Turnover of low molecular weight dissolved organic C (DOC) and microbial C exhibit different temperature sensitivities in Arctic tundra soils

Polar ecosystems are currently experiencing some of the fastest rates of climate warming. An increase in soil temperature in High Arctic regions may stimulate soil permafrost melting and microbial activity, thereby accelerating losses of greenhouse gases. It is therefore important to understand the...

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Veröffentlicht in:Soil biology & biochemistry 2008-07, Vol.40 (7), p.1557-1566
Hauptverfasser: Boddy, Elizabeth, Roberts, Paula, Hill, Paul W., Farrar, John, Jones, David L.
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Roberts, Paula
Hill, Paul W.
Farrar, John
Jones, David L.
description Polar ecosystems are currently experiencing some of the fastest rates of climate warming. An increase in soil temperature in High Arctic regions may stimulate soil permafrost melting and microbial activity, thereby accelerating losses of greenhouse gases. It is therefore important to understand the factors regulating the rates of C turnover in polar soils. Consequently, our aims were to: (1) assess the concentration of low molecular weight (MW) dissolved organic carbon (DOC) in soil, (2) to investigate the temperature-dependent turnover of specific low MW compounds, and (3) to analyse the influence of substrate concentration on C cycling. Microbial mineralisation of labile low MW DOC in two High Arctic tundra soils was investigated using soil solutions spiked with either 14C-labelled glucose or amino acids. Spiked solutions were added to the top- and sub-soil from two ecosystem types (lichen and Carex dominated tundra), maintained at three temperatures (4–20 °C), and their microbial mineralisation kinetics monitored. 14CO 2 evolution from the tundra soils in response to 14C-glucose and -amino acid addition could best be described by a double first order exponential kinetic equation with rate constants k 1 and k 2. Both forms of DOC had a short half-life ( t 1/2) in the pool of microbial respiratory substrate ( t 1/2 = 1.07 ± 0.10 h for glucose and 1.63 ± 0.14 h for amino acids; exponential coefficient k 1 = 0.93 ± 0.07 and 0.64 ± 0.06 h −1 respectively) whilst the second phase of mineralisation, assumed to be C that had entered the microbial biomass, was much slower (average k 2 = 1.30 × 10 −3 ± 0.49 × 10 −4 h −1). Temperature had little effect on the rate of mineralisation of 14C used directly as respiratory substrate. In contrast, the turnover rate of the 14C immobilized in the microbial biomass prior to mineralisation was temperature sensitive ( k 2 values of 0.99 × 10 −3 h −1 and 1.66 × 10 −3 h −1 at 4 and 20 °C respectively). Concentration-dependent glucose and amino acid mineralisation kinetics of glucose and amino acids (0–10 mM) were best described using Michaelis–Menten kinetics; there was a low affinity for both C substrates by the microbial community ( K m = 4.07 ± 0.41 mM, V max = 0.027 ± 0.005 mmol kg −1 h −1). In conclusion, our results suggest that in these C limiting environments the flux of labile, low MW DOC through the soil solution is extremely rapid and relatively insensitive to temperature. In contrast, the turnover of C incorporated
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An increase in soil temperature in High Arctic regions may stimulate soil permafrost melting and microbial activity, thereby accelerating losses of greenhouse gases. It is therefore important to understand the factors regulating the rates of C turnover in polar soils. Consequently, our aims were to: (1) assess the concentration of low molecular weight (MW) dissolved organic carbon (DOC) in soil, (2) to investigate the temperature-dependent turnover of specific low MW compounds, and (3) to analyse the influence of substrate concentration on C cycling. Microbial mineralisation of labile low MW DOC in two High Arctic tundra soils was investigated using soil solutions spiked with either 14C-labelled glucose or amino acids. Spiked solutions were added to the top- and sub-soil from two ecosystem types (lichen and Carex dominated tundra), maintained at three temperatures (4–20 °C), and their microbial mineralisation kinetics monitored. 14CO 2 evolution from the tundra soils in response to 14C-glucose and -amino acid addition could best be described by a double first order exponential kinetic equation with rate constants k 1 and k 2. Both forms of DOC had a short half-life ( t 1/2) in the pool of microbial respiratory substrate ( t 1/2 = 1.07 ± 0.10 h for glucose and 1.63 ± 0.14 h for amino acids; exponential coefficient k 1 = 0.93 ± 0.07 and 0.64 ± 0.06 h −1 respectively) whilst the second phase of mineralisation, assumed to be C that had entered the microbial biomass, was much slower (average k 2 = 1.30 × 10 −3 ± 0.49 × 10 −4 h −1). Temperature had little effect on the rate of mineralisation of 14C used directly as respiratory substrate. In contrast, the turnover rate of the 14C immobilized in the microbial biomass prior to mineralisation was temperature sensitive ( k 2 values of 0.99 × 10 −3 h −1 and 1.66 × 10 −3 h −1 at 4 and 20 °C respectively). Concentration-dependent glucose and amino acid mineralisation kinetics of glucose and amino acids (0–10 mM) were best described using Michaelis–Menten kinetics; there was a low affinity for both C substrates by the microbial community ( K m = 4.07 ± 0.41 mM, V max = 0.027 ± 0.005 mmol kg −1 h −1). In conclusion, our results suggest that in these C limiting environments the flux of labile, low MW DOC through the soil solution is extremely rapid and relatively insensitive to temperature. 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Psychology ; Global warming ; glucose ; kinetics ; lichens ; microbial activity ; Mineralisation ; mineralization ; molecular weight ; permafrost ; Physics, chemistry, biochemistry and biology of agricultural and forest soils ; radionuclides ; Respiration ; soil microorganisms ; soil organic carbon ; Soil science ; soil solution ; temperature ; tundra soils</subject><ispartof>Soil biology &amp; biochemistry, 2008-07, Vol.40 (7), p.1557-1566</ispartof><rights>2008 Elsevier Ltd</rights><rights>2008 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c460t-4c7e9d0c95031f08284d0c696207801c8ff028ed0cca2a84ae322e4dd3af66243</citedby><cites>FETCH-LOGICAL-c460t-4c7e9d0c95031f08284d0c696207801c8ff028ed0cca2a84ae322e4dd3af66243</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://www.sciencedirect.com/science/article/pii/S0038071708000588$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,776,780,3537,27901,27902,65306</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&amp;idt=20476532$$DView record in Pascal Francis$$Hfree_for_read</backlink></links><search><creatorcontrib>Boddy, Elizabeth</creatorcontrib><creatorcontrib>Roberts, Paula</creatorcontrib><creatorcontrib>Hill, Paul W.</creatorcontrib><creatorcontrib>Farrar, John</creatorcontrib><creatorcontrib>Jones, David L.</creatorcontrib><title>Turnover of low molecular weight dissolved organic C (DOC) and microbial C exhibit different temperature sensitivities in Arctic tundra soils</title><title>Soil biology &amp; biochemistry</title><description>Polar ecosystems are currently experiencing some of the fastest rates of climate warming. An increase in soil temperature in High Arctic regions may stimulate soil permafrost melting and microbial activity, thereby accelerating losses of greenhouse gases. It is therefore important to understand the factors regulating the rates of C turnover in polar soils. Consequently, our aims were to: (1) assess the concentration of low molecular weight (MW) dissolved organic carbon (DOC) in soil, (2) to investigate the temperature-dependent turnover of specific low MW compounds, and (3) to analyse the influence of substrate concentration on C cycling. Microbial mineralisation of labile low MW DOC in two High Arctic tundra soils was investigated using soil solutions spiked with either 14C-labelled glucose or amino acids. Spiked solutions were added to the top- and sub-soil from two ecosystem types (lichen and Carex dominated tundra), maintained at three temperatures (4–20 °C), and their microbial mineralisation kinetics monitored. 14CO 2 evolution from the tundra soils in response to 14C-glucose and -amino acid addition could best be described by a double first order exponential kinetic equation with rate constants k 1 and k 2. Both forms of DOC had a short half-life ( t 1/2) in the pool of microbial respiratory substrate ( t 1/2 = 1.07 ± 0.10 h for glucose and 1.63 ± 0.14 h for amino acids; exponential coefficient k 1 = 0.93 ± 0.07 and 0.64 ± 0.06 h −1 respectively) whilst the second phase of mineralisation, assumed to be C that had entered the microbial biomass, was much slower (average k 2 = 1.30 × 10 −3 ± 0.49 × 10 −4 h −1). Temperature had little effect on the rate of mineralisation of 14C used directly as respiratory substrate. In contrast, the turnover rate of the 14C immobilized in the microbial biomass prior to mineralisation was temperature sensitive ( k 2 values of 0.99 × 10 −3 h −1 and 1.66 × 10 −3 h −1 at 4 and 20 °C respectively). Concentration-dependent glucose and amino acid mineralisation kinetics of glucose and amino acids (0–10 mM) were best described using Michaelis–Menten kinetics; there was a low affinity for both C substrates by the microbial community ( K m = 4.07 ± 0.41 mM, V max = 0.027 ± 0.005 mmol kg −1 h −1). In conclusion, our results suggest that in these C limiting environments the flux of labile, low MW DOC through the soil solution is extremely rapid and relatively insensitive to temperature. In contrast, the turnover of C incorporated into higher molecular weight microbial C pools appears to show greater temperature sensitivity.</description><subject>Agronomy. Soil science and plant productions</subject><subject>amino acids</subject><subject>Biochemistry and biology</subject><subject>Biodegradation</subject><subject>biogeochemical cycles</subject><subject>Biological and medical sciences</subject><subject>carbon</subject><subject>Carbon cycling</subject><subject>Carex</subject><subject>Chemical, physicochemical, biochemical and biological properties</subject><subject>Climate change</subject><subject>dissolved organic carbon</subject><subject>Dissolved organic matter</subject><subject>Dissolved organic nitrogen</subject><subject>ecosystems</subject><subject>equations</subject><subject>frozen soils</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Global warming</subject><subject>glucose</subject><subject>kinetics</subject><subject>lichens</subject><subject>microbial activity</subject><subject>Mineralisation</subject><subject>mineralization</subject><subject>molecular weight</subject><subject>permafrost</subject><subject>Physics, chemistry, biochemistry and biology of agricultural and forest soils</subject><subject>radionuclides</subject><subject>Respiration</subject><subject>soil microorganisms</subject><subject>soil organic carbon</subject><subject>Soil science</subject><subject>soil solution</subject><subject>temperature</subject><subject>tundra soils</subject><issn>0038-0717</issn><issn>1879-3428</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2008</creationdate><recordtype>article</recordtype><recordid>eNqFkE1vEzEQhlcIJELhJyB8AbWHXcb2fnhPqArlQ6rUA-3Zcrzj1JHXDrY3hR_Bf8ZRIq4cLMuj553xPFX1lkJDgfYfd00K1m1saBiAaIA2wOFZtaJiGGveMvG8WgFwUcNAh5fVq5R2AMA6ylfVn_sl-nDASIIhLjyROTjUi1ORPKHdPmYy2ZSCO-BEQtwqbzVZk8vPd-srovxEZqtj2FjlShV_PdqNPSaMwYg-k4zzHqPKS0SS0Ceb7aEcTMR6ch11Lt3y4qeoyHGF9Lp6YZRL-OZ8X1QPX27u19_q27uv39fXt7Vue8h1qwccJ9BjB5waEEy05dWPPYNBANXCGGACS00rpkSrkDOG7TRxZfqetfyi-nDqu4_h54Ipy9kmjc4pj2FJko59T4eOF7A7gWXLlCIauY92VvG3pCCP8uVOnuXLo3wJVBb5Jff-PEAlrZyJymub_oUZtEPfcVa4dyfOqCDVNhbm4QcDygFGCiOnhfh0IrD4OFiMMmmLXuNkI-osp2D_85e_JBqojA</recordid><startdate>20080701</startdate><enddate>20080701</enddate><creator>Boddy, Elizabeth</creator><creator>Roberts, Paula</creator><creator>Hill, Paul W.</creator><creator>Farrar, John</creator><creator>Jones, David L.</creator><general>Elsevier Ltd</general><general>Elsevier Science</general><scope>FBQ</scope><scope>IQODW</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7SN</scope><scope>7T7</scope><scope>7TV</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>M7N</scope><scope>P64</scope></search><sort><creationdate>20080701</creationdate><title>Turnover of low molecular weight dissolved organic C (DOC) and microbial C exhibit different temperature sensitivities in Arctic tundra soils</title><author>Boddy, Elizabeth ; Roberts, Paula ; Hill, Paul W. ; Farrar, John ; Jones, David L.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c460t-4c7e9d0c95031f08284d0c696207801c8ff028ed0cca2a84ae322e4dd3af66243</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2008</creationdate><topic>Agronomy. Soil science and plant productions</topic><topic>amino acids</topic><topic>Biochemistry and biology</topic><topic>Biodegradation</topic><topic>biogeochemical cycles</topic><topic>Biological and medical sciences</topic><topic>carbon</topic><topic>Carbon cycling</topic><topic>Carex</topic><topic>Chemical, physicochemical, biochemical and biological properties</topic><topic>Climate change</topic><topic>dissolved organic carbon</topic><topic>Dissolved organic matter</topic><topic>Dissolved organic nitrogen</topic><topic>ecosystems</topic><topic>equations</topic><topic>frozen soils</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Global warming</topic><topic>glucose</topic><topic>kinetics</topic><topic>lichens</topic><topic>microbial activity</topic><topic>Mineralisation</topic><topic>mineralization</topic><topic>molecular weight</topic><topic>permafrost</topic><topic>Physics, chemistry, biochemistry and biology of agricultural and forest soils</topic><topic>radionuclides</topic><topic>Respiration</topic><topic>soil microorganisms</topic><topic>soil organic carbon</topic><topic>Soil science</topic><topic>soil solution</topic><topic>temperature</topic><topic>tundra soils</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Boddy, Elizabeth</creatorcontrib><creatorcontrib>Roberts, Paula</creatorcontrib><creatorcontrib>Hill, Paul W.</creatorcontrib><creatorcontrib>Farrar, John</creatorcontrib><creatorcontrib>Jones, David L.</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Pollution Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><jtitle>Soil biology &amp; biochemistry</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Boddy, Elizabeth</au><au>Roberts, Paula</au><au>Hill, Paul W.</au><au>Farrar, John</au><au>Jones, David L.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Turnover of low molecular weight dissolved organic C (DOC) and microbial C exhibit different temperature sensitivities in Arctic tundra soils</atitle><jtitle>Soil biology &amp; biochemistry</jtitle><date>2008-07-01</date><risdate>2008</risdate><volume>40</volume><issue>7</issue><spage>1557</spage><epage>1566</epage><pages>1557-1566</pages><issn>0038-0717</issn><eissn>1879-3428</eissn><coden>SBIOAH</coden><abstract>Polar ecosystems are currently experiencing some of the fastest rates of climate warming. An increase in soil temperature in High Arctic regions may stimulate soil permafrost melting and microbial activity, thereby accelerating losses of greenhouse gases. It is therefore important to understand the factors regulating the rates of C turnover in polar soils. Consequently, our aims were to: (1) assess the concentration of low molecular weight (MW) dissolved organic carbon (DOC) in soil, (2) to investigate the temperature-dependent turnover of specific low MW compounds, and (3) to analyse the influence of substrate concentration on C cycling. Microbial mineralisation of labile low MW DOC in two High Arctic tundra soils was investigated using soil solutions spiked with either 14C-labelled glucose or amino acids. Spiked solutions were added to the top- and sub-soil from two ecosystem types (lichen and Carex dominated tundra), maintained at three temperatures (4–20 °C), and their microbial mineralisation kinetics monitored. 14CO 2 evolution from the tundra soils in response to 14C-glucose and -amino acid addition could best be described by a double first order exponential kinetic equation with rate constants k 1 and k 2. Both forms of DOC had a short half-life ( t 1/2) in the pool of microbial respiratory substrate ( t 1/2 = 1.07 ± 0.10 h for glucose and 1.63 ± 0.14 h for amino acids; exponential coefficient k 1 = 0.93 ± 0.07 and 0.64 ± 0.06 h −1 respectively) whilst the second phase of mineralisation, assumed to be C that had entered the microbial biomass, was much slower (average k 2 = 1.30 × 10 −3 ± 0.49 × 10 −4 h −1). Temperature had little effect on the rate of mineralisation of 14C used directly as respiratory substrate. In contrast, the turnover rate of the 14C immobilized in the microbial biomass prior to mineralisation was temperature sensitive ( k 2 values of 0.99 × 10 −3 h −1 and 1.66 × 10 −3 h −1 at 4 and 20 °C respectively). Concentration-dependent glucose and amino acid mineralisation kinetics of glucose and amino acids (0–10 mM) were best described using Michaelis–Menten kinetics; there was a low affinity for both C substrates by the microbial community ( K m = 4.07 ± 0.41 mM, V max = 0.027 ± 0.005 mmol kg −1 h −1). In conclusion, our results suggest that in these C limiting environments the flux of labile, low MW DOC through the soil solution is extremely rapid and relatively insensitive to temperature. In contrast, the turnover of C incorporated into higher molecular weight microbial C pools appears to show greater temperature sensitivity.</abstract><cop>Oxford</cop><cop>New York, NY</cop><pub>Elsevier Ltd</pub><doi>10.1016/j.soilbio.2008.01.030</doi><tpages>10</tpages></addata></record>
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subjects Agronomy. Soil science and plant productions
amino acids
Biochemistry and biology
Biodegradation
biogeochemical cycles
Biological and medical sciences
carbon
Carbon cycling
Carex
Chemical, physicochemical, biochemical and biological properties
Climate change
dissolved organic carbon
Dissolved organic matter
Dissolved organic nitrogen
ecosystems
equations
frozen soils
Fundamental and applied biological sciences. Psychology
Global warming
glucose
kinetics
lichens
microbial activity
Mineralisation
mineralization
molecular weight
permafrost
Physics, chemistry, biochemistry and biology of agricultural and forest soils
radionuclides
Respiration
soil microorganisms
soil organic carbon
Soil science
soil solution
temperature
tundra soils
title Turnover of low molecular weight dissolved organic C (DOC) and microbial C exhibit different temperature sensitivities in Arctic tundra soils
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