
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