F. Macasek et al., RADIATION OXIDATION OF PHENOL IN THE PRESENCE OF PETROCHEMICAL WASTE-WATER COMPONENTS, Journal of radioanalytical and nuclear chemistry, 191(1), 1995, pp. 129-143
Radiolytical decomposition of phenol was investigated at Co-60 gamma i
rradiation (1-2 Gy . s(-1) less than or equal to 10 kGy) of pre- and c
ontinuously aerated aqueous solutions at concentrations of phenol 1-10
0 mg . . dm(-3) and in the presence of sodium hydroxide, sulphuric aci
d, sodium and ferrous sulphate, formaldehyde, 2-propanol, n-hexane, xy
lene, benzene, and commercial gasoline. From the decomposition rate at
doses 50-400 Gy, a phenomenological model of linear relation between
the dose acquired for 37% decomposition (D-37) initial concentration (
g . m(-3)) of phenol (p(0)) and of an admixture (s(0)) was confirmed i
n the form D-37 = 52f(tr)(p(0) + f(eq) s(0)), whereas are constants wh
ich can be attributed to the relative transformation resistance of phe
nol towards the OH radicals in given matrix (f(tr), for pure water f(t
r)=1) and relative acceptor capacity of competing substrate (f(eq)). I
n real wastewater, the efficient decrease of phenols content may be su
bstantially lower than that in model solutions, obviously due to radia
tion oxidation of aromates, as proved by irradiation of aqueous soluti
ons of benzene. Technical and economical feasibility of the process is
discussed.