<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.chemosphere.2010.08.026">
    <dct:isReferencedBy>IMPACT4SOIL</dct:isReferencedBy>
    <dct:isReferencedBy>OpenAire</dct:isReferencedBy>
    <dct:isReferencedBy>HAL INRAE</dct:isReferencedBy>
    <dct:isReferencedBy>Crossref</dct:isReferencedBy>
    <dct:isReferencedBy>Microsoft Academic Graph</dct:isReferencedBy>
    <dct:isReferencedBy>Europe PubMed Central</dct:isReferencedBy>
    <dct:isPartOf>Chemosphere</dct:isPartOf>
    <dct:license>Closed Access</dct:license>
    <dct:created>2010-09-13</dct:created>
    <dct:available>2020-05-15</dct:available>
    <dc:description>Nitrification is often negatively affected by heavy metal pollution in soils, this limiting land revegetation. Thus, the potential use of pig slurry as a nitrogen-rich organic amendment in different heavy metal contaminated soils has been evaluated; this also being a way of recycling this waste. In order to identify the factors affecting nitrification processes in heavy metal polluted soils (soil pH, heavy metal solubility and the N source), incubation experiments were run using two polluted soils with different pH values (5.0 and 7.1) and a non-contaminated soil (pH 8.2). Ammonium was added as pig slurry or as ammonium sulphate for comparison (both added at 150 mg NH(4)(+)-N kg(-1) of soil). Pig slurry provoked higher nitrification rates and N-immobilisation than ammonium sulphate, especially in the neutral-polluted soil, reflecting an improvement of the microbial activity in the soil. The microbial immobilisation of N led to an inverse relationship between the amount of N added and nitrate conversion in the neutral-polluted soil and in the non-contaminated soil amended with different pig slurry dosages (75, 150 and 225mg NH(4)(+)-N kg(-1) of soil). Low rates of nitrification and N-immobilisation were found in the acidic soil. Pig slurry addition to metal polluted soils enhanced soil nitrification, especially when metals were in low-solubility forms.</dc:description>
    <dc:subject>[SDE] Environmental Sciences</dc:subject>
    <dc:subject>2. Zero hunger</dc:subject>
    <dc:subject>PIG SLURRY RECYCLING</dc:subject>
    <dc:subject>SOIL RECLAMATION</dc:subject>
    <dc:subject>Nitrogen</dc:subject>
    <dc:subject>Swine</dc:subject>
    <dc:subject>METAL SOLUBILITY</dc:subject>
    <dc:subject>04 agricultural and veterinary sciences</dc:subject>
    <dc:subject>Hydrogen-Ion Concentration</dc:subject>
    <dc:subject>15. Life on land</dc:subject>
    <dc:subject>NITRIFICATION</dc:subject>
    <dc:subject>6. Clean water</dc:subject>
    <dc:subject>12. Responsible consumption</dc:subject>
    <dc:subject>Manure</dc:subject>
    <dc:subject>Quaternary Ammonium Compounds</dc:subject>
    <dc:subject>MICROBIAL IMMOBILISATION</dc:subject>
    <dc:subject>Biodegradation, Environmental</dc:subject>
    <dc:subject>13. Climate action</dc:subject>
    <dc:subject>METAL</dc:subject>
    <dc:subject>Metals, Heavy</dc:subject>
    <dc:subject>Animals</dc:subject>
    <dc:subject>Soil Pollutants</dc:subject>
    <dc:subject>0401 agriculture, forestry, and fisheries</dc:subject>
    <dc:subject>Soil Microbiology</dc:subject>
    <dc:creator rdf:resource="https://orcid.org/0000-0002-2429-837x"/>
    <dc:creator rdf:resource="https://orcid.org/0000-0003-0085-1764"/>
    <dc:creator rdf:resource="https://orcid.org/0000-0003-2024-4531"/>
    <dc:creator rdf:resource="https://orcid.org/0000-0002-9597-4937"/>
    <dc:creator>de La Fuente, C., Clemente, R., Martinez, Jos&#233;, Pilar Bernal, M., </dc:creator>
    <dc:date>2010-10-01</dc:date>
    <dc:type>journalpaper</dc:type>
    <dct:abstract>Nitrification is often negatively affected by heavy metal pollution in soils, this limiting land revegetation. Thus, the potential use of pig slurry as a nitrogen-rich organic amendment in different heavy metal contaminated soils has been evaluated; this also being a way of recycling this waste. In order to identify the factors affecting nitrification processes in heavy metal polluted soils (soil pH, heavy metal solubility and the N source), incubation experiments were run using two polluted soils with different pH values (5.0 and 7.1) and a non-contaminated soil (pH 8.2). Ammonium was added as pig slurry or as ammonium sulphate for comparison (both added at 150 mg NH(4)(+)-N kg(-1) of soil). Pig slurry provoked higher nitrification rates and N-immobilisation than ammonium sulphate, especially in the neutral-polluted soil, reflecting an improvement of the microbial activity in the soil. The microbial immobilisation of N led to an inverse relationship between the amount of N added and nitrate conversion in the neutral-polluted soil and in the non-contaminated soil amended with different pig slurry dosages (75, 150 and 225mg NH(4)(+)-N kg(-1) of soil). Low rates of nitrification and N-immobilisation were found in the acidic soil. Pig slurry addition to metal polluted soils enhanced soil nitrification, especially when metals were in low-solubility forms.</dct:abstract>
    <dc:title>Optimization Of Pig Slurry Application To Heavy Metal Polluted Soils Monitoring Nitrification Processes</dc:title>
    <dc:identifier>10.1016/j.chemosphere.2010.08.026</dc:identifier>
    <dct:references>https://doi.org/10.1016/j.chemosphere.2010.08.026</dct:references>
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