LABORATORY-SCALE AND PILOT-PLANT-SCALE PHOTODEGRADATION OF CHLOROALIPHATICS IN AQUEOUS-SOLUTION BY PHOTOCATALYTIC MEMBRANES IMMOBILIZING TITANIUM-DIOXIDE
Ir. Bellobono et al., LABORATORY-SCALE AND PILOT-PLANT-SCALE PHOTODEGRADATION OF CHLOROALIPHATICS IN AQUEOUS-SOLUTION BY PHOTOCATALYTIC MEMBRANES IMMOBILIZING TITANIUM-DIOXIDE, Journal of photochemistry and photobiology. A, Chemistry, 84(1), 1994, pp. 83-90
The TiO2-mediated photodegradation of chloroaliphatics (dichloromethan
e, trichloroethene and mono-, di- and trichloroethanoic acids) was stu
died at 308 +/- 2 K (with the ratio between the hydrogen peroxide adde
d and the stoichiometric amount (N) in the range 0-30), using PHOTOPER
M(TM) CPP/313 membranes containing immobilized 30% +/- 3% TiO2, at lab
oratory scale (radiant power in the absorption range, 145 W) and in a
pilot plant (radiant power in the absorption range, 31 W). In addition
to this semiconductor, some proprietary photocatalytic systems, inclu
ding stabilized preparations containing Co(III), V(v) and Fe(III) orga
nometallic compounds, were immobilized in the photocatalytic membranes
. The initial rate of photodegradation was studied as a function of th
e initial concentration of the substrates (5.0 x 10(-2)-5.0 x 10(-7) M
) using the linearized form of the Langmuir-Hinshelwood equation, whic
h was well fitted by the membranes over the whole range of concentrati
on, and from which the rate constants k and equilibrium adsorption con
stants K were evaluated. The contributions of processes (a)-(d) ((a) p
hotolysis of micropollutant, independent of the presence of membranes
and oxidizing agent; (b) photodegradation due to UV and hydrogen perox
ide; (c) photodegradation due to the semiconductor immobilized in the
membrane; (d) the same as (c), but in the presence of a promoting phot
ocatalytic system), which occur simultaneously in our experimental con
ditions, were measured. The contribution of process (d), particularly
for a synergistic mixture of tri(tert-butyl) and tri-(isopropyl) vanad
ate(V) or iron(III) potassium oxalate as photocatalysts, is greater th
an that of all other processes, while UV degradation in the presence o
f hydrogen peroxide (b) represents one-tenth or less of the whole. The
rationalization of k values for this integrated membrane process is d
iscussed on the basis of their dependence on the membrane surface and
on the square root of the radiation intensity.