Cruzan George, Faber Willem D, Johnson Keith A, Roberts Linda S, Hellwig Juergen, Maurissen Jacques, Beck Melissa J, Radovsky Ann, Stump Donald G
ToxWorks, Bridgeton, New Jersey 08302, USA.
Birth Defects Res B Dev Reprod Toxicol. 2005 Jun;74(3):221-32. doi: 10.1002/bdrb.20042.
This study was conducted to assess potential adverse functional and/or morphological effects of styrene on the neurological system in the F2 offspring following F0 and F1 generation whole-body inhalation exposures. Four groups of male and female Crl:CD (SD)IGS BR rats (25/sex/group) were exposed to 0, 50, 150, and 500 ppm styrene for 6 hr daily for at least 70 consecutive days prior to mating for the F0 and F1 generations. Inhalation exposure continued for the F0 and F1 females throughout mating and through gestation day 20. On lactation days 1 through 4, the F0 and F1 females received styrene in virgin olive oil via oral gavage at dose levels of 66, 117, and 300 mg/kg/day (divided into three equal doses, approximately 2 hr apart). Inhalation exposure of the F0 and F1 females was re-initiated on lactation day 5 and continued through weaning of the F1 or F2 pups on postnatal day (PND) 21. Developmental landmarks were assessed in F1 and F2 offspring. The neurological development of randomly selected pups from the F2 generation was assessed by functional observational battery, locomotor activity, acoustic startle response, learning and memory evaluations, brain weights and dimension measurements, and brain morphometric and histologic evaluation. Styrene exposure did not affect survival or the clinical condition of the animals. As expected from previous studies, slight body weight and histopathologic effects on the nasal olfactory epithelium were found in F0 and F1 rats exposed to 500 ppm and, to a lesser extent, 150 ppm. There were no indications of adverse effects on reproductive performance in either the F0 or F1 generation. There were exposure-related reductions in mean body weights of the F1 and F2 offspring from the mid and high-exposure groups and an overall pattern of slightly delayed development evident in the F2 offspring only from the 500-ppm group. This developmental delay included reduced body weight (which continued through day 70) and slightly delayed acquisition of some physical landmarks of development. Styrene exposure of the F0 and F1 animals had no effect on survival, the clinical condition or necropsy findings of the F2 animals. Functional observational battery evaluations conducted for all F1 dams during the gestation and lactation periods and for the F2 offspring were unaffected by styrene exposure. Swimming ability as determined by straight channel escape times measured on PND 24 were increased, and reduced grip strength values were evident for both sexes on PND 45 and 60 in the 500-ppm group compared to controls. There were no other parental exposure-related findings in the F2 pre-weaning and post-weaning functional observational battery assessments, the PND 20 and PND 60 auditory startle habituation parameters, in endpoints of learning and memory performance (escape times and errors) in the Biel water maze task at either testing age, or in activity levels measured on PND 61 in the 500-ppm group. Taken together, the exposure-related developmental and neuromotor changes identified in F2 pups from dams exposed to 500 ppm occurred in endpoints known to be both age- and weight-sensitive parameters, and were observed in the absence of any other remarkable indicators of neurobehavioral toxicity. Based on the results of this study, an exposure level of 50 ppm was considered to be the NOAEL for growth of F2 offspring; an exposure level of 500 ppm was considered to be the NOAEL for F2 developmental neurotoxicity.
本研究旨在评估在F0和F1代全身吸入暴露后,苯乙烯对F2代后代神经系统的潜在不良功能和/或形态学影响。四组雄性和雌性Crl:CD(SD)IGS BR大鼠(每组25只/性别)在F0和F1代交配前连续至少70天,每天暴露于0、50、150和500 ppm苯乙烯中6小时。F0和F1代雌性大鼠在整个交配期和妊娠第20天持续进行吸入暴露。在哺乳期第1至4天,F0和F1代雌性大鼠通过口服灌胃接受剂量为66、117和300 mg/kg/天(分为三等份,间隔约2小时)的苯乙烯溶于初榨橄榄油中。F0和F1代雌性大鼠在哺乳期第5天重新开始吸入暴露,并持续到F1或F2代幼崽在出生后第21天断奶。对F1和F2代后代评估发育里程碑。通过功能观察组合、运动活动、听觉惊吓反应、学习和记忆评估、脑重量和尺寸测量以及脑形态计量学和组织学评估,对F2代中随机选择的幼崽的神经发育进行评估。苯乙烯暴露未影响动物的存活或临床状况。正如先前研究预期的那样,在暴露于500 ppm以及在较小程度上暴露于150 ppm的F0和F1代大鼠中,发现体重略有下降以及鼻嗅觉上皮有组织病理学影响。在F0代或F1代中均未发现对生殖性能有不良影响的迹象。中高暴露组的F1和F2代后代平均体重出现与暴露相关的下降,并且仅在500 ppm组的F2代后代中明显存在总体发育略有延迟的模式。这种发育延迟包括体重减轻(持续到第70天)以及一些发育身体里程碑的获得略有延迟。F0和F1代动物的苯乙烯暴露对F2代动物的存活、临床状况或尸检结果没有影响。在妊娠和哺乳期对所有F1代母鼠以及对F2代后代进行的功能观察组合评估不受苯乙烯暴露的影响。与对照组相比,在500 ppm组中,出生后第24天通过直通道逃脱时间测定的游泳能力增加,并且在出生后第45天和60天,两性的握力值均降低。在F2代断奶前和断奶后的功能观察组合评估、出生后第20天和第60天的听觉惊吓习惯化参数、在两个测试年龄的Biel水迷宫任务中的学习和记忆性能终点(逃脱时间和错误)或在500 ppm组出生后第61天测量的活动水平中,没有其他与亲代暴露相关的发现。综上所述,在暴露于500 ppm的母鼠的F2代幼崽中确定的与暴露相关的发育和神经运动变化发生在已知对年龄和体重敏感的参数终点,并且是在没有任何其他明显神经行为毒性指标的情况下观察到的。基于本研究结果,50 ppm的暴露水平被认为是F2代后代生长的无观察到有害作用水平;500 ppm的暴露水平被认为是F2代发育神经毒性的无观察到有害作用水平。