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Title: Arsenic release during pyrolysis of CCA treated wood waste: current state of knowledge
Authors: Helsen, J
Van den Bulck, E
VAN BAEL, Marlies
Issue Date: 2003
Abstract: Low-temperature pyrolysis is evaluated as a possible technique for the disposal of chromated copper arsenate (CCA) treated wood waste. Theoretical and experimental studies are performed in order to gain more insight in the mechanism of arsenic release. In this paper, the most important observations and results of modelling are brought together in order to present the current state of knowledge. Lab-scale pyrolysis experiments show that pyrolysis at 300 degreesC for 20 min gives rise to inconclusive release for the three metals. However, arsenic releases are substantial for all experiments using a temperature of 320 degreesC. A speciation study shows the presence of trivalent arsenic in the pyrolysis residue, indicating that arsenic, present in pentavalent state in the CCA solution and in the CCA treated wood, is partly reduced to the trivalent state during pyrolysis. Arsenic release can be modelled by a simple first order single-reaction kinetic scheme for the temperature range from 350 to 450 degreesC. Based on the order of magnitude of the kinetic constants, the reaction is identified as a reduction reaction. Thermogravimetric (TG) analysis of hydrated chromium arsenate (the major arsenic compound in CCA treated wood) reveals that thermal decomposition probably results in the formation of solid Cr2O3 and gaseous H2O, O-2 and As4O6, indicating again that As(V) is reduced to As(III) and arsenic is released in trivalent form. TG studies of the pure arsenic oxides (As2O5 and As2O3) show that at temperatures lower than 500 degreesC the reduction reaction As2O5 --> As2O3 + O-2 does not take place. At higher temperatures decomposition is observed. As2O3, however, is already released at temperatures as low as 200 degreesC. This release is driven by temperature dependent vapour pressures. It can be concluded that the wood, char and pyrolysis vapours form a reducing environment, thereby influencing the thermal behaviour of the arsenic oxides. An other explanation for the difference in thermal behaviour could be that part of the arsenic in the CCA treated wood is already present in the trivalent form. (C) 2003 Elsevier Science B.V. All rights reserved.
Notes: Katholieke Univ Leuven, Dept Mech Engn, B-3001 Heverlee, Belgium. Limburgs Univ Ctr, Lab Inorgan & Phys Chem, B-3590 Diepenbeek, Belgium.Helsen, J, Katholieke Univ Leuven, Dept Mech Engn, Celestijnenlaan 300A, B-3001 Heverlee, Belgium.
URI: http://hdl.handle.net/1942/2495
DOI: 10.1016/S0165-2370(03)00055-X
ISI #: 000184573200040
ISSN: 0165-2370
Category: A1
Type: Journal Contribution
Validation: ecoom, 2004
Appears in Collections: Research publications

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