College of Population, Resources and Environment, Shandong Normal University, 88 East Wenhua Road, Jinan, Shandong 250014, PR China.
Water Res. 2013 Jun 1;47(9):3211-9. doi: 10.1016/j.watres.2013.03.037. Epub 2013 Mar 26.
The presence of microcystins (MCs) in water sources is of concern due to their direct threats to human health and potential to form oxidation by-products (OBPs) in finished water. To control the environmental risk of MCs related OBPs, we evaluated their generative mechanisms and biological toxicity by mass spectrometry technology and molecular toxicity experiment. Exposed to UV/H2O2, model toxin microcystin-LR (MCLR) in clean water was quickly transformed but successively generated seven types of MCLR-OBPs with the chemical formulas of C49H74N10O13, C49H76N10O14, C49H78N10O16, C49H76N10O15, C37H58N10O12, C33H54N10O12, and C34H54N10O12. Probable isomers for each MCLR-OBP type were then separated and identified, indicating the aromatic ring and conjugated diene in Adda and the CC bond in Mdha were the major target sites of oxidation. Though subsequent toxicology data showed the toxicity of MCLR-OBPs on protein phosphatases 1 and 2A decreased with the extending of treatment by and large, they still possessed considerable biological toxicity (especially for product d). Influenced by MCLR-OBP distribution, concentration and residual toxicity, the secondary pollution of MCLR-OBPs in drinking water also deserved further attention even though MCLR was totally destroyed.
水中微囊藻毒素(MCs)的存在令人担忧,因为它们直接威胁到人类健康,并有可能在饮用水中形成氧化副产物(OBPs)。为了控制与 MCs 相关 OBPs 的环境风险,我们利用质谱技术和分子毒性实验评估了它们的生成机制和生物毒性。在 UV/H2O2 作用下,清洁水中的模式毒素微囊藻毒素-LR(MCLR)迅速转化,但随后相继生成了 7 种具有化学式 C49H74N10O13、C49H76N10O14、C49H78N10O16、C49H76N10O15、C37H58N10O12、C33H54N10O12 和 C34H54N10O12 的 MCLR-OBPs。然后对每种 MCLR-OBP 类型的可能异构体进行了分离和鉴定,表明 Adda 中的芳香环和共轭二烯以及 Mdha 中的 CC 键是氧化的主要靶标。尽管随后的毒理学数据表明,MCLR-OBPs 对蛋白磷酸酶 1 和 2A 的毒性随着处理时间的延长而总体上降低,但它们仍然具有相当大的生物毒性(特别是对于产物 d)。受 MCLR-OBP 分布、浓度和残留毒性的影响,即使 MCLR 被完全破坏,饮用水中 MCLR-OBPs 的二次污染也值得进一步关注。