Nitrate and natural organic matter in aqueous solutions irradiated by simulated sunlight - Influence on the degradation of the pesticides dichlorpropand terbutylazine
Aj. Schindelin et Fh. Frimmel, Nitrate and natural organic matter in aqueous solutions irradiated by simulated sunlight - Influence on the degradation of the pesticides dichlorpropand terbutylazine, ENV SCI P R, 7(4), 2000, pp. 205-210
By means of simulated sunlight, the influence of natural organic matter (NO
M) on the photochemical degradation of halogenated pesticides in the absenc
e and presence of nitrate as a precursor of the highly reactive OH radicals
in aqueous solutions and freshwater was investigated. Solutions of dichlor
prop or terbutylazine (a) in phosphate-buffered demineralized water contain
ing nitrate and/or NOM and (b) in natural freshwaters were irradiated by a
1000-W Xe short-are lamp. The collimated beam was filtered using a combinat
ion of optical filters (WG 320 and WG 295) to simulate the solar spectrum u
nder summer midday conditions. In the absence of nitrate and NOM, the pesti
cides were degraded photolytically by simulated sunlight. The degradation r
ates depended on the absorption spectrum in the UVB range and the quantum y
ield of the degradation. The photochemical degradation of the pesticides wa
s faster in the presence of nitrate due to the sunlight-induced formation o
f OH radicals. In the absence of nitrate, low concentrations of NOM of a br
own-water lake accelerated the degradation due to the formation of reactive
species by NOM. At higher concentrations of NOM, the inner filter effect o
f NOM lowered the degradation rates. In the presence of: 50 mg 1(-1) nitrat
e, NOM decreased the degradation rate significantly. In case the natural wa
ter samples were used as a matrix for the experiments (nitrate concentratio
ns between 2 mg l(-1) and 15 mg l(-1), DOC concentrations below 2.3 mg l(-1
)), NOM acted mainly as a radiation filter and as a scavenger of OH radical
s. As a consequence, in most freshwater systems, the accelerating effect of
NOM by the formation of reactive species is of minor importance compared t
o the inner filter effect and to radical scavenging.