Nitrate and natural organic matter in aqueous solutions irradiated by simulated sunlight - Influence on the degradation of the pesticides dichlorpropand terbutylazine

Citation
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
Citations number
21
Categorie Soggetti
Environment/Ecology
Journal title
ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH
ISSN journal
09441344 → ACNP
Volume
7
Issue
4
Year of publication
2000
Pages
205 - 210
Database
ISI
SICI code
0944-1344(2000)7:4<205:NANOMI>2.0.ZU;2-R
Abstract
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.