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  <titleInfo>
    <title>Composting of water hyacinth by aerobic process</title>
  </titleInfo>
  <name type="personal">
    <namePart>Rachanee Lindratsirikul</namePart>
    <role>
      <roleTerm authority="marcrelator" type="text">creator</roleTerm>
    </role>
  </name>
  <name type="personal">
    <namePart>Samorn Muttamara</namePart>
    <role>
      <roleTerm type="text">Chairperson</roleTerm>
    </role>
  </name>
  <name type="personal">
    <namePart>Chongrak Polprasert</namePart>
    <role>
      <roleTerm type="text">Examination Committee</roleTerm>
    </role>
  </name>
  <name type="personal">
    <namePart>Ahn, Kyu-Hong</namePart>
    <role>
      <roleTerm type="text">Examination Committee</roleTerm>
    </role>
  </name>
  <name type="corporate">
    <namePart>Japanese Government</namePart>
    <role>
      <roleTerm type="text">Scholarship Donor</roleTerm>
    </role>
  </name>
  <typeOfResource>text</typeOfResource>
  <originInfo>
    <place>
      <placeTerm type="code" authority="marccountry">th</placeTerm>
    </place>
    <place>
      <placeTerm type="text">Bangkok</placeTerm>
    </place>
    <publisher>Asian Institute of Technology</publisher>
    <dateIssued>1988</dateIssued>
    <issuance>monographic</issuance>
  </originInfo>
  <language>
    <languageTerm authority="iso639-2b" type="code">eng</languageTerm>
  </language>
  <physicalDescription>
    <extent>58 p.</extent>
  </physicalDescription>
  <abstract>Pilot scale composting of water hyacinth with forced aeration was  undertaken with two sets of experiments: three piles for each set. Each  compost pile was made from chopped water hyacinth and cesspool slurry.  They were experimented upon by the difference of aeration rates and  inoculum seeding sizes. The aeration rates were varied at 0.30, 0.54 and  1.54 m 3/day/kg of volatile solids (VS). The inoculum seeding size of  0.015% was used with and without aeration and 0.03% with aeration. The  chemical and physical parameters were observed throughout the composting  period. Fecal coliform was used as the hygiene indicator.  In piles with variation of forced aeration rates, the minimum rate  3 of 0.3m /day/kg of VS gave the greatest reduction in the organic carbon  and the C/N ratio. The peak temperature of 59.8°C was observed in the  same pile. In the other piles with the variation of size of inoculum  seeding, better results in reduction of organic carbon and C/N ratio were  observed in the non-aerated pile. A maximum temperature of 56. 1°C was  obtained in the same pile. Temperatures beyond 50°C were attained at the  pile center for 4 days in aerated piles with seeding and 8 days in the  non-aerated pile .  In both the experiments, more than 85% of the fecal coliform were  destroyed. For a C/N ratio of 28, the optimum aeration for highest  decomposition rate required is 0.3m3/d/kg of VS . An inoculum seeding of  0. 015% in a pile of C/N ratio 23: 1 without aeration was found to give  better results than those with aeration.</abstract>
  <note>A Thesis submitted in partial fulfillment of the requirements for the degree of Master of Science, School of Environment, Resources and Development</note>
  <note>Thesis (M.Sc.) - Asian Institute of Technology, 1988</note>
  <subject authority="lcsh">
    <topic>Water-hyacinth</topic>
  </subject>
  <relatedItem type="series">
    <titleInfo>
      <title>Thesis ; no. EV-88-19</title>
    </titleInfo>
    <name type="corporate">
      <namePart>Asian Institute of Technology.</namePart>
      <namePart/>
    </name>
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  <identifier type="uri">http://203.159.5.9/ait-thesis/detail.php?q=B18889</identifier>
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    <url displayLabel="Full-Text">http://203.159.5.9/ait-thesis/detail.php?q=B18889</url>
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    <recordCreationDate encoding="marc">120399</recordCreationDate>
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