posted on 2002-12-21, 00:00authored byAndrew J. Feitz, T. David Waite
A kinetic model has been developed to investigate the
relative importance of major pathways for the photocatalytic
degradation of trace levels of the cyanobacterial toxin
microcystin-LR (MLR) in solutions containing a complex suite
of dissolved organic matter and to test the sensitivity of
MLR degradation to rate constants of the key processes. The
kinetic model incorporates adsorption of the trace
contaminant, other organics and oxygen on the particle
surface, surface reactions between adsorbed radical and
nonradical species, desorption of surface radical species,
solution phase radical reactions, and radical termination
pathways. Under conditions where the contaminant adsorbs
strongly to semiconductor surface sites, rapid degradation
is observed, and a primary degradation step appears to
involve reaction between surface-located long-lived organic
radicals (formed from hydroxyl radical scavenging by the
bulk organic) and adsorbed trace contaminant. MLR
degradation is relatively insensitive to changes in light
intensity under these strongly adsorbing conditions but
highly dependent under weakly adsorbing conditions and
when solution phase degradation is important. While not
verified independently, desorption of surface bound
superoxide appears to lead to the production of organic
peroxyl radicals through reaction of superoxide with the bulk
organic. These solution phase organic peroxyl radicals
are highly reactive and appear to be the primary source
of trace contaminant degradation under conditions where
the trace contaminant shows no observable adsorption
and surface degradation is negligible. Under alkaline
conditions, adsorption of carbonate onto the particle surface
results in scavenging of surface hydroxyl radicals to
form surface carbonate radicals that rapidly quench surface
bound superoxide. This prevents organic peroxyl production,
the primary agent of solution-phase trace contaminant
degradation.