A review of soil carbon change in New Zealand's grazed grasslands
Soil organic matter is a potential sink of atmospheric carbon (C) and critical for maintaining soil quality. We reviewed New Zealand studies of soil C changes after conversion from woody vegetation to pasture, and under long-term pasture. Soil C increased by about 13.7 t C ha −1 to a new steady stat...
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Veröffentlicht in: | New Zealand journal of agricultural research 2017-06, Vol.60 (2), p.93-118 |
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container_title | New Zealand journal of agricultural research |
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creator | Schipper, Louis A. Mudge, Paul L. Kirschbaum, Miko U. F. Hedley, Carolyn B. Golubiewski, Nancy E. Smaill, Simeon J. Kelliher, Francis M. |
description | Soil organic matter is a potential sink of atmospheric carbon (C) and critical for maintaining soil quality. We reviewed New Zealand studies of soil C changes after conversion from woody vegetation to pasture, and under long-term pasture. Soil C increased by about 13.7 t C ha
−1
to a new steady state when forests were initially converted to pasture. In the last 3-4 decades, resampling of soil profiles demonstrated that under long-term pasture on flat land, soil C had subsequently declined for allophanic, gley and organic soils by 0.54, 0.32 and 2.9 t C ha
−1
y
−1
, respectively, and soil C had not changed in the remainder of sampled soil orders. For the same time period, pasture soils on stable midslopes of hill country gained 0.6 t C ha
−1
y
−1
. Whether these changes are ongoing is not known, except for the organic soils where losses will continue so long as they are drained. Phosphorus fertiliser application did not change C stocks. Irrigation decreased carbon by 7 t C ha
−1
. Carbon losses during pasture renewal ranged between 0.8 and 4.1 t C ha
−1
. Some evidence suggests tussock grasslands can gain C when fertilised and not overgrazed. When combined to the national scale, different data sets suggest either no change or a gain of C, but with large uncertainties. We highlight key land-use practices and soil orders that require further information of soil C stock changes and advocate for a better understanding of underpinning reasons for changes in soil C. |
doi_str_mv | 10.1080/00288233.2017.1284134 |
format | Article |
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−1
to a new steady state when forests were initially converted to pasture. In the last 3-4 decades, resampling of soil profiles demonstrated that under long-term pasture on flat land, soil C had subsequently declined for allophanic, gley and organic soils by 0.54, 0.32 and 2.9 t C ha
−1
y
−1
, respectively, and soil C had not changed in the remainder of sampled soil orders. For the same time period, pasture soils on stable midslopes of hill country gained 0.6 t C ha
−1
y
−1
. Whether these changes are ongoing is not known, except for the organic soils where losses will continue so long as they are drained. Phosphorus fertiliser application did not change C stocks. Irrigation decreased carbon by 7 t C ha
−1
. Carbon losses during pasture renewal ranged between 0.8 and 4.1 t C ha
−1
. Some evidence suggests tussock grasslands can gain C when fertilised and not overgrazed. When combined to the national scale, different data sets suggest either no change or a gain of C, but with large uncertainties. We highlight key land-use practices and soil orders that require further information of soil C stock changes and advocate for a better understanding of underpinning reasons for changes in soil C.</description><identifier>ISSN: 0028-8233</identifier><identifier>ISSN: 1175-8775</identifier><identifier>EISSN: 1175-8775</identifier><identifier>DOI: 10.1080/00288233.2017.1284134</identifier><language>eng</language><publisher>Abingdon: Taylor & Francis</publisher><subject>Carbon ; Carbon content ; Deforestation ; Grasslands ; grazed ; land use ; management ; New Zealand ; pasture ; Pastures ; soil ; Soils</subject><ispartof>New Zealand journal of agricultural research, 2017-06, Vol.60 (2), p.93-118</ispartof><rights>2017 The Royal Society of New Zealand 2017</rights><rights>2017 The Royal Society of New Zealand</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c432t-8c5e2259c8bfff0556924f43f76140bd7e89f692bc7cccf6cb5ae2f64612ddd83</citedby><cites>FETCH-LOGICAL-c432t-8c5e2259c8bfff0556924f43f76140bd7e89f692bc7cccf6cb5ae2f64612ddd83</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,778,782,27911,27912</link.rule.ids><backlink>$$Uhttps://natlib-primo.hosted.exlibrisgroup.com/primo-explore/search?query=any,contains,998940339802837&tab=innz&search_scope=INNZ&vid=NLNZ&offset=0$$DView this record in NLNZ$$Hfree_for_read</backlink></links><search><creatorcontrib>Schipper, Louis A.</creatorcontrib><creatorcontrib>Mudge, Paul L.</creatorcontrib><creatorcontrib>Kirschbaum, Miko U. F.</creatorcontrib><creatorcontrib>Hedley, Carolyn B.</creatorcontrib><creatorcontrib>Golubiewski, Nancy E.</creatorcontrib><creatorcontrib>Smaill, Simeon J.</creatorcontrib><creatorcontrib>Kelliher, Francis M.</creatorcontrib><title>A review of soil carbon change in New Zealand's grazed grasslands</title><title>New Zealand journal of agricultural research</title><description>Soil organic matter is a potential sink of atmospheric carbon (C) and critical for maintaining soil quality. We reviewed New Zealand studies of soil C changes after conversion from woody vegetation to pasture, and under long-term pasture. Soil C increased by about 13.7 t C ha
−1
to a new steady state when forests were initially converted to pasture. In the last 3-4 decades, resampling of soil profiles demonstrated that under long-term pasture on flat land, soil C had subsequently declined for allophanic, gley and organic soils by 0.54, 0.32 and 2.9 t C ha
−1
y
−1
, respectively, and soil C had not changed in the remainder of sampled soil orders. For the same time period, pasture soils on stable midslopes of hill country gained 0.6 t C ha
−1
y
−1
. Whether these changes are ongoing is not known, except for the organic soils where losses will continue so long as they are drained. Phosphorus fertiliser application did not change C stocks. Irrigation decreased carbon by 7 t C ha
−1
. Carbon losses during pasture renewal ranged between 0.8 and 4.1 t C ha
−1
. Some evidence suggests tussock grasslands can gain C when fertilised and not overgrazed. When combined to the national scale, different data sets suggest either no change or a gain of C, but with large uncertainties. We highlight key land-use practices and soil orders that require further information of soil C stock changes and advocate for a better understanding of underpinning reasons for changes in soil C.</description><subject>Carbon</subject><subject>Carbon content</subject><subject>Deforestation</subject><subject>Grasslands</subject><subject>grazed</subject><subject>land use</subject><subject>management</subject><subject>New Zealand</subject><subject>pasture</subject><subject>Pastures</subject><subject>soil</subject><subject>Soils</subject><issn>0028-8233</issn><issn>1175-8775</issn><issn>1175-8775</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2017</creationdate><recordtype>article</recordtype><recordid>eNp9kEtLAzEUhYMoWKs_QRhw4WpqnpNkZym-oOhGN25CJo86ZZrUpLW2v94ZWnHn6nDv_e493APAJYIjBAW8gRALgQkZYYj4CGFBEaFHYIAQZ6XgnB2DQc-UPXQKznKed2VFhRyA8bhI7qtxmyL6IsemLYxOdQyF-dBh5oomFM_d8N3pVgd7nYtZ0jtne8m5b-VzcOJ1m93FQYfg7f7udfJYTl8enibjaWkowatSGOYwZtKI2nsPGaskpp4SzytEYW25E9J3vdpwY4yvTM20w76iFcLWWkGG4Gp_d5ni59rllZrHdQqdpUJCYk6673uK7SmTYs7JebVMzUKnrUJQ9Wmp37RUn5Y6pPV3PbRhp5pg3XenUgpJISFSdEuEd9TtnmqCj2mhNzG1Vq30to3JJx1MkxX53-gHW3x6cw</recordid><startdate>20170601</startdate><enddate>20170601</enddate><creator>Schipper, Louis A.</creator><creator>Mudge, Paul L.</creator><creator>Kirschbaum, Miko U. F.</creator><creator>Hedley, Carolyn B.</creator><creator>Golubiewski, Nancy E.</creator><creator>Smaill, Simeon J.</creator><creator>Kelliher, Francis M.</creator><general>Taylor & Francis</general><general>Taylor & Francis Ltd</general><scope>DUNLO</scope><scope>GOM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QL</scope><scope>7SS</scope><scope>7ST</scope><scope>7T7</scope><scope>7U9</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>H94</scope><scope>M7N</scope><scope>P64</scope><scope>SOI</scope></search><sort><creationdate>20170601</creationdate><title>A review of soil carbon change in New Zealand's grazed grasslands</title><author>Schipper, Louis A. ; Mudge, Paul L. ; Kirschbaum, Miko U. F. ; Hedley, Carolyn B. ; Golubiewski, Nancy E. ; Smaill, Simeon J. ; Kelliher, Francis M.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c432t-8c5e2259c8bfff0556924f43f76140bd7e89f692bc7cccf6cb5ae2f64612ddd83</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2017</creationdate><topic>Carbon</topic><topic>Carbon content</topic><topic>Deforestation</topic><topic>Grasslands</topic><topic>grazed</topic><topic>land use</topic><topic>management</topic><topic>New Zealand</topic><topic>pasture</topic><topic>Pastures</topic><topic>soil</topic><topic>Soils</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Schipper, Louis A.</creatorcontrib><creatorcontrib>Mudge, Paul L.</creatorcontrib><creatorcontrib>Kirschbaum, Miko U. F.</creatorcontrib><creatorcontrib>Hedley, Carolyn B.</creatorcontrib><creatorcontrib>Golubiewski, Nancy E.</creatorcontrib><creatorcontrib>Smaill, Simeon J.</creatorcontrib><creatorcontrib>Kelliher, Francis M.</creatorcontrib><collection>Index New Zealand (A&I)</collection><collection>Index New Zealand</collection><collection>CrossRef</collection><collection>Bacteriology Abstracts (Microbiology B)</collection><collection>Entomology Abstracts (Full archive)</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Virology and AIDS Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>AIDS and Cancer Research Abstracts</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environment Abstracts</collection><jtitle>New Zealand journal of agricultural research</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Schipper, Louis A.</au><au>Mudge, Paul L.</au><au>Kirschbaum, Miko U. F.</au><au>Hedley, Carolyn B.</au><au>Golubiewski, Nancy E.</au><au>Smaill, Simeon J.</au><au>Kelliher, Francis M.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>A review of soil carbon change in New Zealand's grazed grasslands</atitle><jtitle>New Zealand journal of agricultural research</jtitle><date>2017-06-01</date><risdate>2017</risdate><volume>60</volume><issue>2</issue><spage>93</spage><epage>118</epage><pages>93-118</pages><issn>0028-8233</issn><issn>1175-8775</issn><eissn>1175-8775</eissn><abstract>Soil organic matter is a potential sink of atmospheric carbon (C) and critical for maintaining soil quality. We reviewed New Zealand studies of soil C changes after conversion from woody vegetation to pasture, and under long-term pasture. Soil C increased by about 13.7 t C ha
−1
to a new steady state when forests were initially converted to pasture. In the last 3-4 decades, resampling of soil profiles demonstrated that under long-term pasture on flat land, soil C had subsequently declined for allophanic, gley and organic soils by 0.54, 0.32 and 2.9 t C ha
−1
y
−1
, respectively, and soil C had not changed in the remainder of sampled soil orders. For the same time period, pasture soils on stable midslopes of hill country gained 0.6 t C ha
−1
y
−1
. Whether these changes are ongoing is not known, except for the organic soils where losses will continue so long as they are drained. Phosphorus fertiliser application did not change C stocks. Irrigation decreased carbon by 7 t C ha
−1
. Carbon losses during pasture renewal ranged between 0.8 and 4.1 t C ha
−1
. Some evidence suggests tussock grasslands can gain C when fertilised and not overgrazed. When combined to the national scale, different data sets suggest either no change or a gain of C, but with large uncertainties. We highlight key land-use practices and soil orders that require further information of soil C stock changes and advocate for a better understanding of underpinning reasons for changes in soil C.</abstract><cop>Abingdon</cop><pub>Taylor & Francis</pub><doi>10.1080/00288233.2017.1284134</doi><tpages>26</tpages></addata></record> |
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source | Royal Society of New Zealand Open Access Journals; EZB-FREE-00999 freely available EZB journals |
subjects | Carbon Carbon content Deforestation Grasslands grazed land use management New Zealand pasture Pastures soil Soils |
title | A review of soil carbon change in New Zealand's grazed grasslands |
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