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模拟太阳光辐射下水溶液中的硝酸盐和天然有机物对农药敌草隆和特丁津降解的影响。

Nitrate and natural organic matter in aqueous solutions irradiated by simulated sunlight: Influence on the degradation of the pesticides dichlorprop and terbutylazine.

机构信息

Engler-Bunte-Institut, Universität Karlsruhe, Engler-Bunte-Ring 1, D-76131, Karlsruhe, Germany.

出版信息

Environ Sci Pollut Res Int. 2000;7(4):205-10. doi: 10.1007/BF02987349.

Abstract

By means of simulated sunlight, the influence of natural organic matter (NOM) on the photochemical degradation of halogenated pesticides in the absence and presence of nitrate as a precursor of the highly reactive OH radicals in aqueous solutions and freshwater was investigated. Solutions of dichlorprop or terbutylazine (a) in phosphate-buffered demineralized water containing nitrate and/or NOM and (b) in natural freshwaters were irradiated by a 1000-W Xe short-arc lamp. The collimated beam was filtered using a combination of optical filters (WG 320 and WG 295) to simulate the solar spectrum under summer midday conditions. In the absence of nitrate and NOM, the pesticides were degraded photolytically by simulated sunlight. The degradation rates depended on the absorption spectrum in the UVB range and the quantum yield of the degradation. The photochemical degradation of the pesticides was faster in the presence of nitrate due to the sunlight-induced formation of OH radicals. In the absence of nitrate, low concentrations of NOM of a brownwater lake accelerated the degradation due to the formation of reactive species by NOM. At higher concentrations of NOM, the inner filter effect of NOM lowered the degradation rates. In the presence of 50 mg l-1 nitrate, NOM decreased the degradation rate significantly. In case the natural water samples were used as a matrix for the experiments (nitrate concentrations 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 radicals. As a consequence, in most freshwater systems, the accelerating effect of NOM by the formation of reactive species is of minor importance compared to the inner filter effect and to radical scavenging.

摘要

利用模拟太阳光,研究了天然有机物 (NOM) 在不存在和存在硝酸盐的情况下对水中卤代农药光化学降解的影响,硝酸盐是水中高反应性 OH 自由基的前体。在含有硝酸盐和/或 NOM 的磷酸盐缓冲去矿物质水中(a)和在天然淡水中(b),将二氯丙或特丁津的溶液用光学滤光片(WG 320 和 WG 295)的组合进行辐照,以模拟夏季中午条件下的太阳光谱。在不存在硝酸盐和 NOM 的情况下,农药通过模拟太阳光光解降解。降解速率取决于在 UVB 范围内的吸收光谱和降解的量子产率。由于阳光诱导形成 OH 自由基,农药在存在硝酸盐的情况下光化学降解更快。在不存在硝酸盐的情况下,低浓度的棕色水湖水 NOM 由于 NOM 形成了反应性物质而加速了降解。在 NOM 浓度较高的情况下,NOM 的内滤效应降低了降解速率。在存在 50mg/L 硝酸盐的情况下,NOM 显著降低了降解速率。如果将天然水样用作实验的基质(硝酸盐浓度在 2mg/L 到 15mg/L 之间,DOC 浓度低于 2.3mg/L),NOM 主要作为辐射过滤器和 OH 自由基的清除剂。因此,在大多数淡水系统中,与内滤效应和自由基清除相比,NOM 通过形成反应性物质的加速效应的重要性较小。

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