Degradation of Biomacromolecules during High-Rate Composting of Wheat StrawAmended Feces
A. H. M. Veeken*,a,
F. Adanid,
K. G. J. Nieropb,
P. A. de Jagerc and
H. V. M. Hamelersa
a Dep. of Environmental Technology, Wageningen Agricultural Univ., P.O. Box 8129, 6700 EV Wageningen, the Netherlands
b Lab. of Soil Science and Geology, Wageningen Agricultural Univ., P.O. Box 8129, 6700 EV Wageningen, the Netherlands
c Lab. of Molecular Physics, Wageningen Agricultural Univ., P.O. Box 8129, 6700 EV Wageningen, the Netherlands
d Dipartimento di Fisiologia delle Piante Coltivate e Chimica Agraria, Univ. of Milan, Via Celoria 2, 20133 Milano, Italy

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Fig. 1. Characteristics of the composting process. (A) Oxygen uptake rate (OUR) and cumulative oxygen consumption (COU). (B) Ratio of oxygen uptake rate on carbon dioxide production rate (CPR). (C) Flow rates of incoming and recirculation air. (D) Average temperature of the compost bed.
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Fig. 2. Cross polarization magic angle spinning (CPMAS) 13C nuclear magnetic resonance (NMR) spectra of straw, pig feces, and compost bed after 1 and 4 wk of composting.
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Fig. 3. Absolute changes in relative areas of the four nuclear magnetic resonance (NMR) regions during high-rate composting of wheat strawamended pig feces.
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Fig. 4. Recovery of the four biomacromolecules during sequential forage fiber analysis of the sample after 1 wk of composting (NDF, neutral detergent fiber; NDADF, neutral detergent acid detergent fiber; ADL, acid detergent lignin).
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Fig. 6. Development of total organic matter and specific organic compounds during high-rate composting of wheat strawamended pig feces.
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Copyright © 2001 by the American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America.