Hunter E S, Rogers E H, Schmid J E, Richard A
Reproductive Toxicology Division, National Health and Environmental Effects Research Laboratory, U.S. EPA, Research Triangle Park, North Carolina 27711, USA.
Teratology. 1996 Aug;54(2):57-64. doi: 10.1002/(SICI)1096-9926(199606)54:2<57::AID-TERA1>3.0.CO;2-1.
A major class of disinfection by-products in drinking water are the haloacetic acids. Both dichloro- and trichloroacetic acids are teratogenic when administered to rats throughout organogenesis. However, there is little information regarding the developmental toxicity of other haloacetic acids. Therefore, 3-6 somite staged CD-1 mouse embryos were exposed to acetic acid (AA) or mono- (M), di- (D), and tri- (T) substituted fluoro- (F), chloro- (C), or bromo- (B) acetic acids in whole embryo culture in order to evaluate the effects of these agents on development. A 24 hour exposure to the haloacetic acids produced dysmorphogenesis. Effects on neural tube development ranged from prosencephalic hypoplasia to non-closure defects throughout the cranial region. Exposure to the haloacetic acids affected optic development, produced malpositioned and/or hypoplastic pharyngeal arches, and resulted in perturbation of heart development. In order to determine the relative toxicities of these agents, benchmark concentrations were calculated as the lower 95% confidence interval of the concentration that produced a 5% increase in neural tube defects. The benchmark concentrations occurred over a wide range with DFA (5912.6 microM) and MBA (2.7 microM) at the extremes. Using the benchmark concentrations to compare the chemicals gives a ranking of the agents in order of increasing potency as: DFA < TFA < DCA < AA < TBA < or = TCA < DBA < MCA < MBA. TCA and DCA have demonstrated ability to disrupt development in vivo but were among the least potent haloacetic acids in vitro. Because of the potential for widespread exposure to haloacetic acids in drinking water and the incomplete toxicity profile of these chemicals, further work on their developmental effects is warranted.
饮用水中一类主要的消毒副产物是卤代乙酸。在大鼠整个器官形成期给予二氯乙酸和三氯乙酸均具有致畸性。然而,关于其他卤代乙酸的发育毒性信息很少。因此,将3 - 6体节期的CD - 1小鼠胚胎在全胚胎培养中暴露于乙酸(AA)或单 - (M)、二 - (D)和三 - (T)取代的氟 - (F)、氯 - (C)或溴 - (B)乙酸中,以评估这些试剂对发育的影响。对卤代乙酸进行24小时暴露会导致畸形发生。对神经管发育的影响范围从整个颅前脑发育不全到未闭合缺陷。暴露于卤代乙酸会影响视觉发育,导致咽弓位置异常和/或发育不全,并导致心脏发育紊乱。为了确定这些试剂的相对毒性,计算基准浓度,即导致神经管缺陷增加5%的浓度的95%置信区间下限。基准浓度范围很广,极端情况下分别为二氟乙酸(DFA,5912.6微摩尔)和一溴乙酸(MBA,2.7微摩尔)。使用基准浓度比较这些化学物质,得到试剂按效力递增顺序的排名为:DFA < 三氟乙酸(TFA) < 二氯乙酸(DCA) < AA < 三溴乙酸(TBA) < 或 = 三氯乙酸(TCA) < 二溴乙酸(DBA) < 一氯乙酸(MCA) < MBA。三氯乙酸和二氯乙酸已证明在体内具有干扰发育的能力,但在体外却是效力最低的卤代乙酸之一。由于饮用水中可能广泛接触卤代乙酸,且这些化学物质的毒性特征不完整,因此有必要进一步研究它们对发育的影响。