Based on laboratory experiments combined with kinetic modeling, we pro
pose a conceptual model for the photodegradation of initially uncomple
xed EDTA in the presence of gamma-FeOOH (lepidocrocite), as follows: F
ree EDTA becomes adsorbed at the surface of gamma-FeOOH and is initial
ly photooxidized as a surface species. Thereby, gamma-FeOOH is reducti
vely dissolved. Our results suggest that photooxidation of adsorbed ED
TA, coupled to reductive dissolution of gamma-FeOOH, occurs through ph
otolysis of the Fe(111)EDTA surface complex. The photochemically forme
d Fe(ll) then catalyzes the thermal dissolution of the solid phase in
the presence of EDTA. This process results in production of dissolved
Fe(111)EDTA, which is subsequently photolyzed. Hence, in these heterog
eneous systems, initially uncomplexed EDTA is photooxidized via two pa
thways: (i) photooxidation at the surface of gamma-FeOOH and (ii) phot
olysis of dissolved Fe(111)EDTA that is formed in the Fe(ll)-catalyzed
dissolution of gamma-FeOOH. Which pathway predominates depends on the
relative rates of Fe(ll) oxidation and of Fe(ll)-catalyzed formation
of dissolved Fe(111)EDTA. At pH 3, photooxidation of EDTA occurred pre
dominantly through photolysis of dissolved Fe(111)EDTA, whereas at pH
7, photooxidation of adsorbed EDTA was more important in our aerated h
eterogeneous systems, because of the faster Fe(II) oxidation at pH 7,
compared to pH 3. Our results indicate that not only dissolved Fe(111)
EDTA but also Fe(111)EDTA surface complexes are efficiently photolyzed
.