This paper is an assessment of the potential for recycling spent, pres
ervative-treated wood products. Approximately 6 x 10(6) m(3) of wood t
reated with chromated copper arsenate (CCA), pentachlorophenol, and cr
eosote are disposed of annually and about 19 x 10(6) m(3)/year will be
available for recycling by 2020. Currently, about 1.3 x 10(6) m(3)/ye
ar of creosote-treated railroad ties and 2 x 10(6) m(3) of utility pol
es treated with pentachlorophenol and creosote are available for recyc
ling. The balance is primarily from CCA-treated dimension lumber and t
he amount is forecasted to increase significantly due to its use in ho
using and decking. The recent expansion of the wood recycling industry
has not included preservative-treated wood because of technical probl
ems and regulatory uncertainties. The most viable recycling option for
wood treated with arsenic is probably composite manufacturing, but pr
oblems such as characterization of comminution emissions and adhesive
compatibility remain. Composting is also a potentially viable option,
particularly for pentachlorophenol- and creosote-treated wood, althoug
h comminution emissions need to be characterized and questions need to
be answered about the effects of microbial growth inhibition from the
potentially large preservative concentrations.