PHOTOCHEMICAL REDUCTION OF ORGANICALLY-BOUND FeIII IN A HIGH-ALTITUDE STREAM THAT RESULTS IN UNEXPECTED INCREASES IN [FeIII(AQ)]

Many studies have shown that the concentration of aqueous Fe²⁺ increases in surface waters during exposure to sunlight and attribute this phenomenon either to photoreductive dissolution of ferric minerals/colloids or to ligand-to-metal charge transfer within organic complexes of Fe³⁺. In a multi-summer study of iron redox cycling in a relatively high pH stream (Middle Crow Creek, MCC) that drains a mostly-granitic watershed at an altitude of 2400 m, aqueous Fe³⁺ (not Fe²⁺) concentrations were correlated with both sunlight and temperature. A steady state model fails to explain the [Fe²⁺] and [Fe³⁺] data from this stream. However, Fe²⁺ concentrations can be explained using a simple kinetic model in which rate constants for oxidation and reduction were obtained by fitting data from in situ oxidation experiments, including first-order thermal (non photochemical) reduction of Fe³⁺. Rate constants obtained from experiments in the dark result in too much Fe²⁺ to match the data from illuminated experiments, requiring a net photooxidation process to explain [Fe³⁺] measured in MCC. The organic content of MCC results in high concentrations of Fe-DOM complexes that not only act as a reservoir contributing to daily changes in [Fe_tot] as measured by our methods, but whose photochemistry may contribute highly oxidizing reactive oxygen species to the stream. In situ studies suggest that photochemical reduction of organically bound Fe³⁺ occurs, followed by thermal release of Fe²⁺ to the water column and subsequent rapid re-oxidation.