Phenolic compounds undergo several transformation processes in soil and wat
er (i.e., partial degradation, mineralization, and polymerization), many of
which have been attributed primarily to biological activity. Results from
previous work indicate that naturally occurring Mn oxides are also capable
of oxidizing phenolic compounds. In the present study, C-14-labeled catecho
l was reacted with birnessite (manganese oxide) in aqueous suspension at pH
4. The mass of catechol-derived C in solid, solution, and gas phases was q
uantified as a function of time. Between 5 and 16% of the total catechol C
was liberated as CO2 from oxidation and abiotic ring cleavage under various
conditions. Most of the C-14 (55-83%) was incorporated into the solid phas
e in the form of stable organic reaction products whereas solution phase C-
14 concentrations increased from 16 to 39% with a doubling of total catecho
l added. Polymerization and CO2 evolution appear to be competitive pathways
in the transformation of catechol since their relative importance was stro
ngly dependent on initial birnessite-catechol reaction conditions. Solid ph
ase Fourier transform infrared (FTIR) spectra are consistent with the prese
nce of phenolic, quinone, and aromatic ring cleavage products. Carbon dioxi
de release appears to be limited by availability of reactive birnessite sur
face sites and it is diminished in the presence of polymerized reaction pro
ducts.