<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.geoderma.2004.02.014">
    <dct:isReferencedBy>IMPACT4SOIL</dct:isReferencedBy>
    <dct:isReferencedBy>OpenAire</dct:isReferencedBy>
    <dct:isReferencedBy>Research@WUR</dct:isReferencedBy>
    <dct:isReferencedBy>Crossref</dct:isReferencedBy>
    <dct:isReferencedBy>Microsoft Academic Graph</dct:isReferencedBy>
    <dct:isPartOf>Geoderma</dct:isPartOf>
    <dct:license>Restricted</dct:license>
    <dct:created>2004-04-10</dct:created>
    <dc:description>Abstract   The purpose of this study was to evaluate possible changes in soil organic matter (SOM) dynamics after establishing riparian forests on soils previously under Brazilian savannah (&#8220;cerrado&#8221;). We selected a site with a homogeneous Typic Acric Red&#8211;Yellow Latosol (Anionic Acrustox). Part of this site was maintained under native vegetation (grassy cerrado C 4 -dominated), and part was planted with riparian species (C 3 ) in 1992. Litter and soil samples were collected and analysed (total organic carbon, total nitrogen,  &#948;  13 C isotopic analysis, and SOM density fractionation). Due to the predominance of grasses, carbon input was mainly below ground in cerrado. In such a soil, the decomposition process was more efficient, and much C and N were transferred to the heavy fraction. When forest was planted, there was a change from belowground to aboveground litter input (largely superficial), leading to higher C and N stocks in the light and lower stocks in the heavy fraction (resulting in lower stocks for bulk soil). The introduction of the C 3  vegetation decreased the soil  &#948;  13 C signature. It has occurred particularly in the topsoil (0&#8211;5 cm) due to the deposition of C 3  litter on the soil surface. At the same time, the presence of cerrado-remaining C below 5 cm maintained higher  &#948;  13 C values in this layer. During the 8 years after forest plantation, the input mode influenced both the  &#948;  13 C distribution with depth, and the C replacement: between 0 and 2.5 cm, nearly 50% of cerrado-derived C was replaced by forest-derived C, while below 5 cm, replacement was around 20%. The relatively rapid C dynamics in this Oxisol (27% replacement in the top 20 cm after 8 years of forest plantation) shows that, under tropical conditions, significant changes may occur in a short period of time.</dc:description>
    <dc:subject>delta-c-13</dc:subject>
    <dc:subject>decomposition</dc:subject>
    <dc:subject>c-13 natural-abundance</dc:subject>
    <dc:subject>particle-size fractions</dc:subject>
    <dc:subject>turnover</dc:subject>
    <dc:subject>0401 agriculture, forestry, and fisheries</dc:subject>
    <dc:subject>vegetation changes</dc:subject>
    <dc:subject>04 agricultural and veterinary sciences</dc:subject>
    <dc:subject>15. Life on land</dc:subject>
    <dc:subject>stable carbon isotope</dc:subject>
    <dc:subject>density fractions</dc:subject>
    <dc:subject>ratios</dc:subject>
    <dc:subject>nitrogen</dc:subject>
    <dc:creator>de Alcantara, F.A., Buurman, P., Furtini Neto, A.E., Curi, N., Roscoe, R., </dc:creator>
    <dc:date>2004-12-01</dc:date>
    <dc:type>journalpaper</dc:type>
    <dct:abstract>Abstract   The purpose of this study was to evaluate possible changes in soil organic matter (SOM) dynamics after establishing riparian forests on soils previously under Brazilian savannah (&#8220;cerrado&#8221;). We selected a site with a homogeneous Typic Acric Red&#8211;Yellow Latosol (Anionic Acrustox). Part of this site was maintained under native vegetation (grassy cerrado C 4 -dominated), and part was planted with riparian species (C 3 ) in 1992. Litter and soil samples were collected and analysed (total organic carbon, total nitrogen,  &#948;  13 C isotopic analysis, and SOM density fractionation). Due to the predominance of grasses, carbon input was mainly below ground in cerrado. In such a soil, the decomposition process was more efficient, and much C and N were transferred to the heavy fraction. When forest was planted, there was a change from belowground to aboveground litter input (largely superficial), leading to higher C and N stocks in the light and lower stocks in the heavy fraction (resulting in lower stocks for bulk soil). The introduction of the C 3  vegetation decreased the soil  &#948;  13 C signature. It has occurred particularly in the topsoil (0&#8211;5 cm) due to the deposition of C 3  litter on the soil surface. At the same time, the presence of cerrado-remaining C below 5 cm maintained higher  &#948;  13 C values in this layer. During the 8 years after forest plantation, the input mode influenced both the  &#948;  13 C distribution with depth, and the C replacement: between 0 and 2.5 cm, nearly 50% of cerrado-derived C was replaced by forest-derived C, while below 5 cm, replacement was around 20%. The relatively rapid C dynamics in this Oxisol (27% replacement in the top 20 cm after 8 years of forest plantation) shows that, under tropical conditions, significant changes may occur in a short period of time.</dct:abstract>
    <dc:title>Conversion Of Grassy Cerrado Into Riparian Forest And Its Impact On Soil Organic Matter Dynamics In An Oxisol From Southeast Brazil</dc:title>
    <dc:identifier>10.1016/j.geoderma.2004.02.014</dc:identifier>
    <dct:references>https://doi.org/10.1016/j.geoderma.2004.02.014</dct:references>
  </rdf:Description>
</rdf:RDF>