The ability of the iron minerals hematite and magnetite to catalyze the dec
omposition of hydrogen peroxide (H2O2) and initiate the Fenton-like oxidati
on of pentachlorophenol (PCP) was investigated in batch, bench-scale system
s in which PCP was spiked onto silica sand. Pentachlorophenol degradation w
as documented in silica sand-mineral-H2O2 systems by the release of chlorid
e and the loss of total organic carbon. The most efficient oxidation stoich
iometry was the magnetite-catalyzed reaction over the first 8 h with 490 me
l H2O2 consumed/mol PCP degraded. After 8 h, the peroxide efficiency decrea
sed significantly; amorphous iron hydroxide formation on the magnetite surf
ace may have catalyzed the decomposition of H2O2 to oxygen species other th
an hydroxyl radicals, Mineral-catalyzed Fenton-like treatment in two natura
l soils was demonstrated after spiking the soils with PCP; the contaminant
was degraded with no iron addition, The oxidation stoichiometry in the two
soils was 1,100 and 2,930 mol H2O2 consumed/mol PCP degraded.