Comparison between APSIM and NZ-DNDC models when describing N-dynamics under urine patches
Nitrous oxide (N ₂O) emissions from soil are the result of complex interactions between physical, chemical and biological processes. We compared two process-based models (APSIM and NZ-DNDC) with measurements of N ₂O emissions, soil and content (0–75 mm) and water-filled pore space from a series of f...
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Veröffentlicht in: | New Zealand journal of agricultural research 2015-04, Vol.58 (2), p.131-155 |
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description | Nitrous oxide (N ₂O) emissions from soil are the result of complex interactions between physical, chemical and biological processes. We compared two process-based models (APSIM and NZ-DNDC) with measurements of N ₂O emissions, soil and content (0–75 mm) and water-filled pore space from a series of field campaigns where known amounts of animal urine-N were applied to four soil types under permanent pastures, in two regions within New Zealand, at different times of the year. We also compared cumulative N ₂O emissions with an N ₂O inventory emission factor approach (EF ₃ method). Overall, the two process-based models performed less well than the EF ₃ method for simulating cumulative N ₂O emissions over the complete data set. However, in winter, the APSIM model correlated well with measurements (r = 0.97), while NZ-DNDC performed well on the Otago soils (r = 0.83 and 0.92 for Wingatui and Otokia, respectively). The process-based models have the potential to account for the effect of weather conditions and soil type on N ₂O emissions that are not accounted for by the EF ₃ method. However, further improvements are currently needed. The fractions of N lost to different processes within the complex soil–plant atmosphere system differed between the two models. The size of the predicted plant uptake, leaching and NH ₃ volatilisation fluxes are large compared with N ₂O emissions and could affect the simulated soil N pools and thus the predicted N ₂O fluxes. To simulate N ₂O fluxes accurately, it is therefore important to ensure these processes are well modelled and further validation studies are needed. |
doi_str_mv | 10.1080/00288233.2014.987876 |
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We compared two process-based models (APSIM and NZ-DNDC) with measurements of N ₂O emissions, soil and content (0–75 mm) and water-filled pore space from a series of field campaigns where known amounts of animal urine-N were applied to four soil types under permanent pastures, in two regions within New Zealand, at different times of the year. We also compared cumulative N ₂O emissions with an N ₂O inventory emission factor approach (EF ₃ method). Overall, the two process-based models performed less well than the EF ₃ method for simulating cumulative N ₂O emissions over the complete data set. However, in winter, the APSIM model correlated well with measurements (r = 0.97), while NZ-DNDC performed well on the Otago soils (r = 0.83 and 0.92 for Wingatui and Otokia, respectively). The process-based models have the potential to account for the effect of weather conditions and soil type on N ₂O emissions that are not accounted for by the EF ₃ method. However, further improvements are currently needed. The fractions of N lost to different processes within the complex soil–plant atmosphere system differed between the two models. The size of the predicted plant uptake, leaching and NH ₃ volatilisation fluxes are large compared with N ₂O emissions and could affect the simulated soil N pools and thus the predicted N ₂O fluxes. To simulate N ₂O fluxes accurately, it is therefore important to ensure these processes are well modelled and further validation studies are needed.</description><identifier>ISSN: 1175-8775</identifier><identifier>ISSN: 0028-8233</identifier><identifier>EISSN: 1175-8775</identifier><identifier>DOI: 10.1080/00288233.2014.987876</identifier><language>eng</language><publisher>Abingdon: Taylor & Francis</publisher><subject>ammonia ; Analysis ; Animal waste ; animals ; APSIM ; Computer simulation ; data collection ; Emissions ; emissions factor ; Evaluation ; inventories ; leaching ; Measurement ; nitrogen ; Nitrous oxide ; NZ-DNDC ; permanent grasslands ; process-based modelling ; soil types ; Urine ; urine patch ; volatilization ; weather ; winter</subject><ispartof>New Zealand journal of agricultural research, 2015-04, Vol.58 (2), p.131-155</ispartof><rights>2015 Landcare Research New Zealand Ltd 2015</rights><rights>2015 Landcare Research New Zealand Ltd</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c433t-d9744c5e979dd1e64cc49366f6561b7605da7fe61583417f5e139e9ab04bbc433</citedby><cites>FETCH-LOGICAL-c433t-d9744c5e979dd1e64cc49366f6561b7605da7fe61583417f5e139e9ab04bbc433</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27901,27902</link.rule.ids><backlink>$$Uhttps://natlib-primo.hosted.exlibrisgroup.com/primo-explore/search?query=any,contains,998397503602837&tab=innz&search_scope=INNZ&vid=NLNZ&offset=0$$DView this record in NLNZ$$Hfree_for_read</backlink></links><search><creatorcontrib>Giltrap, DL</creatorcontrib><creatorcontrib>Vogeler, I</creatorcontrib><creatorcontrib>Cichota, R</creatorcontrib><creatorcontrib>Luo, J</creatorcontrib><creatorcontrib>van der Weerden, TJ</creatorcontrib><creatorcontrib>de Klein, CAM</creatorcontrib><title>Comparison between APSIM and NZ-DNDC models when describing N-dynamics under urine patches</title><title>New Zealand journal of agricultural research</title><addtitle>Comparison between Agricultural Production Systems Simulator and New Zealand version of the DeNitrification-DeComposition models when describing Nitrogen-dynamics under urine patches</addtitle><description>Nitrous oxide (N ₂O) emissions from soil are the result of complex interactions between physical, chemical and biological processes. We compared two process-based models (APSIM and NZ-DNDC) with measurements of N ₂O emissions, soil and content (0–75 mm) and water-filled pore space from a series of field campaigns where known amounts of animal urine-N were applied to four soil types under permanent pastures, in two regions within New Zealand, at different times of the year. We also compared cumulative N ₂O emissions with an N ₂O inventory emission factor approach (EF ₃ method). Overall, the two process-based models performed less well than the EF ₃ method for simulating cumulative N ₂O emissions over the complete data set. However, in winter, the APSIM model correlated well with measurements (r = 0.97), while NZ-DNDC performed well on the Otago soils (r = 0.83 and 0.92 for Wingatui and Otokia, respectively). The process-based models have the potential to account for the effect of weather conditions and soil type on N ₂O emissions that are not accounted for by the EF ₃ method. However, further improvements are currently needed. The fractions of N lost to different processes within the complex soil–plant atmosphere system differed between the two models. The size of the predicted plant uptake, leaching and NH ₃ volatilisation fluxes are large compared with N ₂O emissions and could affect the simulated soil N pools and thus the predicted N ₂O fluxes. To simulate N ₂O fluxes accurately, it is therefore important to ensure these processes are well modelled and further validation studies are needed.</description><subject>ammonia</subject><subject>Analysis</subject><subject>Animal waste</subject><subject>animals</subject><subject>APSIM</subject><subject>Computer simulation</subject><subject>data collection</subject><subject>Emissions</subject><subject>emissions factor</subject><subject>Evaluation</subject><subject>inventories</subject><subject>leaching</subject><subject>Measurement</subject><subject>nitrogen</subject><subject>Nitrous oxide</subject><subject>NZ-DNDC</subject><subject>permanent grasslands</subject><subject>process-based modelling</subject><subject>soil types</subject><subject>Urine</subject><subject>urine patch</subject><subject>volatilization</subject><subject>weather</subject><subject>winter</subject><issn>1175-8775</issn><issn>0028-8233</issn><issn>1175-8775</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2015</creationdate><recordtype>article</recordtype><recordid>eNqFkctKAzEUhgdR8PoGggHXU5Mmk8tKpN4KWgV14yZkkoxGZpKaTKn16U0ZRXeuzoHznf-QL0VxiOAIQQ5PIBxzPsZ4NIaIjARnnNGNYgchVpWcsWrzT79d7Kb0ljco4WKneJ6Ebq6iS8GD2vZLaz04u3-Y3gLlDZg9l-ez8wnogrFtAsvXPDU26ehq51_ArDQrrzqnE1h4YyNYROctmKtev9q0X2w1qk324LvuFU-XF4-T6_Lm7mo6ObspNcG4L41ghOjKCiaMQZYSrYnAlDa0oqhmFFZGscZSVHFMEGsqi7CwQtWQ1PU6Yq84HnLnMbwvbOrlW1hEn09KRBmHHGFCM0UGSseQUrSNnEfXqbiSCMq1RfljUa4tysHib7hv_ad0-ZUfuQrBsWAVxDTvYJap04FyvgmxU8sQWyN7tWpDbKLy2iWJ_7lzNCQ0Kkj1kj9EPj1kgEIImcgS8BfZzYsj</recordid><startdate>20150403</startdate><enddate>20150403</enddate><creator>Giltrap, DL</creator><creator>Vogeler, I</creator><creator>Cichota, R</creator><creator>Luo, J</creator><creator>van der Weerden, TJ</creator><creator>de Klein, CAM</creator><general>Taylor & Francis</general><general>Taylor & Francis Ltd</general><scope>FBQ</scope><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>20150403</creationdate><title>Comparison between APSIM and NZ-DNDC models when describing N-dynamics under urine patches</title><author>Giltrap, DL ; Vogeler, I ; Cichota, R ; Luo, J ; van der Weerden, TJ ; de Klein, CAM</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c433t-d9744c5e979dd1e64cc49366f6561b7605da7fe61583417f5e139e9ab04bbc433</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2015</creationdate><topic>ammonia</topic><topic>Analysis</topic><topic>Animal waste</topic><topic>animals</topic><topic>APSIM</topic><topic>Computer simulation</topic><topic>data collection</topic><topic>Emissions</topic><topic>emissions factor</topic><topic>Evaluation</topic><topic>inventories</topic><topic>leaching</topic><topic>Measurement</topic><topic>nitrogen</topic><topic>Nitrous oxide</topic><topic>NZ-DNDC</topic><topic>permanent grasslands</topic><topic>process-based modelling</topic><topic>soil types</topic><topic>Urine</topic><topic>urine patch</topic><topic>volatilization</topic><topic>weather</topic><topic>winter</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Giltrap, DL</creatorcontrib><creatorcontrib>Vogeler, I</creatorcontrib><creatorcontrib>Cichota, R</creatorcontrib><creatorcontrib>Luo, J</creatorcontrib><creatorcontrib>van der Weerden, TJ</creatorcontrib><creatorcontrib>de Klein, CAM</creatorcontrib><collection>AGRIS</collection><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>Giltrap, DL</au><au>Vogeler, I</au><au>Cichota, R</au><au>Luo, J</au><au>van der Weerden, TJ</au><au>de Klein, CAM</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Comparison between APSIM and NZ-DNDC models when describing N-dynamics under urine patches</atitle><jtitle>New Zealand journal of agricultural research</jtitle><addtitle>Comparison between Agricultural Production Systems Simulator and New Zealand version of the DeNitrification-DeComposition models when describing Nitrogen-dynamics under urine patches</addtitle><date>2015-04-03</date><risdate>2015</risdate><volume>58</volume><issue>2</issue><spage>131</spage><epage>155</epage><pages>131-155</pages><issn>1175-8775</issn><issn>0028-8233</issn><eissn>1175-8775</eissn><abstract>Nitrous oxide (N ₂O) emissions from soil are the result of complex interactions between physical, chemical and biological processes. We compared two process-based models (APSIM and NZ-DNDC) with measurements of N ₂O emissions, soil and content (0–75 mm) and water-filled pore space from a series of field campaigns where known amounts of animal urine-N were applied to four soil types under permanent pastures, in two regions within New Zealand, at different times of the year. We also compared cumulative N ₂O emissions with an N ₂O inventory emission factor approach (EF ₃ method). Overall, the two process-based models performed less well than the EF ₃ method for simulating cumulative N ₂O emissions over the complete data set. However, in winter, the APSIM model correlated well with measurements (r = 0.97), while NZ-DNDC performed well on the Otago soils (r = 0.83 and 0.92 for Wingatui and Otokia, respectively). The process-based models have the potential to account for the effect of weather conditions and soil type on N ₂O emissions that are not accounted for by the EF ₃ method. However, further improvements are currently needed. The fractions of N lost to different processes within the complex soil–plant atmosphere system differed between the two models. The size of the predicted plant uptake, leaching and NH ₃ volatilisation fluxes are large compared with N ₂O emissions and could affect the simulated soil N pools and thus the predicted N ₂O fluxes. To simulate N ₂O fluxes accurately, it is therefore important to ensure these processes are well modelled and further validation studies are needed.</abstract><cop>Abingdon</cop><pub>Taylor & Francis</pub><doi>10.1080/00288233.2014.987876</doi><tpages>25</tpages><oa>free_for_read</oa></addata></record> |
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subjects | ammonia Analysis Animal waste animals APSIM Computer simulation data collection Emissions emissions factor Evaluation inventories leaching Measurement nitrogen Nitrous oxide NZ-DNDC permanent grasslands process-based modelling soil types Urine urine patch volatilization weather winter |
title | Comparison between APSIM and NZ-DNDC models when describing N-dynamics under urine patches |
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