<rdf:RDF xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:dct="http://purl.org/dc/terms/" xmlns:rdf="http://www.w3.org/1999/02/22-rdf-syntax-ns#">
  <rdf:Description rdf:about="https://doi.org/10.1016/j.agee.2011.11.018">
    <dct:isReferencedBy>IMPACT4SOIL</dct:isReferencedBy>
    <dct:isReferencedBy>OpenAire</dct:isReferencedBy>
    <dct:isReferencedBy>HAL INRAE</dct:isReferencedBy>
    <dct:isReferencedBy>Bielefeld Academic Search Engine (BASE)</dct:isReferencedBy>
    <dct:isReferencedBy>NERC Open Research Archive</dct:isReferencedBy>
    <dct:isReferencedBy>HAL - Universit&#233; de Bourgogne (HAL-uB)</dct:isReferencedBy>
    <dct:isReferencedBy>Crossref</dct:isReferencedBy>
    <dct:isReferencedBy>Agritrop</dct:isReferencedBy>
    <dct:isReferencedBy>Microsoft Academic Graph</dct:isReferencedBy>
    <dct:isPartOf>Agriculture, Ecosystems &amp;amp; Environment</dct:isPartOf>
    <dct:license>Open Access</dct:license>
    <dct:created>2011-12-29</dct:created>
    <dct:available>2016-02-04</dct:available>
    <dc:description>Agroforestry represents an opportunity to reduce CO2 concentrations in the atmosphere by increasing carbon (C) stocks in agricultural lands. Agroforestry practices may also promote mineral N fertilization and the use of N2-fixing legumes that favor the emission of non-CO2 greenhouse gases (GHG) (N2O and CH4). The present study evaluates the net GHG balance in two adjacent coffee plantations, both highly fertilized (250 kg N ha-1 year-1): a monoculture (CM) and a culture shaded by the N2-fixing legume tree species Inga densiflora (CIn). C stocks, soil N2O emissions and CH4 uptakes were measured during the first cycle of both plantations. During a 3-year period (6-9 years after the establishment of the systems), soil C in the upper 10 cm remained constant in the CIn plantation (+0.09 &#177; 0.58 Mg C ha-1 year-1) and decreased slightly but not significantly in the CM plantation (-0.43 &#177; 0.53 Mg C ha-1 year-1). Aboveground carbon stocks in the coffee monoculture and the agroforestry system amounted to 9.8 &#177; 0.4 and 25.2 &#177; 0.6 Mg C ha-1, respectively, at 7 years after establishment. C storage rate in the phytomass was more than twice as large in the CIn compared to the CM system (4.6 &#177; 0.1 and 2.0 &#177; 0.1 Mg C ha-1 year-1, respectively). Annual soil N2O emissions were 1.3 times larger in the CIn than in the CM plantation (5.8 &#177; 0.5 and 4.3 &#177; 0.3 kg N-N2O ha-1 year-1, respectively). The net GHG balance at the soil scale calculated from the changes in soil C stocks and N2O emissions, expressed in CO2 equivalent, was negative in both coffee plantations indicating that the soil was a net source of GHG. Nevertheless this balance was in favor of the agroforestry system. The net GHG balance at the plantation scale, which includes additionally C storage in the phytomass, was positive and about 4 times larger in the CIn (14.59 &#177; 2.20 Mg CO2 eq ha-1 year-1) than in the CM plantation (3.83 &#177; 1.98 Mg CO2 eq ha-1 year-1). Thus converting the coffee monoculture to the coffee agroforestry plantation shaded by the N2-fixing tree species I. densiflora would increase net atmospheric GHG removals by 10.76 &#177; 2.96 Mg CO2 eq ha-1 year-1 during the first cycle of 8-9 years.</dc:description>
    <dc:subject>P33 - Chimie et physique du sol</dc:subject>
    <dc:subject>570</dc:subject>
    <dc:subject>571</dc:subject>
    <dc:subject>[SDV]Life Sciences [q-bio]</dc:subject>
    <dc:subject>F08 - Syst&#232;mes et modes de culture</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_1920</dc:subject>
    <dc:subject>stockage</dc:subject>
    <dc:subject>Funders: EU CASCA project</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_24345</dc:subject>
    <dc:subject>01 natural sciences</dc:subject>
    <dc:subject>630</dc:subject>
    <dc:subject>agroforestry</dc:subject>
    <dc:subject>leguminous tree</dc:subject>
    <dc:subject>soil organic matter</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_7427</dc:subject>
    <dc:subject>andosol</dc:subject>
    <dc:subject>gaz &#224; effet de serre</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_1721</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_34841</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_1666</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_1301</dc:subject>
    <dc:subject>Inga</dc:subject>
    <dc:subject>syst&#232;me de culture</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_35657</dc:subject>
    <dc:subject>0105 earth and related environmental sciences</dc:subject>
    <dc:subject>agroforesterie</dc:subject>
    <dc:subject>2. Zero hunger</dc:subject>
    <dc:subject>changement climatique</dc:subject>
    <dc:subject>Coffea arabica</dc:subject>
    <dc:subject>04 agricultural and veterinary sciences</dc:subject>
    <dc:subject>15. Life on land</dc:subject>
    <dc:subject>carbon sequestration</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_331583</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_207</dc:subject>
    <dc:subject>K10 - Production foresti&#232;re</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_404</dc:subject>
    <dc:subject>[SDV] Life Sciences [q-bio]</dc:subject>
    <dc:subject>s&#233;questration du carbone</dc:subject>
    <dc:subject>climate change</dc:subject>
    <dc:subject>13. Climate action</dc:subject>
    <dc:subject>global warming potential</dc:subject>
    <dc:subject>0401 agriculture, forestry, and fisheries</dc:subject>
    <dc:subject>P01 - Conservation de la nature et ressources fonci&#232;res</dc:subject>
    <dc:subject>carbone</dc:subject>
    <dc:subject>http://aims.fao.org/aos/agrovoc/c_1971</dc:subject>
    <dc:subject>central america</dc:subject>
    <dc:subject>Andosol</dc:subject>
    <dc:subject>mati&#232;re organique du sol</dc:subject>
    <dc:creator rdf:resource="https://orcid.org/0000-0002-8065-106x"/>
    <dc:creator rdf:resource="https://orcid.org/0000-0001-8659-6092"/>
    <dc:creator rdf:resource="https://orcid.org/0000-0002-1210-2499"/>
    <dc:creator>Jean-Michel Harmand, Kristell Hergoualc'h, Kristell Hergoualc'h, Eric Blanchart, Ute Skiba, Catherine H&#233;nault, </dc:creator>
    <dc:date>2012-02-01</dc:date>
    <dc:type>journalpaper</dc:type>
    <dct:abstract>Agroforestry represents an opportunity to reduce CO2 concentrations in the atmosphere by increasing carbon (C) stocks in agricultural lands. Agroforestry practices may also promote mineral N fertilization and the use of N2-fixing legumes that favor the emission of non-CO2 greenhouse gases (GHG) (N2O and CH4). The present study evaluates the net GHG balance in two adjacent coffee plantations, both highly fertilized (250 kg N ha-1 year-1): a monoculture (CM) and a culture shaded by the N2-fixing legume tree species Inga densiflora (CIn). C stocks, soil N2O emissions and CH4 uptakes were measured during the first cycle of both plantations. During a 3-year period (6-9 years after the establishment of the systems), soil C in the upper 10 cm remained constant in the CIn plantation (+0.09 &#177; 0.58 Mg C ha-1 year-1) and decreased slightly but not significantly in the CM plantation (-0.43 &#177; 0.53 Mg C ha-1 year-1). Aboveground carbon stocks in the coffee monoculture and the agroforestry system amounted to 9.8 &#177; 0.4 and 25.2 &#177; 0.6 Mg C ha-1, respectively, at 7 years after establishment. C storage rate in the phytomass was more than twice as large in the CIn compared to the CM system (4.6 &#177; 0.1 and 2.0 &#177; 0.1 Mg C ha-1 year-1, respectively). Annual soil N2O emissions were 1.3 times larger in the CIn than in the CM plantation (5.8 &#177; 0.5 and 4.3 &#177; 0.3 kg N-N2O ha-1 year-1, respectively). The net GHG balance at the soil scale calculated from the changes in soil C stocks and N2O emissions, expressed in CO2 equivalent, was negative in both coffee plantations indicating that the soil was a net source of GHG. Nevertheless this balance was in favor of the agroforestry system. The net GHG balance at the plantation scale, which includes additionally C storage in the phytomass, was positive and about 4 times larger in the CIn (14.59 &#177; 2.20 Mg CO2 eq ha-1 year-1) than in the CM plantation (3.83 &#177; 1.98 Mg CO2 eq ha-1 year-1). Thus converting the coffee monoculture to the coffee agroforestry plantation shaded by the N2-fixing tree species I. densiflora would increase net atmospheric GHG removals by 10.76 &#177; 2.96 Mg CO2 eq ha-1 year-1 during the first cycle of 8-9 years.</dct:abstract>
    <dc:title>Changes In Carbon Stock And Greenhouse Gas Balance In A Coffee (Coffea Arabica) Monoculture Versus An Agroforestry System With Inga Densiflora, In Costa Rica</dc:title>
    <dc:identifier>10.1016/j.agee.2011.11.018</dc:identifier>
    <dct:references>https://doi.org/10.1016/j.agee.2011.11.018</dct:references>
  </rdf:Description>
</rdf:RDF>