1 Integrated Laboratory Systems Inc, Research Triangle Park, NC, USA.
2 SNF SAS, rue Adrienne Bolland, ZAC de Milieux, Andrézieux, Rhône-Alpes, France.
Int J Toxicol. 2017 Mar/Apr;36(2):124-132. doi: 10.1177/1091581817697696. Epub 2017 Mar 16.
Acrylamide (AA) at high exposure levels is neurotoxic, induces testicular toxicity, and increases dominant lethal mutations in rats. RNA-sequencing in testes was used to identify differentially expressed genes (DEG), explore AA-induced pathway perturbations that could contribute to AA-induced testicular toxicity and then used to derive a benchmark dose (BMD). Male F344/DuCrl rats were administered 0.0, 0.5, 1.5, 3.0, 6.0, or 12.0 mg AA/kg bw/d in drinking water for 5, 15, or 31 days. The experimental design used exposure levels that spanned and exceeded the exposure levels used in the rat dominant lethal, 2-generation reproductive toxicology, and cancer bioassays. The time of sample collection was based on previous studies that developed gene expression-based BMD. At 12.0 mg/kg, there were 38, 33, and 65 DEG ( P value <.005; fold change >1.5) in the testes after 5, 15, or 31 days of exposure, respectively. At 31 days, there was a dose-dependent increase in the number of DEG, and at 12.0 mg/kg/d the top three functional clusters affected by AA exposure were actin filament organization, response to calcium ion, and regulation of cell proliferation. The BMD lower 95% confidence limit using DEG ranged from 1.8 to 6.8 mg/kg compared to a no-observed-adverse-effect-level of 2.0 mg/kg/d for male reproductive toxicity. These results are consistent with the known effects of AA on calcium signaling and cytoskeletal actin filaments leading to neurotoxicity and suggest that AA can cause rat dominant lethal mutations by these same mechanisms leading to impaired chromosome segregation during cell division.
丙烯酰胺(AA)在高暴露水平下具有神经毒性,可诱导睾丸毒性,并增加大鼠的显性致死突变。本研究采用睾丸 RNA 测序鉴定差异表达基因(DEG),探索 AA 诱导的通路扰动,这些扰动可能导致 AA 诱导的睾丸毒性,并进一步推导基准剂量(BMD)。雄性 F344/DuCrl 大鼠连续 5、15 或 31 天经口灌胃给予 0.0、0.5、1.5、3.0、6.0 或 12.0 mg/kg bw/dAA。实验设计的暴露水平跨越并超过了大鼠显性致死、2 代生殖毒性和癌症生物测定中使用的暴露水平。样品采集时间基于先前建立基于基因表达的 BMD 的研究。在 12.0 mg/kg 时,分别在 5、15 或 31 天的暴露后,睾丸中有 38、33 和 65 个 DEG(P 值<0.005;倍数变化>1.5)。在 31 天时,DEG 的数量呈剂量依赖性增加,在 12.0 mg/kg/d 时,受 AA 暴露影响的前三个功能簇是肌动蛋白丝组织、钙离子反应和细胞增殖调控。使用 DEG 的 BMD 下限 95%置信区间范围为 1.8 至 6.8 mg/kg,而雄性生殖毒性的无观察不良效应水平为 2.0 mg/kg/d。这些结果与 AA 对钙信号和细胞骨架肌动蛋白丝的已知作用一致,导致神经毒性,并表明 AA 可能通过相同的机制导致大鼠显性致死突变,导致细胞分裂过程中的染色体分离受损。