Influence of water depth and soil amelioration on greenhouse gas emissions from peat soil columns
Recently, large areas of tropical peatland have been converted into agricultural fields. To be used for agricultural activities, peat soils need to be drained, limed and fertilized due to excess water, low nutrient content and high acidity. Water depth and amelioration have significant effects on gr...
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creator | Susilawati, Helena Lina Setyanto, Prihasto Ariani, Miranti Hervani, Anggri Inubushi, Kazuyuki |
description | Recently, large areas of tropical peatland have been converted into agricultural fields. To be used for agricultural activities, peat soils need to be drained, limed and fertilized due to excess water, low nutrient content and high acidity. Water depth and amelioration have significant effects on greenhouse gas (GHG) production. Twenty-seven soil samples were collected from Jabiren, Central Kalimantan, Indonesia, in 2014 to examine the effect of water depth and amelioration on GHG emissions. Soil columns were formed in the peatland using polyvinyl chloride (PVC) pipe with a diameter of 21 cm and a length of 100 cm. The PVC pipe was inserted vertically into the soil to a depth of 100 cm and carefully pulled up with the soil inside after sealing the bottom. The treatments consisting of three static water depths (15, 35 and 55 cm from the soil surface) and three ameliorants (without ameliorant/control, biochar+compost and steel slag+compost) were arranged using a randomized block design with two factors and three replications. Fluxes of carbon dioxide (CO ₂), methane (CH ₄) and nitrous oxide (N ₂O) from the soil columns were measured weekly. There was a linear relationship between water depth and CO ₂ emissions. No significant difference was observed in the CH ₄ emissions in response to water depth and amelioration. The ameliorations influenced the CO ₂ and N ₂O emissions from the peat soil. The application of biochar+compost enhanced the CO ₂ and N ₂O emissions but reduced the CH ₄ emission. Moreover, the application of steel slag+compost increased the emissions of all three gases. The highest CO ₂ and N ₂O emissions occurred in response to the biochar+compost treatment followed by the steel slag-compost treatment and without ameliorant. Soil pH, redox potential (Eh) and temperature influenced the CO ₂, CH ₄ and N ₂O fluxes. Experiments for monitoring water depth and amelioration should be developed using peat soil as well as peat soil–crop systems. |
doi_str_mv | 10.1080/00380768.2015.1107459 |
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To be used for agricultural activities, peat soils need to be drained, limed and fertilized due to excess water, low nutrient content and high acidity. Water depth and amelioration have significant effects on greenhouse gas (GHG) production. Twenty-seven soil samples were collected from Jabiren, Central Kalimantan, Indonesia, in 2014 to examine the effect of water depth and amelioration on GHG emissions. Soil columns were formed in the peatland using polyvinyl chloride (PVC) pipe with a diameter of 21 cm and a length of 100 cm. The PVC pipe was inserted vertically into the soil to a depth of 100 cm and carefully pulled up with the soil inside after sealing the bottom. The treatments consisting of three static water depths (15, 35 and 55 cm from the soil surface) and three ameliorants (without ameliorant/control, biochar+compost and steel slag+compost) were arranged using a randomized block design with two factors and three replications. Fluxes of carbon dioxide (CO ₂), methane (CH ₄) and nitrous oxide (N ₂O) from the soil columns were measured weekly. There was a linear relationship between water depth and CO ₂ emissions. No significant difference was observed in the CH ₄ emissions in response to water depth and amelioration. The ameliorations influenced the CO ₂ and N ₂O emissions from the peat soil. The application of biochar+compost enhanced the CO ₂ and N ₂O emissions but reduced the CH ₄ emission. Moreover, the application of steel slag+compost increased the emissions of all three gases. The highest CO ₂ and N ₂O emissions occurred in response to the biochar+compost treatment followed by the steel slag-compost treatment and without ameliorant. Soil pH, redox potential (Eh) and temperature influenced the CO ₂, CH ₄ and N ₂O fluxes. Experiments for monitoring water depth and amelioration should be developed using peat soil as well as peat soil–crop systems.</description><identifier>ISSN: 1747-0765</identifier><identifier>ISSN: 0038-0768</identifier><identifier>EISSN: 1747-0765</identifier><identifier>DOI: 10.1080/00380768.2015.1107459</identifier><language>eng</language><publisher>Kyoto: Taylor & Francis</publisher><subject>acidity ; Biochar ; carbon dioxide ; gases ; greenhouse effect ; greenhouse gas emissions ; greenhouse gases ; methane ; monitoring ; nitrous oxide ; nutrient content ; peat ; peat soils ; peatlands ; poly(vinyl chloride) ; redox potential ; soil depth ; soil pH ; soil sampling ; steel ; steel slag ; temperature ; water tables</subject><ispartof>Soil science and plant nutrition (Tokyo), 2016-01, Vol.62 (1), p.57-68</ispartof><rights>2015 Japanese Society of Soil Science and Plant Nutrition 2015</rights><rights>2015 Japanese Society of Soil Science and Plant Nutrition</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c578t-2a7a52f291e859c69a5c1c26984f5dcb21385f0d22806e058ad8938a3e7ad1463</citedby><cites>FETCH-LOGICAL-c578t-2a7a52f291e859c69a5c1c26984f5dcb21385f0d22806e058ad8938a3e7ad1463</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27903,27904</link.rule.ids></links><search><creatorcontrib>Susilawati, Helena Lina</creatorcontrib><creatorcontrib>Setyanto, Prihasto</creatorcontrib><creatorcontrib>Ariani, Miranti</creatorcontrib><creatorcontrib>Hervani, Anggri</creatorcontrib><creatorcontrib>Inubushi, Kazuyuki</creatorcontrib><title>Influence of water depth and soil amelioration on greenhouse gas emissions from peat soil columns</title><title>Soil science and plant nutrition (Tokyo)</title><description>Recently, large areas of tropical peatland have been converted into agricultural fields. To be used for agricultural activities, peat soils need to be drained, limed and fertilized due to excess water, low nutrient content and high acidity. Water depth and amelioration have significant effects on greenhouse gas (GHG) production. Twenty-seven soil samples were collected from Jabiren, Central Kalimantan, Indonesia, in 2014 to examine the effect of water depth and amelioration on GHG emissions. Soil columns were formed in the peatland using polyvinyl chloride (PVC) pipe with a diameter of 21 cm and a length of 100 cm. The PVC pipe was inserted vertically into the soil to a depth of 100 cm and carefully pulled up with the soil inside after sealing the bottom. The treatments consisting of three static water depths (15, 35 and 55 cm from the soil surface) and three ameliorants (without ameliorant/control, biochar+compost and steel slag+compost) were arranged using a randomized block design with two factors and three replications. Fluxes of carbon dioxide (CO ₂), methane (CH ₄) and nitrous oxide (N ₂O) from the soil columns were measured weekly. There was a linear relationship between water depth and CO ₂ emissions. No significant difference was observed in the CH ₄ emissions in response to water depth and amelioration. The ameliorations influenced the CO ₂ and N ₂O emissions from the peat soil. The application of biochar+compost enhanced the CO ₂ and N ₂O emissions but reduced the CH ₄ emission. Moreover, the application of steel slag+compost increased the emissions of all three gases. The highest CO ₂ and N ₂O emissions occurred in response to the biochar+compost treatment followed by the steel slag-compost treatment and without ameliorant. Soil pH, redox potential (Eh) and temperature influenced the CO ₂, CH ₄ and N ₂O fluxes. Experiments for monitoring water depth and amelioration should be developed using peat soil as well as peat soil–crop systems.</description><subject>acidity</subject><subject>Biochar</subject><subject>carbon dioxide</subject><subject>gases</subject><subject>greenhouse effect</subject><subject>greenhouse gas emissions</subject><subject>greenhouse gases</subject><subject>methane</subject><subject>monitoring</subject><subject>nitrous oxide</subject><subject>nutrient content</subject><subject>peat</subject><subject>peat soils</subject><subject>peatlands</subject><subject>poly(vinyl chloride)</subject><subject>redox potential</subject><subject>soil depth</subject><subject>soil pH</subject><subject>soil sampling</subject><subject>steel</subject><subject>steel slag</subject><subject>temperature</subject><subject>water tables</subject><issn>1747-0765</issn><issn>0038-0768</issn><issn>1747-0765</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2016</creationdate><recordtype>article</recordtype><recordid>eNqFkUtLxDAUhYso-PwJYsCNmxnzaNp0p4gvGHChrsM1vZmppMmYtIj_3gwdQdwIgQTud849nBTFKaNzRhW9pFQoWldqzimTc8ZoXcpmpzhgdVnP8kDu_nrvF4cpvVNalkLygwIevXUjeoMkWPIJA0bS4npYEfAtSaFzBHp0XYgwdMGTfJYR0a_CmJAsIRHsu5TyKBEbQ0_WCMOkM8GNvU_HxZ4Fl_Bkex8Vr3e3LzcPs8XT_ePN9WJmZK2GGYcaJLe8YahkY6oGpGGGV40qrWzNG2dCSUtbzhWtkEoFrWqEAoE1tKysxFFxMfmuY_gYMQ06BzPoHHjMYTXLDcm6bPgGPf-Dvocx-pxuQ_G8shE8U3KiTAwpRbR6Hbse4pdmVG-K1z_F603xelt81l1Nus7bEHv4DNG1eoAvF6KN4E2XtPjP4myysBA0LGNWvD5noqKUMZE_TnwDQRiSxA</recordid><startdate>20160102</startdate><enddate>20160102</enddate><creator>Susilawati, Helena Lina</creator><creator>Setyanto, Prihasto</creator><creator>Ariani, Miranti</creator><creator>Hervani, Anggri</creator><creator>Inubushi, Kazuyuki</creator><general>Taylor & Francis</general><general>Taylor & Francis Ltd</general><scope>FBQ</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QL</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>7QH</scope><scope>7UA</scope></search><sort><creationdate>20160102</creationdate><title>Influence of water depth and soil amelioration on greenhouse gas emissions from peat soil columns</title><author>Susilawati, Helena Lina ; Setyanto, Prihasto ; Ariani, Miranti ; Hervani, Anggri ; Inubushi, Kazuyuki</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c578t-2a7a52f291e859c69a5c1c26984f5dcb21385f0d22806e058ad8938a3e7ad1463</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2016</creationdate><topic>acidity</topic><topic>Biochar</topic><topic>carbon dioxide</topic><topic>gases</topic><topic>greenhouse effect</topic><topic>greenhouse gas emissions</topic><topic>greenhouse gases</topic><topic>methane</topic><topic>monitoring</topic><topic>nitrous oxide</topic><topic>nutrient content</topic><topic>peat</topic><topic>peat soils</topic><topic>peatlands</topic><topic>poly(vinyl chloride)</topic><topic>redox potential</topic><topic>soil depth</topic><topic>soil pH</topic><topic>soil sampling</topic><topic>steel</topic><topic>steel slag</topic><topic>temperature</topic><topic>water tables</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Susilawati, Helena Lina</creatorcontrib><creatorcontrib>Setyanto, Prihasto</creatorcontrib><creatorcontrib>Ariani, Miranti</creatorcontrib><creatorcontrib>Hervani, Anggri</creatorcontrib><creatorcontrib>Inubushi, Kazuyuki</creatorcontrib><collection>AGRIS</collection><collection>CrossRef</collection><collection>Bacteriology Abstracts (Microbiology B)</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>Aqualine</collection><collection>Water Resources Abstracts</collection><jtitle>Soil science and plant nutrition (Tokyo)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Susilawati, Helena Lina</au><au>Setyanto, Prihasto</au><au>Ariani, Miranti</au><au>Hervani, Anggri</au><au>Inubushi, Kazuyuki</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Influence of water depth and soil amelioration on greenhouse gas emissions from peat soil columns</atitle><jtitle>Soil science and plant nutrition (Tokyo)</jtitle><date>2016-01-02</date><risdate>2016</risdate><volume>62</volume><issue>1</issue><spage>57</spage><epage>68</epage><pages>57-68</pages><issn>1747-0765</issn><issn>0038-0768</issn><eissn>1747-0765</eissn><abstract>Recently, large areas of tropical peatland have been converted into agricultural fields. To be used for agricultural activities, peat soils need to be drained, limed and fertilized due to excess water, low nutrient content and high acidity. Water depth and amelioration have significant effects on greenhouse gas (GHG) production. Twenty-seven soil samples were collected from Jabiren, Central Kalimantan, Indonesia, in 2014 to examine the effect of water depth and amelioration on GHG emissions. Soil columns were formed in the peatland using polyvinyl chloride (PVC) pipe with a diameter of 21 cm and a length of 100 cm. The PVC pipe was inserted vertically into the soil to a depth of 100 cm and carefully pulled up with the soil inside after sealing the bottom. The treatments consisting of three static water depths (15, 35 and 55 cm from the soil surface) and three ameliorants (without ameliorant/control, biochar+compost and steel slag+compost) were arranged using a randomized block design with two factors and three replications. Fluxes of carbon dioxide (CO ₂), methane (CH ₄) and nitrous oxide (N ₂O) from the soil columns were measured weekly. There was a linear relationship between water depth and CO ₂ emissions. No significant difference was observed in the CH ₄ emissions in response to water depth and amelioration. The ameliorations influenced the CO ₂ and N ₂O emissions from the peat soil. The application of biochar+compost enhanced the CO ₂ and N ₂O emissions but reduced the CH ₄ emission. Moreover, the application of steel slag+compost increased the emissions of all three gases. The highest CO ₂ and N ₂O emissions occurred in response to the biochar+compost treatment followed by the steel slag-compost treatment and without ameliorant. Soil pH, redox potential (Eh) and temperature influenced the CO ₂, CH ₄ and N ₂O fluxes. Experiments for monitoring water depth and amelioration should be developed using peat soil as well as peat soil–crop systems.</abstract><cop>Kyoto</cop><pub>Taylor & Francis</pub><doi>10.1080/00380768.2015.1107459</doi><tpages>12</tpages><oa>free_for_read</oa></addata></record> |
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subjects | acidity Biochar carbon dioxide gases greenhouse effect greenhouse gas emissions greenhouse gases methane monitoring nitrous oxide nutrient content peat peat soils peatlands poly(vinyl chloride) redox potential soil depth soil pH soil sampling steel steel slag temperature water tables |
title | Influence of water depth and soil amelioration on greenhouse gas emissions from peat soil columns |
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