<oai_dc:dc xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
  <dc:creator>Yu Q</dc:creator>
  <dc:creator>Duan L</dc:creator>
  <dc:creator>Yu L</dc:creator>
  <dc:creator>Chen X</dc:creator>
  <dc:creator>Si G</dc:creator>
  <dc:creator>Ke P</dc:creator>
  <dc:creator>Ye Z</dc:creator>
  <dc:creator>Mulder J</dc:creator>
  <dc:date>2018</dc:date>
  <dc:description xmlns:ns0="xml" ns0:lang="en">The influence of nitrogen (N) deposition on forest ecosystems largely depend on the N status. Developing threshold and practical indicators for N saturation in subtropical forests, with extremely high N deposition, would both enhance forest management and the assessments of global N balance and carbon (C) sequestration. Here, we quantified the N mass balance and assessed current N status at a number of subtropical forest sites in South China, using both N content, C/N ratio, and 15N natural abundance (δ15N) as potential indicators of N saturation. Among the studied sites, N deposition ranged from 13.8 to 113 kg N ha-1 yr-1 in throughfall, and was dominated by ammonium (NH4+). The threshold for N leaching in subtropical forest was first found to be 26-36 kg N ha-1 yr-1, which was 160% higher than in temperate forest (based on prescribed minimum). This indicates that critical parameter inputs in global models of the impact of N deposition are in need of revision, based on specific ecosystem characteristics. We found a critical C/N ratio of 20 for the O/A horizon as indicator of N saturation. Foliar N content and δ15N were positively correlated with N deposition and were well suited to indicate regional N status. The δ15N enrichment factor (Ɛfoli/So2, δ15Nfoliage - δ15NSoil2) was between -10‰ and -1‰, and had similar trend to those obtained from other regions with increasing N deposition. These suggest that the enrichment factor could be used to investigate the influence of N deposition in forest ecosystems, regardless of spatial heterogeneity in δ15N of N input, soil N availability and geomorphology.</dc:description>
  <dc:identifier>https://sonar.ch/global/documents/75509</dc:identifier>
  <dc:language>eng</dc:language>
  <dc:relation>info:eu-repo/semantics/altIdentifier/doi/10.1016/j.envpol.2018.06.001</dc:relation>
  <dc:relation>info:eu-repo/semantics/altIdentifier/pmid/29902749</dc:relation>
  <dc:source>Environmental pollution (Barking, Essex : 1987). - 2018</dc:source>
  <dc:subject xmlns:ns1="xml" ns1:lang="en">Enrichment factor</dc:subject>
  <dc:subject xmlns:ns2="xml" ns2:lang="en">N deposition</dc:subject>
  <dc:subject xmlns:ns3="xml" ns3:lang="en">N isotope</dc:subject>
  <dc:subject xmlns:ns4="xml" ns4:lang="en">N saturation</dc:subject>
  <dc:subject xmlns:ns5="xml" ns5:lang="en">Subtropical forests</dc:subject>
  <dc:subject xmlns:ns6="xml" ns6:lang="en">Ammonium Compounds</dc:subject>
  <dc:subject xmlns:ns7="xml" ns7:lang="en">China</dc:subject>
  <dc:subject xmlns:ns8="xml" ns8:lang="en">Ecosystem</dc:subject>
  <dc:subject xmlns:ns9="xml" ns9:lang="en">Environmental Monitoring</dc:subject>
  <dc:subject xmlns:ns10="xml" ns10:lang="en">Forests</dc:subject>
  <dc:subject xmlns:ns11="xml" ns11:lang="en">Nitrogen</dc:subject>
  <dc:subject xmlns:ns12="xml" ns12:lang="en">Nitrogen Cycle</dc:subject>
  <dc:subject xmlns:ns13="xml" ns13:lang="en">Soil</dc:subject>
  <dc:subject xmlns:ns14="xml" ns14:lang="en">Trees</dc:subject>
  <dc:title xmlns:ns15="xml" ns15:lang="en">Threshold and multiple indicators for nitrogen saturation in subtropical forests.</dc:title>
  <dc:type>http://purl.org/coar/resource_type/c_6501</dc:type>
</oai_dc:dc>
