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A Modelling Approach to Global Nitrate Leaching Caused by Anthropogenic Fertilisation

Identifieur interne : 000467 ( Istex/Corpus ); précédent : 000466; suivant : 000468

A Modelling Approach to Global Nitrate Leaching Caused by Anthropogenic Fertilisation

Auteurs : Bin-Le Lin ; A. Sakoda ; R. Shibasaki ; M. Suzuki

Source :

RBID : ISTEX:A8D0566F5B852D6CCCC0C56A17181A53A0C63DAB

Abstract

Water quality associated with nitrate (NO3−) leaching from agricultural soils is an important environmental issue. This paper describes a new modelling approach to quantitatively evaluate the effect of the use of fertilisers on global nitrate leaching. A global process-based simulation model was previously developed for the nitrogen cycle in terrestrial ecosystems, in which soil inorganic nitrogen in the form of ammonium (NH4+) and NO3− was considered. After introducing data on world fertiliser consumption (FAO, 1995) into the steady-state model, the extent of disturbance to the nitrogen cycle caused by fertilisation was calculated. Although fertilisation resulted in an annual increase in net primary production (NPP, represented as carbon) of 18 Gtyear−1, NO3− leaching and gaseous losses of nitrogen oxides and ammonia were also accelerated. Most regions with heavy fertiliser application (over 100kgha−1year−1) showed a high annual leaching load equal to or more than 20kgha−1year−1. About 2.5% of the land area occupied by terrestrial ecosystems suffered a serious leaching load of more than 30kgha−1year−1. Of the total amount of applied fertilisers (138Tgyear−1) 19% was lost to NO3− leaching, 8% to gaseous ammonia, and 3% to gaseous nitrogen oxides. The rest was assumed to be fixed in the ecosystems through vegetation uptake.

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DOI: 10.1016/S0043-1354(00)00484-X

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ISTEX:A8D0566F5B852D6CCCC0C56A17181A53A0C63DAB

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<div type="abstract" xml:lang="en">Water quality associated with nitrate (NO3−) leaching from agricultural soils is an important environmental issue. This paper describes a new modelling approach to quantitatively evaluate the effect of the use of fertilisers on global nitrate leaching. A global process-based simulation model was previously developed for the nitrogen cycle in terrestrial ecosystems, in which soil inorganic nitrogen in the form of ammonium (NH4+) and NO3− was considered. After introducing data on world fertiliser consumption (FAO, 1995) into the steady-state model, the extent of disturbance to the nitrogen cycle caused by fertilisation was calculated. Although fertilisation resulted in an annual increase in net primary production (NPP, represented as carbon) of 18 Gtyear−1, NO3− leaching and gaseous losses of nitrogen oxides and ammonia were also accelerated. Most regions with heavy fertiliser application (over 100kgha−1year−1) showed a high annual leaching load equal to or more than 20kgha−1year−1. About 2.5% of the land area occupied by terrestrial ecosystems suffered a serious leaching load of more than 30kgha−1year−1. Of the total amount of applied fertilisers (138Tgyear−1) 19% was lost to NO3− leaching, 8% to gaseous ammonia, and 3% to gaseous nitrogen oxides. The rest was assumed to be fixed in the ecosystems through vegetation uptake.</div>
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<note type="content">Fig. 1: Structure of the model of the global biogeochemical nitrogen/carbon cycle.</note>
<note type="content">Fig. 2: Distribution map showing global fertiliser consumption in 1995 based on the FAO database.</note>
<note type="content">Fig. 3: Distribution map of global nitrate leaching in the absence of anthropogenic fertilisation.</note>
<note type="content">Fig. 4: Distribution map of global nitrate leaching after disturbance by anthropogenic fertilisation.</note>
<note type="content">Fig. 5: Leaching-load levels and the amount of land area subject to each level of load (%).</note>
<note type="content">Fig. 6: Comparison between the nitrate leaching load in field experiments and the model-based calculations.</note>
<note type="content">Table 1: Values of soil-specific parameters used in the model calculations</note>
<note type="content">Table 2: Databases of environmental variables, soil texture, and vegetation type used in model calculations</note>
<note type="content">Table 3: Fertiliser consumption, fertiliser load, and percentage of occupied area in each fertiliser load based on the database of FAO (1995)</note>
<note type="content">Table 4: Flux changes caused by the disturbance of anthropogenic fertilisation</note>
<note type="content">Table 5: Nitrate leaching load at various sites related to fertilisation</note>
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<ce:sup></ce:sup>
leaching and gaseous losses of nitrogen oxides and ammonia were also accelerated. Most regions with heavy fertiliser application (over 100
<ce:hsp sp="0.16"></ce:hsp>
kg
<ce:hsp sp="0.16"></ce:hsp>
ha
<ce:sup>−1</ce:sup>
<ce:hsp sp="0.16"></ce:hsp>
year
<ce:sup>−1</ce:sup>
) showed a high annual leaching load equal to or more than 20
<ce:hsp sp="0.16"></ce:hsp>
kg
<ce:hsp sp="0.16"></ce:hsp>
ha
<ce:sup>−1</ce:sup>
<ce:hsp sp="0.16"></ce:hsp>
year
<ce:sup>−1</ce:sup>
. About 2.5% of the land area occupied by terrestrial ecosystems suffered a serious leaching load of more than 30
<ce:hsp sp="0.16"></ce:hsp>
kg
<ce:hsp sp="0.16"></ce:hsp>
ha
<ce:sup>−1</ce:sup>
<ce:hsp sp="0.16"></ce:hsp>
year
<ce:sup>−1</ce:sup>
. Of the total amount of applied fertilisers (138
<ce:hsp sp="0.16"></ce:hsp>
Tg
<ce:hsp sp="0.16"></ce:hsp>
year
<ce:sup>−1</ce:sup>
) 19% was lost to NO
<ce:inf>3</ce:inf>
<ce:sup></ce:sup>
leaching, 8% to gaseous ammonia, and 3% to gaseous nitrogen oxides. The rest was assumed to be fixed in the ecosystems through vegetation uptake.</ce:simple-para>
</ce:abstract-sec>
</ce:abstract>
<ce:keywords class="keyword">
<ce:section-title>Keywords</ce:section-title>
<ce:keyword>
<ce:text>global biogeochemical nitrogen cycle</ce:text>
</ce:keyword>
<ce:keyword>
<ce:text>ecosystem model</ce:text>
</ce:keyword>
<ce:keyword>
<ce:text>nitrate leaching</ce:text>
</ce:keyword>
<ce:keyword>
<ce:text>fertilisation</ce:text>
</ce:keyword>
<ce:keyword>
<ce:text>leaching load</ce:text>
</ce:keyword>
</ce:keywords>
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<title>A Modelling Approach to Global Nitrate Leaching Caused by Anthropogenic Fertilisation</title>
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<titleInfo type="alternative" contentType="CDATA">
<title>A Modelling Approach to Global Nitrate Leaching Caused by Anthropogenic Fertilisation</title>
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<name type="personal">
<namePart type="given">Bin-Le</namePart>
<namePart type="family">Lin</namePart>
<affiliation>E-mail: binlelin@iis.u-tokyo.ac.jp</affiliation>
<affiliation>Institute of Industrial Science, University of Tokyo, 7-22-1 Roppongi Minato-ku, Tokyo 106-8558, Japan</affiliation>
<description>Author to whom all correspondence should be addressed. Tel: +81(3)3402-6231 ext. 2413; fax: +81(3)3408-0593</description>
<role>
<roleTerm type="text">author</roleTerm>
</role>
</name>
<name type="personal">
<namePart type="given">A.</namePart>
<namePart type="family">Sakoda</namePart>
<affiliation>Institute of Industrial Science, University of Tokyo, 7-22-1 Roppongi Minato-ku, Tokyo 106-8558, Japan</affiliation>
<role>
<roleTerm type="text">author</roleTerm>
</role>
</name>
<name type="personal">
<namePart type="given">R.</namePart>
<namePart type="family">Shibasaki</namePart>
<affiliation>Center for Spatial Information Science, University of Tokyo, 4-6-1 Komaba Meguro-ku, Tokyo 153-8505, Japan</affiliation>
<role>
<roleTerm type="text">author</roleTerm>
</role>
</name>
<name type="personal">
<namePart type="given">M.</namePart>
<namePart type="family">Suzuki</namePart>
<affiliation>The United Nations University, 5-53-67, Jingumae, Shibuya-ku, Tokyo 150-8304, Japan</affiliation>
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<dateIssued encoding="w3cdtf">2001</dateIssued>
<copyrightDate encoding="w3cdtf">2001</copyrightDate>
</originInfo>
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<languageTerm type="code" authority="iso639-2b">eng</languageTerm>
<languageTerm type="code" authority="rfc3066">en</languageTerm>
</language>
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<abstract lang="en">Water quality associated with nitrate (NO3−) leaching from agricultural soils is an important environmental issue. This paper describes a new modelling approach to quantitatively evaluate the effect of the use of fertilisers on global nitrate leaching. A global process-based simulation model was previously developed for the nitrogen cycle in terrestrial ecosystems, in which soil inorganic nitrogen in the form of ammonium (NH4+) and NO3− was considered. After introducing data on world fertiliser consumption (FAO, 1995) into the steady-state model, the extent of disturbance to the nitrogen cycle caused by fertilisation was calculated. Although fertilisation resulted in an annual increase in net primary production (NPP, represented as carbon) of 18 Gtyear−1, NO3− leaching and gaseous losses of nitrogen oxides and ammonia were also accelerated. Most regions with heavy fertiliser application (over 100kgha−1year−1) showed a high annual leaching load equal to or more than 20kgha−1year−1. About 2.5% of the land area occupied by terrestrial ecosystems suffered a serious leaching load of more than 30kgha−1year−1. Of the total amount of applied fertilisers (138Tgyear−1) 19% was lost to NO3− leaching, 8% to gaseous ammonia, and 3% to gaseous nitrogen oxides. The rest was assumed to be fixed in the ecosystems through vegetation uptake.</abstract>
<note type="content">Fig. 1: Structure of the model of the global biogeochemical nitrogen/carbon cycle.</note>
<note type="content">Fig. 2: Distribution map showing global fertiliser consumption in 1995 based on the FAO database.</note>
<note type="content">Fig. 3: Distribution map of global nitrate leaching in the absence of anthropogenic fertilisation.</note>
<note type="content">Fig. 4: Distribution map of global nitrate leaching after disturbance by anthropogenic fertilisation.</note>
<note type="content">Fig. 5: Leaching-load levels and the amount of land area subject to each level of load (%).</note>
<note type="content">Fig. 6: Comparison between the nitrate leaching load in field experiments and the model-based calculations.</note>
<note type="content">Table 1: Values of soil-specific parameters used in the model calculations</note>
<note type="content">Table 2: Databases of environmental variables, soil texture, and vegetation type used in model calculations</note>
<note type="content">Table 3: Fertiliser consumption, fertiliser load, and percentage of occupied area in each fertiliser load based on the database of FAO (1995)</note>
<note type="content">Table 4: Flux changes caused by the disturbance of anthropogenic fertilisation</note>
<note type="content">Table 5: Nitrate leaching load at various sites related to fertilisation</note>
<subject>
<genre>Keywords</genre>
<topic>global biogeochemical nitrogen cycle</topic>
<topic>ecosystem model</topic>
<topic>nitrate leaching</topic>
<topic>fertilisation</topic>
<topic>leaching load</topic>
</subject>
<relatedItem type="host">
<titleInfo>
<title>Water Research</title>
</titleInfo>
<titleInfo type="abbreviated">
<title>WR</title>
</titleInfo>
<genre type="journal">journal</genre>
<originInfo>
<dateIssued encoding="w3cdtf">200106</dateIssued>
</originInfo>
<identifier type="ISSN">0043-1354</identifier>
<identifier type="PII">S0043-1354(00)X0091-7</identifier>
<part>
<date>200106</date>
<detail type="volume">
<number>35</number>
<caption>vol.</caption>
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<detail type="issue">
<number>8</number>
<caption>no.</caption>
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<start>1861</start>
<end>2100</end>
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<identifier type="istex">A8D0566F5B852D6CCCC0C56A17181A53A0C63DAB</identifier>
<identifier type="DOI">10.1016/S0043-1354(00)00484-X</identifier>
<identifier type="PII">S0043-1354(00)00484-X</identifier>
<accessCondition type="use and reproduction" contentType="copyright">©2001 Elsevier Science Ltd</accessCondition>
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