A new conceptual model for the fate of lignin in decomposing plant litter
Lignin is a main component of plant litter. Its degradation is thought to be critical for litter decomposition rates and the build-up of soil organic matter. We studied the relationships between lignin degradation and the production of dissolved organic carbon (DOC) and of CO 2 during litter decompo...
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Veröffentlicht in: | Ecology (Durham) 2011-05, Vol.92 (5), p.1052-1062 |
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creator | Klotzbüücher, Thimo Kaiser, Klaus Guggenberger, Georg Gatzek, Christiane Kalbitz, Karsten |
description | Lignin is a main component of plant litter. Its degradation is thought to be critical for litter decomposition rates and the build-up of soil organic matter. We studied the relationships between lignin degradation and the production of dissolved organic carbon (DOC) and of CO
2
during litter decomposition. Needle or leaf litter of five species (Norway spruce, Scots pine, mountain ash, European beech, sycamore maple) and of different decomposition stage (freshly fallen and up to 27 months of field exposure) was incubated in the laboratory for two years. Lignin degradation was followed with the CuO method. Strong lignin degradation occurred during the first 200 incubation days, as revealed by decreasing yields of lignin-derived phenols. Thereafter lignin degradation leveled off. This pattern was similar for fresh and decomposed litter, and it stands in contrast to the common view of limited lignin degradation in fresh litter. Dissolved organic carbon and CO
2
also peaked in the first period of the incubation but were not interrelated. In the later phase of incubation, CO
2
production was positively correlated with DOC amounts, suggesting that bioavailable, soluble compounds became a limiting factor for CO
2
production. Lignin degradation occurred only when CO
2
production was high, and not limited by bioavailable carbon. Thus carbon availability was the most important control on lignin degradation. In turn, lignin degradation could not explain differences in DOC and CO
2
production over the study period. Our results challenge the traditional view regarding the fate and role of lignin during litter decomposition. Lignin degradation is controlled by the availability of easily decomposable carbon sources. Consequently, it occurs particularly in the initial phase of litter decomposition and is hampered at later stages if easily decomposable resources decline. |
doi_str_mv | 10.1890/10-1307.1 |
format | Article |
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2
during litter decomposition. Needle or leaf litter of five species (Norway spruce, Scots pine, mountain ash, European beech, sycamore maple) and of different decomposition stage (freshly fallen and up to 27 months of field exposure) was incubated in the laboratory for two years. Lignin degradation was followed with the CuO method. Strong lignin degradation occurred during the first 200 incubation days, as revealed by decreasing yields of lignin-derived phenols. Thereafter lignin degradation leveled off. This pattern was similar for fresh and decomposed litter, and it stands in contrast to the common view of limited lignin degradation in fresh litter. Dissolved organic carbon and CO
2
also peaked in the first period of the incubation but were not interrelated. In the later phase of incubation, CO
2
production was positively correlated with DOC amounts, suggesting that bioavailable, soluble compounds became a limiting factor for CO
2
production. Lignin degradation occurred only when CO
2
production was high, and not limited by bioavailable carbon. Thus carbon availability was the most important control on lignin degradation. In turn, lignin degradation could not explain differences in DOC and CO
2
production over the study period. Our results challenge the traditional view regarding the fate and role of lignin during litter decomposition. Lignin degradation is controlled by the availability of easily decomposable carbon sources. Consequently, it occurs particularly in the initial phase of litter decomposition and is hampered at later stages if easily decomposable resources decline.</description><identifier>ISSN: 0012-9658</identifier><identifier>EISSN: 1939-9170</identifier><identifier>DOI: 10.1890/10-1307.1</identifier><identifier>PMID: 21661566</identifier><identifier>CODEN: ECGYAQ</identifier><language>eng</language><publisher>Washington, DC: Ecological Society of America</publisher><subject>Acer pseudoplatanus ; Animal and plant ecology ; Animal, plant and microbial ecology ; Biochemistry ; Biodegradation, Environmental ; Biological and medical sciences ; C availability ; carbon ; Carbon - chemistry ; Carbon - metabolism ; Carbon dioxide ; Carbon Dioxide - metabolism ; carbon dioxide production ; correlation ; cupric oxide ; Decomposition ; Dissolved organic carbon ; dissolved organic matter ; Ecology ; Fagus sylvatica subsp. sylvatica ; Flowers & plants ; Forest soils ; Fundamental and applied biological sciences. Psychology ; General aspects ; Lignin ; Lignin - chemistry ; Lignin - metabolism ; Litter ; Models, Biological ; Organic soils ; phenols ; Picea abies ; Pinus sylvestris ; Plant Leaves - chemistry ; Plant litter ; plant litter decomposition ; respiration rates ; Soil biochemistry ; Soil biology ; Soil ecology ; soil organic matter ; Sorbus aucuparia ; Time Factors</subject><ispartof>Ecology (Durham), 2011-05, Vol.92 (5), p.1052-1062</ispartof><rights>Copyright © 2011 Ecological Society of America</rights><rights>2011 by the Ecological Society of America</rights><rights>2015 INIST-CNRS</rights><rights>Copyright Ecological Society of America May 2011</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-a5872-620759173e45b5e963a952528852a717997e356cb6f4f51f624ab5a7d83effc73</citedby><cites>FETCH-LOGICAL-a5872-620759173e45b5e963a952528852a717997e356cb6f4f51f624ab5a7d83effc73</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/41151233$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/41151233$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,780,784,803,1417,27924,27925,45574,45575,58017,58250</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=24186434$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/21661566$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><contributor>Henry, HAL</contributor><creatorcontrib>Klotzbüücher, Thimo</creatorcontrib><creatorcontrib>Kaiser, Klaus</creatorcontrib><creatorcontrib>Guggenberger, Georg</creatorcontrib><creatorcontrib>Gatzek, Christiane</creatorcontrib><creatorcontrib>Kalbitz, Karsten</creatorcontrib><title>A new conceptual model for the fate of lignin in decomposing plant litter</title><title>Ecology (Durham)</title><addtitle>Ecology</addtitle><description>Lignin is a main component of plant litter. Its degradation is thought to be critical for litter decomposition rates and the build-up of soil organic matter. We studied the relationships between lignin degradation and the production of dissolved organic carbon (DOC) and of CO
2
during litter decomposition. Needle or leaf litter of five species (Norway spruce, Scots pine, mountain ash, European beech, sycamore maple) and of different decomposition stage (freshly fallen and up to 27 months of field exposure) was incubated in the laboratory for two years. Lignin degradation was followed with the CuO method. Strong lignin degradation occurred during the first 200 incubation days, as revealed by decreasing yields of lignin-derived phenols. Thereafter lignin degradation leveled off. This pattern was similar for fresh and decomposed litter, and it stands in contrast to the common view of limited lignin degradation in fresh litter. Dissolved organic carbon and CO
2
also peaked in the first period of the incubation but were not interrelated. In the later phase of incubation, CO
2
production was positively correlated with DOC amounts, suggesting that bioavailable, soluble compounds became a limiting factor for CO
2
production. Lignin degradation occurred only when CO
2
production was high, and not limited by bioavailable carbon. Thus carbon availability was the most important control on lignin degradation. In turn, lignin degradation could not explain differences in DOC and CO
2
production over the study period. Our results challenge the traditional view regarding the fate and role of lignin during litter decomposition. Lignin degradation is controlled by the availability of easily decomposable carbon sources. Consequently, it occurs particularly in the initial phase of litter decomposition and is hampered at later stages if easily decomposable resources decline.</description><subject>Acer pseudoplatanus</subject><subject>Animal and plant ecology</subject><subject>Animal, plant and microbial ecology</subject><subject>Biochemistry</subject><subject>Biodegradation, Environmental</subject><subject>Biological and medical sciences</subject><subject>C availability</subject><subject>carbon</subject><subject>Carbon - chemistry</subject><subject>Carbon - metabolism</subject><subject>Carbon dioxide</subject><subject>Carbon Dioxide - metabolism</subject><subject>carbon dioxide production</subject><subject>correlation</subject><subject>cupric oxide</subject><subject>Decomposition</subject><subject>Dissolved organic carbon</subject><subject>dissolved organic matter</subject><subject>Ecology</subject><subject>Fagus sylvatica subsp. sylvatica</subject><subject>Flowers & plants</subject><subject>Forest soils</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General aspects</subject><subject>Lignin</subject><subject>Lignin - chemistry</subject><subject>Lignin - metabolism</subject><subject>Litter</subject><subject>Models, Biological</subject><subject>Organic soils</subject><subject>phenols</subject><subject>Picea abies</subject><subject>Pinus sylvestris</subject><subject>Plant Leaves - chemistry</subject><subject>Plant litter</subject><subject>plant litter decomposition</subject><subject>respiration rates</subject><subject>Soil biochemistry</subject><subject>Soil biology</subject><subject>Soil ecology</subject><subject>soil organic matter</subject><subject>Sorbus aucuparia</subject><subject>Time Factors</subject><issn>0012-9658</issn><issn>1939-9170</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2011</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqNkktv1DAQxy0EotuFAx8AsEAIcUjx-O1jtSpQqRIH6IFT5E3sJatsnNqOyn77umQpD6kSluU5zG_mPw8j9AzICWhD3gOpgBF1Ag_QAgwzlQFFHqIFIUArI4U-QscpbUk5wPVjdERBShBSLtD5KR7cNW7C0LgxT7bHu9C6HvsQcf7usLfZ4eBx322GbsDltq4JuzGkbtjgsbdDLr6cXXyCHnnbJ_f0YJfo8sPZ19Wn6uLzx_PV6UVlhVa0kpQoUepjjou1cEYyawQVVGtBrQJljHJMyGYtPfcCvKTcroVVrWbO-0axJXo75x1juJpcyvWuS43rSykuTKnWioNRQpj_IIuuFPyWfPUPuQ1THEobtZaaSqK5LNC7GWpiSCk6X4-x29m4r4HUt3v4acseyrNELw4Jp_XOtXfkr8EX4M0BsKmxvY92aLr0m-OgJWe8cGLmrrve7e9XrM9W3ygBMFQAEbTEPZ_jtimHeBfHAQRQxor_5ez3NtR2E4v25ZeSQJYvYpQyuhCvZ8Lm_RiG2iX7h9zY-jr_yPdSf4_jBsPFxGY</recordid><startdate>201105</startdate><enddate>201105</enddate><creator>Klotzbüücher, Thimo</creator><creator>Kaiser, Klaus</creator><creator>Guggenberger, Georg</creator><creator>Gatzek, Christiane</creator><creator>Kalbitz, Karsten</creator><general>Ecological Society of America</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>7QG</scope><scope>7SN</scope><scope>7SS</scope><scope>7ST</scope><scope>7T7</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>K9.</scope><scope>P64</scope><scope>RC3</scope><scope>SOI</scope><scope>7X8</scope></search><sort><creationdate>201105</creationdate><title>A new conceptual model for the fate of lignin in decomposing plant litter</title><author>Klotzbüücher, Thimo ; Kaiser, Klaus ; Guggenberger, Georg ; Gatzek, Christiane ; Kalbitz, Karsten</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-a5872-620759173e45b5e963a952528852a717997e356cb6f4f51f624ab5a7d83effc73</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2011</creationdate><topic>Acer pseudoplatanus</topic><topic>Animal and plant ecology</topic><topic>Animal, plant and microbial ecology</topic><topic>Biochemistry</topic><topic>Biodegradation, Environmental</topic><topic>Biological and medical sciences</topic><topic>C availability</topic><topic>carbon</topic><topic>Carbon - chemistry</topic><topic>Carbon - metabolism</topic><topic>Carbon dioxide</topic><topic>Carbon Dioxide - metabolism</topic><topic>carbon dioxide production</topic><topic>correlation</topic><topic>cupric oxide</topic><topic>Decomposition</topic><topic>Dissolved organic carbon</topic><topic>dissolved organic matter</topic><topic>Ecology</topic><topic>Fagus sylvatica subsp. sylvatica</topic><topic>Flowers & plants</topic><topic>Forest soils</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General aspects</topic><topic>Lignin</topic><topic>Lignin - chemistry</topic><topic>Lignin - metabolism</topic><topic>Litter</topic><topic>Models, Biological</topic><topic>Organic soils</topic><topic>phenols</topic><topic>Picea abies</topic><topic>Pinus sylvestris</topic><topic>Plant Leaves - chemistry</topic><topic>Plant litter</topic><topic>plant litter decomposition</topic><topic>respiration rates</topic><topic>Soil biochemistry</topic><topic>Soil biology</topic><topic>Soil ecology</topic><topic>soil organic matter</topic><topic>Sorbus aucuparia</topic><topic>Time Factors</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Klotzbüücher, Thimo</creatorcontrib><creatorcontrib>Kaiser, Klaus</creatorcontrib><creatorcontrib>Guggenberger, Georg</creatorcontrib><creatorcontrib>Gatzek, Christiane</creatorcontrib><creatorcontrib>Kalbitz, Karsten</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>Animal Behavior Abstracts</collection><collection>Ecology Abstracts</collection><collection>Entomology Abstracts (Full archive)</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>ProQuest Health & Medical Complete (Alumni)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Genetics Abstracts</collection><collection>Environment Abstracts</collection><collection>MEDLINE - Academic</collection><jtitle>Ecology (Durham)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Klotzbüücher, Thimo</au><au>Kaiser, Klaus</au><au>Guggenberger, Georg</au><au>Gatzek, Christiane</au><au>Kalbitz, Karsten</au><au>Henry, HAL</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>A new conceptual model for the fate of lignin in decomposing plant litter</atitle><jtitle>Ecology (Durham)</jtitle><addtitle>Ecology</addtitle><date>2011-05</date><risdate>2011</risdate><volume>92</volume><issue>5</issue><spage>1052</spage><epage>1062</epage><pages>1052-1062</pages><issn>0012-9658</issn><eissn>1939-9170</eissn><coden>ECGYAQ</coden><abstract>Lignin is a main component of plant litter. Its degradation is thought to be critical for litter decomposition rates and the build-up of soil organic matter. We studied the relationships between lignin degradation and the production of dissolved organic carbon (DOC) and of CO
2
during litter decomposition. Needle or leaf litter of five species (Norway spruce, Scots pine, mountain ash, European beech, sycamore maple) and of different decomposition stage (freshly fallen and up to 27 months of field exposure) was incubated in the laboratory for two years. Lignin degradation was followed with the CuO method. Strong lignin degradation occurred during the first 200 incubation days, as revealed by decreasing yields of lignin-derived phenols. Thereafter lignin degradation leveled off. This pattern was similar for fresh and decomposed litter, and it stands in contrast to the common view of limited lignin degradation in fresh litter. Dissolved organic carbon and CO
2
also peaked in the first period of the incubation but were not interrelated. In the later phase of incubation, CO
2
production was positively correlated with DOC amounts, suggesting that bioavailable, soluble compounds became a limiting factor for CO
2
production. Lignin degradation occurred only when CO
2
production was high, and not limited by bioavailable carbon. Thus carbon availability was the most important control on lignin degradation. In turn, lignin degradation could not explain differences in DOC and CO
2
production over the study period. Our results challenge the traditional view regarding the fate and role of lignin during litter decomposition. Lignin degradation is controlled by the availability of easily decomposable carbon sources. Consequently, it occurs particularly in the initial phase of litter decomposition and is hampered at later stages if easily decomposable resources decline.</abstract><cop>Washington, DC</cop><pub>Ecological Society of America</pub><pmid>21661566</pmid><doi>10.1890/10-1307.1</doi><tpages>11</tpages></addata></record> |
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subjects | Acer pseudoplatanus Animal and plant ecology Animal, plant and microbial ecology Biochemistry Biodegradation, Environmental Biological and medical sciences C availability carbon Carbon - chemistry Carbon - metabolism Carbon dioxide Carbon Dioxide - metabolism carbon dioxide production correlation cupric oxide Decomposition Dissolved organic carbon dissolved organic matter Ecology Fagus sylvatica subsp. sylvatica Flowers & plants Forest soils Fundamental and applied biological sciences. Psychology General aspects Lignin Lignin - chemistry Lignin - metabolism Litter Models, Biological Organic soils phenols Picea abies Pinus sylvestris Plant Leaves - chemistry Plant litter plant litter decomposition respiration rates Soil biochemistry Soil biology Soil ecology soil organic matter Sorbus aucuparia Time Factors |
title | A new conceptual model for the fate of lignin in decomposing plant litter |
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