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      <ref-type name="Journal Article">17</ref-type>
      <work-type>ACL : Articles dans des revues avec comité de lecture répertoriées par l'AERES</work-type>
      <contributors>
        <authors>
          <author>
            <style face="bold" font="default" size="100%">Barthès, Bernard</style>
          </author>
          <author>
            <style face="bold" font="default" size="100%">Kouakoua, Ernest</style>
          </author>
          <author>
            <style face="bold" font="default" size="100%">Moulin Esmard, Patricia</style>
          </author>
          <author>
            <style face="normal" font="default" size="100%">Hmaidi, K.</style>
          </author>
          <author>
            <style face="normal" font="default" size="100%">Gallali, T.</style>
          </author>
          <author>
            <style face="normal" font="default" size="100%">Clairotte, M.</style>
          </author>
          <author>
            <style face="bold" font="default" size="100%">Bernoux, Martial</style>
          </author>
          <author>
            <style face="bold" font="default" size="100%">Bourdon, Emmanuel</style>
          </author>
          <author>
            <style face="bold" font="default" size="100%">Toucet, Joële</style>
          </author>
          <author>
            <style face="bold" font="default" size="100%">Chevallier, Tiphaine</style>
          </author>
        </authors>
        <secondary-authors>
          <author>
            <style face="normal" font="default" size="100%">Viscarra Rossela, R.A.</style>
          </author>
          <author>
            <style face="normal" font="default" size="100%">Stenberg, B.</style>
          </author>
        </secondary-authors>
      </contributors>
      <titles>
        <title>Studying the physical protection of soil carbon with quantitative infrared spectroscopy</title>
        <secondary-title>Near infrared spectroscopy of soils</secondary-title>
        <secondary-title>Journal of Near Infrared Spectroscopy</secondary-title>
      </titles>
      <pages>199-214</pages>
      <keywords>
        <keyword>SOL</keyword>
        <keyword>MATIERE ORGANIQUE</keyword>
        <keyword>CARBONE</keyword>
        <keyword>SPECTROSCOPIE</keyword>
        <keyword>REFLECTANCE</keyword>
        <keyword>RESPIRATION</keyword>
        <keyword>ANALYSE MULTIVARIABLE</keyword>
        <keyword>TUNISIE</keyword>
      </keywords>
      <dates>
        <year>2016</year>
      </dates>
      <call-num>fdi:010067291</call-num>
      <language>ENG</language>
      <periodical>
        <full-title>Journal of Near Infrared Spectroscopy</full-title>
      </periodical>
      <isbn>0967-0335</isbn>
      <accession-num>ISI:000381677800002</accession-num>
      <number>3</number>
      <electronic-resource-num>10.1255/jnirs.1232</electronic-resource-num>
      <urls>
        <related-urls>
          <url>https://www.documentation.ird.fr/hor/fdi:010067291</url>
        </related-urls>
        <pdf-urls>
          <url>https://www.documentation.ird.fr/intranet/publi/depot/2016-07-27/010067291.pdf</url>
        </pdf-urls>
      </urls>
      <volume>24</volume>
      <remote-database-provider>Horizon (IRD)</remote-database-provider>
      <abstract>Near infrared (NIR) and mid-infrared (mid-IR) reflectance spectroscopy are time- and cost-effective tools for characterising soil organic carbon (SOC). Here they were used for quantifying (i) carbon (C) dioxide (CO2) emission from soil samples crushed to 2 mm and 0.2 mm, at 18°C and 28°C; (ii) physical C protection, calculated as the difference between CO2 emissions from 0.2 mm and 2 mm crushed soil at a given temperature; and (iii) the temperature vulnerability of this protection, calculated as the difference between C protection at 18°C and 28°C. This was done for 97 topsoil samples from Tunisia, mostly calcareous, which were incubated for 21 days. Soil CO2 emission increased with temperature and fine crushing. However, C protection in 0.2–2 mm aggregates had little effect on the temperature vulnerability of CO2 emission, possibly due to preferential SOC protection in smaller aggregates. In general, NIR spectroscopy, and to a lesser extent mid-IR spectroscopy, yielded accurate predictions of soil CO2 emission (0.60 ≤ R2 ≤ 0.91), and acceptable predictions of C protection at the beginning of incubation (0.52 ≤ R2 ≤ 0.81) but not over the whole 21 day period (R2 ≤ 0.59). For CO2 emission, prediction error was the same order of magnitude as, and sometimes similar to, the uncertainty of conventional determination, indicating that a noticeable proportion of the former could be attributed to the latter. The temperature vulnerability of C protection could not be modelled correctly (R2 ≤ 0.11), due to error propagation. The prediction of SOC was better with NIR spectroscopy and that of soil inorganic C (SIC) was very accurate (R2 ≥ 0.94), especially with mid-IR spectroscopy. Soil CO2 emission, C protection and its vulnerability were best predicted with NIR spectra, those of 0.2 mm samples especially. With 2 mm samples, mid-IR spectroscopy yielded the worst predictions in general. NIR spectroscopy prediction models suggested that CO2 emission and C protection depended (i) on aliphatic compounds (i.e. labile substrates), dominantly at 18°C; (ii) on amides or proteins (i.e. microbial biomass), markedly at 28°C; and (iii) negatively, on organohalogens and aromatic amines (i.e. pesticides). Models using mid-IR spectra showed a negative influence of carbonates on CO2 emission, suggesting they did not contribute to soil CO2 emission and might form during incubation. They also suggested that CO2 emission and C protection related to carboxylic acids, saturated aliphatic ones especially.</abstract>
      <custom6>068ANASOL</custom6>
      <custom1>UR210</custom1>
      <custom7>Tunisie</custom7>
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