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The effects of phytophagous insects on water and soil nutrient concentrations and fluxes through forest stands of the Level II monitoring network in the UK
The effects of insect defoliators on throughfall and soil nutrient fluxes were studied in coniferous and deciduous stands at five UK intensive monitoring plots (1998 to 2008). Links were found between the dissolved organic carbon (DOC), nitrogen (N) and potassium (K) fluxes through the forest system...
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Published in: | The Science of the total environment 2010-12, Vol.409 (1), p.169-181 |
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description | The effects of insect defoliators on throughfall and soil nutrient fluxes were studied in coniferous and deciduous stands at five UK intensive monitoring plots (1998 to 2008). Links were found between the dissolved organic carbon (DOC), nitrogen (N) and potassium (K) fluxes through the forest system to biological activity within the canopy. Underlying soil type determined the leaching or accumulation of these elements. Under oak, monitored at two sites, frass from caterpillars of
Tortrix viridana and
Operophtera brumata added direct deposition of ~
16
kg
ha
−1extra N during defoliation. Peaks of nitrate (NO
3–N) flux between 5 and 9
kg
ha
−1 (×5 usual winter values) were recorded in consecutive years in shallow soil waters. Synchronous rises in deep soil NO
3–N fluxes at the Grizedale sandy site indicate downward flushing, not seen at the clay site. Under three Sitka spruce stands, generation of honeydew (DOC) was attributed to two aphid species (
Elatobium abietinum and
Cinara pilicornis) with distinctive feeding strategies. Throughfall DOC showed mean annual fluxes (6 seasons) ~
45–60
kg
ha
−1 compared with rainfall values of 14–22
kg
ha
−1. Increases of total N in throughfall and NO
3–N fluxes in shallow soil solution were detected — soil water fluxes reached
8
kg
ha
−1 in Llyn Brianne, ~
25
kg
ha
−1 in Tummel, and ~
40
kg NO
3–N
ha
−1 in Coalburn. At Tummel, on sandy soil, NO
3–N leaching showed increased concentration at depth, attributed to microbiological activity within the soil. By contrast, at Coalburn and Llyn Brianne, sites on peaty gleys, soil water NO
3–N was retained mostly within the humus layer. Soil type is thus key to predicting N movement and retention patterns. These long term analyses show important direct and indirect effects of phytophagous insects in forest ecosystems, on above and below ground processes affecting tree growth, soil condition, vegetation and water quality. |
doi_str_mv | 10.1016/j.scitotenv.2010.09.029 |
format | article |
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Tortrix viridana and
Operophtera brumata added direct deposition of ~
16
kg
ha
−1extra N during defoliation. Peaks of nitrate (NO
3–N) flux between 5 and 9
kg
ha
−1 (×5 usual winter values) were recorded in consecutive years in shallow soil waters. Synchronous rises in deep soil NO
3–N fluxes at the Grizedale sandy site indicate downward flushing, not seen at the clay site. Under three Sitka spruce stands, generation of honeydew (DOC) was attributed to two aphid species (
Elatobium abietinum and
Cinara pilicornis) with distinctive feeding strategies. Throughfall DOC showed mean annual fluxes (6 seasons) ~
45–60
kg
ha
−1 compared with rainfall values of 14–22
kg
ha
−1. Increases of total N in throughfall and NO
3–N fluxes in shallow soil solution were detected — soil water fluxes reached
8
kg
ha
−1 in Llyn Brianne, ~
25
kg
ha
−1 in Tummel, and ~
40
kg NO
3–N
ha
−1 in Coalburn. At Tummel, on sandy soil, NO
3–N leaching showed increased concentration at depth, attributed to microbiological activity within the soil. By contrast, at Coalburn and Llyn Brianne, sites on peaty gleys, soil water NO
3–N was retained mostly within the humus layer. Soil type is thus key to predicting N movement and retention patterns. These long term analyses show important direct and indirect effects of phytophagous insects in forest ecosystems, on above and below ground processes affecting tree growth, soil condition, vegetation and water quality.</description><identifier>ISSN: 0048-9697</identifier><identifier>EISSN: 1879-1026</identifier><identifier>DOI: 10.1016/j.scitotenv.2010.09.029</identifier><identifier>PMID: 20961599</identifier><identifier>CODEN: STENDL</identifier><language>eng</language><publisher>Kidlington: Elsevier B.V</publisher><subject>Animal and plant ecology ; Animal, plant and microbial ecology ; Animals ; Aphididae ; Biological and medical sciences ; Cinara pilicornis ; Elatobium abietinum ; Environmental Monitoring ; Fluxes ; Forest monitoring ; Forestry ; Forests ; Fresh Water - chemistry ; Fundamental and applied biological sciences. Psychology ; General forest ecology ; Generalities. Production, biomass. Quality of wood and forest products. General forest ecology ; Insecta - metabolism ; Insecta - physiology ; Insects ; K flux ; Microorganisms ; Monitoring ; Nitrogen - analysis ; Nitrogen - metabolism ; Nitrogen Cycle ; Nutrients ; Oak ; Operophtera brumata ; Sitka spruce ; Soil (material) ; Soil - chemistry ; Soil Pollutants - analysis ; Soil Pollutants - metabolism ; Soil type ; Soil water NO 3–N ; Spruce aphid ; Stands ; Supports ; Synecology ; Terrestrial ecosystems ; Throughfall DOC flux ; Tortrix viridana ; Total N flux ; Trees - chemistry ; Trees - metabolism ; United Kingdom ; Water quality ; Winter moth</subject><ispartof>The Science of the total environment, 2010-12, Vol.409 (1), p.169-181</ispartof><rights>2010</rights><rights>2015 INIST-CNRS</rights><rights>Crown Copyright © 2010. Published by Elsevier B.V. All rights reserved.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c489t-a83ea6e7e661cca32c48c4f86b69fa4b7b5aa4e5c6649acfa56ba88ede0bb8e63</citedby><cites>FETCH-LOGICAL-c489t-a83ea6e7e661cca32c48c4f86b69fa4b7b5aa4e5c6649acfa56ba88ede0bb8e63</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=23452349$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/20961599$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Pitman, R.M.</creatorcontrib><creatorcontrib>Vanguelova, E.I.</creatorcontrib><creatorcontrib>Benham, S.E.</creatorcontrib><title>The effects of phytophagous insects on water and soil nutrient concentrations and fluxes through forest stands of the Level II monitoring network in the UK</title><title>The Science of the total environment</title><addtitle>Sci Total Environ</addtitle><description>The effects of insect defoliators on throughfall and soil nutrient fluxes were studied in coniferous and deciduous stands at five UK intensive monitoring plots (1998 to 2008). Links were found between the dissolved organic carbon (DOC), nitrogen (N) and potassium (K) fluxes through the forest system to biological activity within the canopy. Underlying soil type determined the leaching or accumulation of these elements. Under oak, monitored at two sites, frass from caterpillars of
Tortrix viridana and
Operophtera brumata added direct deposition of ~
16
kg
ha
−1extra N during defoliation. Peaks of nitrate (NO
3–N) flux between 5 and 9
kg
ha
−1 (×5 usual winter values) were recorded in consecutive years in shallow soil waters. Synchronous rises in deep soil NO
3–N fluxes at the Grizedale sandy site indicate downward flushing, not seen at the clay site. Under three Sitka spruce stands, generation of honeydew (DOC) was attributed to two aphid species (
Elatobium abietinum and
Cinara pilicornis) with distinctive feeding strategies. Throughfall DOC showed mean annual fluxes (6 seasons) ~
45–60
kg
ha
−1 compared with rainfall values of 14–22
kg
ha
−1. Increases of total N in throughfall and NO
3–N fluxes in shallow soil solution were detected — soil water fluxes reached
8
kg
ha
−1 in Llyn Brianne, ~
25
kg
ha
−1 in Tummel, and ~
40
kg NO
3–N
ha
−1 in Coalburn. At Tummel, on sandy soil, NO
3–N leaching showed increased concentration at depth, attributed to microbiological activity within the soil. By contrast, at Coalburn and Llyn Brianne, sites on peaty gleys, soil water NO
3–N was retained mostly within the humus layer. Soil type is thus key to predicting N movement and retention patterns. These long term analyses show important direct and indirect effects of phytophagous insects in forest ecosystems, on above and below ground processes affecting tree growth, soil condition, vegetation and water quality.</description><subject>Animal and plant ecology</subject><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Aphididae</subject><subject>Biological and medical sciences</subject><subject>Cinara pilicornis</subject><subject>Elatobium abietinum</subject><subject>Environmental Monitoring</subject><subject>Fluxes</subject><subject>Forest monitoring</subject><subject>Forestry</subject><subject>Forests</subject><subject>Fresh Water - chemistry</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General forest ecology</subject><subject>Generalities. Production, biomass. Quality of wood and forest products. General forest ecology</subject><subject>Insecta - metabolism</subject><subject>Insecta - physiology</subject><subject>Insects</subject><subject>K flux</subject><subject>Microorganisms</subject><subject>Monitoring</subject><subject>Nitrogen - analysis</subject><subject>Nitrogen - metabolism</subject><subject>Nitrogen Cycle</subject><subject>Nutrients</subject><subject>Oak</subject><subject>Operophtera brumata</subject><subject>Sitka spruce</subject><subject>Soil (material)</subject><subject>Soil - chemistry</subject><subject>Soil Pollutants - analysis</subject><subject>Soil Pollutants - metabolism</subject><subject>Soil type</subject><subject>Soil water NO 3–N</subject><subject>Spruce aphid</subject><subject>Stands</subject><subject>Supports</subject><subject>Synecology</subject><subject>Terrestrial ecosystems</subject><subject>Throughfall DOC flux</subject><subject>Tortrix viridana</subject><subject>Total N flux</subject><subject>Trees - chemistry</subject><subject>Trees - metabolism</subject><subject>United Kingdom</subject><subject>Water quality</subject><subject>Winter moth</subject><issn>0048-9697</issn><issn>1879-1026</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2010</creationdate><recordtype>article</recordtype><recordid>eNqFks9uEzEQxlcIREPhFagvCC4J9v7xro9VVSAiEgeas-X1jrMOGzvY3pQ-Cy_LbBLKjVqyRhr_Zr6xP2fZFaMLRhn_uF1EbZNP4A6LnGKWigXNxbNsxppazBnN-fNsRmnZzAUX9UX2KsYtxVU37GV2kVPBWSXELPt91wMBY0CnSLwh-_4h-X2vNn6MxLp4yjtyrxIEolxHorcDcWMKFlwi2juNMahkvYtHwAzjL4gk9cGPm54YHyAmEhOeHSUSKq7gAANZLsnOO7xHsG5DHKR7H36g6hFZf32dvTBqiPDmHC-z9afbu5sv89W3z8ub69Vcl41Ic9UUoDjUwDnTWhU5pnVpGt5yYVTZ1m2lVAmV5rwUShtV8VY1DXRA27YBXlxm709998H_HHFYubNRwzAoB_gMsqlYySuR50-SNS8Yn1AkP_yXZHVNi4IKNsnXJ1QHH2MAI_fB7lR4kIzKyW25lY9uy8ltSYVEt7Hy7VlkbHfQPdb9tReBd2dARa0GE5TTNv7jirLCPXFXJ84oL9UmILP-jkoFZYKKilZIXJ8IQCMOFsI0EqD3nQ34R2Tn7ZPj_gEplNoT</recordid><startdate>20101201</startdate><enddate>20101201</enddate><creator>Pitman, R.M.</creator><creator>Vanguelova, E.I.</creator><creator>Benham, S.E.</creator><general>Elsevier B.V</general><general>[Amsterdam; New York]: Elsevier Science</general><general>Elsevier</general><scope>FBQ</scope><scope>IQODW</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>7SU</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>KR7</scope><scope>7X8</scope><scope>7QH</scope><scope>7SS</scope><scope>7ST</scope><scope>7TG</scope><scope>7TV</scope><scope>7UA</scope><scope>F1W</scope><scope>H97</scope><scope>KL.</scope><scope>L.G</scope><scope>SOI</scope></search><sort><creationdate>20101201</creationdate><title>The effects of phytophagous insects on water and soil nutrient concentrations and fluxes through forest stands of the Level II monitoring network in the UK</title><author>Pitman, R.M. ; Vanguelova, E.I. ; Benham, S.E.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c489t-a83ea6e7e661cca32c48c4f86b69fa4b7b5aa4e5c6649acfa56ba88ede0bb8e63</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2010</creationdate><topic>Animal and plant ecology</topic><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Aphididae</topic><topic>Biological and medical sciences</topic><topic>Cinara pilicornis</topic><topic>Elatobium abietinum</topic><topic>Environmental Monitoring</topic><topic>Fluxes</topic><topic>Forest monitoring</topic><topic>Forestry</topic><topic>Forests</topic><topic>Fresh Water - chemistry</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General forest ecology</topic><topic>Generalities. Production, biomass. Quality of wood and forest products. General forest ecology</topic><topic>Insecta - metabolism</topic><topic>Insecta - physiology</topic><topic>Insects</topic><topic>K flux</topic><topic>Microorganisms</topic><topic>Monitoring</topic><topic>Nitrogen - analysis</topic><topic>Nitrogen - metabolism</topic><topic>Nitrogen Cycle</topic><topic>Nutrients</topic><topic>Oak</topic><topic>Operophtera brumata</topic><topic>Sitka spruce</topic><topic>Soil (material)</topic><topic>Soil - chemistry</topic><topic>Soil Pollutants - analysis</topic><topic>Soil Pollutants - metabolism</topic><topic>Soil type</topic><topic>Soil water NO 3–N</topic><topic>Spruce aphid</topic><topic>Stands</topic><topic>Supports</topic><topic>Synecology</topic><topic>Terrestrial ecosystems</topic><topic>Throughfall DOC flux</topic><topic>Tortrix viridana</topic><topic>Total N flux</topic><topic>Trees - chemistry</topic><topic>Trees - metabolism</topic><topic>United Kingdom</topic><topic>Water quality</topic><topic>Winter moth</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Pitman, R.M.</creatorcontrib><creatorcontrib>Vanguelova, E.I.</creatorcontrib><creatorcontrib>Benham, S.E.</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Environmental Engineering Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><collection>MEDLINE - Academic</collection><collection>Aqualine</collection><collection>Entomology Abstracts (Full archive)</collection><collection>Environment Abstracts</collection><collection>Meteorological & Geoastrophysical Abstracts</collection><collection>Pollution Abstracts</collection><collection>Water Resources Abstracts</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Meteorological & Geoastrophysical Abstracts - Academic</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Environment Abstracts</collection><jtitle>The Science of the total environment</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Pitman, R.M.</au><au>Vanguelova, E.I.</au><au>Benham, S.E.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>The effects of phytophagous insects on water and soil nutrient concentrations and fluxes through forest stands of the Level II monitoring network in the UK</atitle><jtitle>The Science of the total environment</jtitle><addtitle>Sci Total Environ</addtitle><date>2010-12-01</date><risdate>2010</risdate><volume>409</volume><issue>1</issue><spage>169</spage><epage>181</epage><pages>169-181</pages><issn>0048-9697</issn><eissn>1879-1026</eissn><coden>STENDL</coden><abstract>The effects of insect defoliators on throughfall and soil nutrient fluxes were studied in coniferous and deciduous stands at five UK intensive monitoring plots (1998 to 2008). Links were found between the dissolved organic carbon (DOC), nitrogen (N) and potassium (K) fluxes through the forest system to biological activity within the canopy. Underlying soil type determined the leaching or accumulation of these elements. Under oak, monitored at two sites, frass from caterpillars of
Tortrix viridana and
Operophtera brumata added direct deposition of ~
16
kg
ha
−1extra N during defoliation. Peaks of nitrate (NO
3–N) flux between 5 and 9
kg
ha
−1 (×5 usual winter values) were recorded in consecutive years in shallow soil waters. Synchronous rises in deep soil NO
3–N fluxes at the Grizedale sandy site indicate downward flushing, not seen at the clay site. Under three Sitka spruce stands, generation of honeydew (DOC) was attributed to two aphid species (
Elatobium abietinum and
Cinara pilicornis) with distinctive feeding strategies. Throughfall DOC showed mean annual fluxes (6 seasons) ~
45–60
kg
ha
−1 compared with rainfall values of 14–22
kg
ha
−1. Increases of total N in throughfall and NO
3–N fluxes in shallow soil solution were detected — soil water fluxes reached
8
kg
ha
−1 in Llyn Brianne, ~
25
kg
ha
−1 in Tummel, and ~
40
kg NO
3–N
ha
−1 in Coalburn. At Tummel, on sandy soil, NO
3–N leaching showed increased concentration at depth, attributed to microbiological activity within the soil. By contrast, at Coalburn and Llyn Brianne, sites on peaty gleys, soil water NO
3–N was retained mostly within the humus layer. Soil type is thus key to predicting N movement and retention patterns. These long term analyses show important direct and indirect effects of phytophagous insects in forest ecosystems, on above and below ground processes affecting tree growth, soil condition, vegetation and water quality.</abstract><cop>Kidlington</cop><pub>Elsevier B.V</pub><pmid>20961599</pmid><doi>10.1016/j.scitotenv.2010.09.029</doi><tpages>13</tpages></addata></record> |
fulltext | fulltext |
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language | eng |
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source | ScienceDirect Freedom Collection |
subjects | Animal and plant ecology Animal, plant and microbial ecology Animals Aphididae Biological and medical sciences Cinara pilicornis Elatobium abietinum Environmental Monitoring Fluxes Forest monitoring Forestry Forests Fresh Water - chemistry Fundamental and applied biological sciences. Psychology General forest ecology Generalities. Production, biomass. Quality of wood and forest products. General forest ecology Insecta - metabolism Insecta - physiology Insects K flux Microorganisms Monitoring Nitrogen - analysis Nitrogen - metabolism Nitrogen Cycle Nutrients Oak Operophtera brumata Sitka spruce Soil (material) Soil - chemistry Soil Pollutants - analysis Soil Pollutants - metabolism Soil type Soil water NO 3–N Spruce aphid Stands Supports Synecology Terrestrial ecosystems Throughfall DOC flux Tortrix viridana Total N flux Trees - chemistry Trees - metabolism United Kingdom Water quality Winter moth |
title | The effects of phytophagous insects on water and soil nutrient concentrations and fluxes through forest stands of the Level II monitoring network in the UK |
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