Product distribution from straw and washed straw pyrolysis shows the usual
temperature (660-990 K) dependence, but the pretreatment makes the initial
degradation temperature slightly higher and gives rise to larger yields of
condensable products (mainly at the expenses of char). Water washing also a
ffects decomposition of straw in air. Devolatilization again takes place at
higher temperatures and with a higher peak rate, but char combustion react
ivities are always lower. Hot water washing of large (0.5-1 mm) straw char
particles is less effective for ash removal than straw washing, independent
ly of the temperature and the atmosphere where chars were formed. In partic
ular, for low temperature (520 K) and air, the ash removed decreases as suc
cessively higher conversion levels are examined. (C) 2000 Elsevier Science
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