National Exposure Research Laboratory, U.S. Environmental Protection Agency, 960 College Station Rd., Athens, Georgia 30605, USA.
Environ Sci Technol. 2011 Aug 15;45(16):6845-54. doi: 10.1021/es200983f. Epub 2011 Jul 15.
Iodinated X-ray contrast media (ICM) were investigated as a source of iodine in the formation of iodo-trihalomethane (iodo-THM) and iodo-acid disinfection byproducts (DBPs), both of which are highly genotoxic and/or cytotoxic in mammalian cells. ICM are widely used at medical centers to enable imaging of soft tissues (e.g., organs, veins, blood vessels) and are designed to be inert substances, with 95% eliminated in urine and feces unmetabolized within 24 h. ICM are not well removed in wastewater treatment plants, such that they have been found at elevated concentrations in rivers and streams (up to 100 μg/L). Naturally occurring iodide in source waters is believed to be a primary source of iodine in the formation of iodo-DBPs, but a previous 23-city iodo-DBP occurrence study also revealed appreciable levels of iodo-DBPs in some drinking waters that had very low or no detectable iodide in their source waters. When 10 of the original 23 cities' source waters were resampled, four ICM were found--iopamidol, iopromide, iohexol, and diatrizoate--with iopamidol most frequently detected, in 6 of the 10 plants sampled, with concentrations up to 2700 ng/L. Subsequent controlled laboratory reactions of iopamidol with aqueous chlorine and monochloramine in the absence of natural organic matter (NOM) produced only trace levels of iodo-DBPs; however, when reacted in real source waters (containing NOM), chlorine and monochloramine produced significant levels of iodo-THMs and iodo-acids, up to 212 nM for dichloroiodomethane and 3.0 nM for iodoacetic acid, respectively, for chlorination. The pH behavior was different for chlorine and monochloramine, such that iodo-DBP concentrations maximized at higher pH (8.5) for chlorine, but at lower pH (6.5) for monochloramine. Extracts from chloraminated source waters with and without iopamidol, as well as from chlorinated source waters with iopamidol, were the most cytotoxic samples in mammalian cells. Source waters with iopamidol but no disinfectant added were the least cytotoxic. While extracts from chlorinated and chloraminated source waters were genotoxic, the addition of iopamidol enhanced their genotoxicity. Therefore, while ICM are not toxic in themselves, their presence in source waters may be a source of concern because of the formation of highly toxic iodo-DBPs in chlorinated and chloraminated drinking water.
碘造影剂(ICM)被研究为碘三卤甲烷(碘-THM)和碘酸消毒副产物(DBP)形成的碘源,这些物质在哺乳动物细胞中都具有高度遗传毒性和/或细胞毒性。ICM 在医疗中心被广泛用于使软组织(如器官、静脉、血管)成像,设计为惰性物质,95%在尿液中排出,24 小时内未代谢的粪便中有 95%排出。ICM 在废水处理厂中不能很好地去除,因此在河流和溪流中发现其浓度升高(高达 100μg/L)。水源中天然存在的碘化物被认为是形成碘-DBP 的碘的主要来源,但之前的 23 个城市的碘-DBP 发生研究也表明,在一些饮用水中存在相当水平的碘-DBP,而这些饮用水的水源中几乎没有或没有可检测到的碘化物。当对最初的 23 个城市中的 10 个水源进行重新采样时,发现了四种 ICM——iopamidol、iopromide、iohexol 和 diatrizoate——其中iopamidol 被检测到的频率最高,在采样的 10 个工厂中的 6 个工厂中均有检出,浓度高达 2700ng/L。随后在没有天然有机物(NOM)的情况下,用氯和一氯胺在实验室控制条件下对 iopamidol 进行反应,只产生痕量的碘-DBP;然而,当在实际的水源(含有 NOM)中反应时,氯和一氯胺会产生大量的碘三卤甲烷和碘酸,分别达到二氯碘甲烷 212nM 和碘乙酸 3.0nM,用于氯化。氯和一氯胺的 pH 行为不同,使得碘-DBP 浓度在较高 pH(8.5)时达到最大值,而在较低 pH(6.5)时达到最大值。用氯和一氯胺处理含 iopamidol 和不含 iopamidol 的水源提取物以及用氯处理含 iopamidol 的水源提取物是哺乳动物细胞中最具细胞毒性的样品。添加了消毒剂的水源提取物没有添加碘造影剂,其细胞毒性最小。虽然氯化和氯胺化的水源提取物具有遗传毒性,但添加 iopamidol 增强了其遗传毒性。因此,虽然 ICM 本身并不有毒,但由于在氯化和氯胺化饮用水中形成了高毒性的碘-DBP,它们在水源中的存在可能是一个令人担忧的来源。