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[地表水净化处理过程中诱变化合物的产生]

[Production of mutagenic compounds during the water purification treatment of surface water].

作者信息

Gilli G, Carraro E, Ferrara A

机构信息

Dipartimento di Igiene e Medicina di Comunità, Università degli Studi, Torino.

出版信息

Ann Ist Super Sanita. 1991;27(4):657-64.

PMID:1668195
Abstract

In the last years many studies have reported the presence of mutagenic/carcinogenic compounds in treated waters. These substances can be present in raw water, but are also produced during drinking water purification. Mutagens are formed as by-products of chemical reactions between oxidants/disinfectants used in treatments and organic load of the raw water (humic and fulvic acids). The aim of this study was to evaluate the production of mutagenic substances during the main phases of the Po river water treatment ("PO3" plant) in Turin. Water samples (50 litres), collected from February 1989 to August 1990, were concentrated with XAD-2/XAD-8 resins mixture. Extracts were tested for mutagenicity at different doses (1, 2.5, 5 and 10 litres) by Ames Salmonella assay, using TA 100 and TA 98 strains, without microsome fraction (S9). Raw water was rarely mutagenic while, in particular at the highest doses (5 and 10 litres), sometimes showed toxic effect. After ozonation treatment only few samples were mutagenic with TA 100 strain, while 43% of the samples were mutagenic with TA 98. The following treatment of clariflocculation and chlorination with NaClO produced mutagens in 95% of the samples assayed with TA 100 and in 85% of the samples assayed with TA 98. The next GAC/sand filtration step seems to reduce the mutagenic load produced in the previous phases. Finally, drinking water after chlorination with ClO2 showed weak mutagenicity at 1 litre dose (26% and 21% of positive samples with TA 100 and TA 98 respectively) and this effect increased at the higher dosages.(ABSTRACT TRUNCATED AT 250 WORDS)

摘要

在过去几年中,许多研究报告了处理过的水中存在诱变/致癌化合物。这些物质可能存在于原水中,但也会在饮用水净化过程中产生。诱变剂是处理过程中使用的氧化剂/消毒剂与原水有机负荷(腐殖酸和富里酸)之间化学反应的副产物。本研究的目的是评估都灵波河水处理(“PO3”工厂)主要阶段诱变物质的产生情况。1989年2月至1990年8月采集的水样(50升)用XAD - 2/XAD - 8树脂混合物进行浓缩。提取物在不同剂量(1、2.5、5和10升)下通过艾姆斯沙门氏菌试验进行诱变性测试,使用TA 100和TA 98菌株,不使用微粒体部分(S9)。原水很少具有诱变性,而特别是在最高剂量(5和10升)时,有时会显示出毒性作用。臭氧处理后,只有少数样品对TA 100菌株具有诱变性,而43%的样品对TA 98具有诱变性。随后用NaClO进行的澄清絮凝和氯化处理在95%用TA 100检测的样品和85%用TA 98检测的样品中产生了诱变剂。接下来的颗粒活性炭/砂滤步骤似乎降低了前一阶段产生的诱变负荷。最后,用ClO2氯化后的饮用水在1升剂量时显示出较弱的诱变性(分别有26%和21%的阳性样品对TA 100和TA 98呈阳性),并且这种效应在较高剂量时会增加。(摘要截短至250字)

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