Nelson Krysta R, Schroeder Anthony L, Ankley Gerald T, Blackwell Brett R, Blanksma Chad, Degitz Sigmund J, Flynn Kevin M, Jensen Kathleen M, Johnson Rodney D, Kahl Michael D, Knapen Dries, Kosian Patricia A, Milsk Rebecca Y, Randolph Eric C, Saari Travis, Stinckens Evelyn, Vergauwen Lucia, Villeneuve Daniel L
Student Services Contractor, U.S. Environmental Protection Agency, Office of Research and Development, National Health and Environmental Effects Research Laboratory, Mid-Continent Ecology Division, 6201Congdon Blvd., Duluth, MN 55804, USA.
U.S. Environmental Protection Agency, Office of Research and Development, National Health and Environmental Effects Research Laboratory, Mid-Continent Ecology Division, 6201Congdon Blvd., Duluth, MN 55804, USA; University of Minnesota-Twin Cities, Water Resources Center, 1985 Lower Buford Circle, St. Paul, MN 55108, USA.
Aquat Toxicol. 2016 Apr;173:192-203. doi: 10.1016/j.aquatox.2015.12.024. Epub 2016 Jan 7.
In the present study, a hypothesized adverse outcome pathway linking inhibition of thyroid peroxidase (TPO) activity to impaired swim bladder inflation was investigated in two experiments in which fathead minnows (Pimephales promelas) were exposed to 2-mercaptobenzothiazole (MBT). Continuous exposure to 1mg MBT/L for up to 22 days had no effect on inflation of the posterior chamber of the swim bladder, which typically inflates around 6 days post fertilization (dpf), a period during which maternally-derived thyroid hormone is presumed to be present. In contrast, inflation of the anterior swim bladder, which occurs around 14dpf, was impacted. Specifically, at 14dpf, approximately 50% of fish exposed to 1mg MBT/L did not have an inflated anterior swim bladder. In fish exposed to MBT through 21 or 22dpf, the anterior swim bladder was able to inflate, but the ratio of the anterior/posterior chamber length was significantly reduced compared to controls. Both abundance of thyroid peroxidase mRNA and thyroid follicle histology suggest that fathead minnows mounted a compensatory response to the presumed inhibition of TPO activity by MBT. Time-course characterization showed that fish exposed to MBT for at least 4 days prior to normal anterior swim bladder inflation had significant reductions in anterior swim bladder size, relative to the posterior chamber, compared to controls. These results, along with similar results observed in zebrafish (see part II, this issue) are consistent with the hypothesis that thyroid hormone signaling plays a significant role in mediating anterior swim bladder inflation and development in cyprinids, and that role can be disrupted by exposure to thyroid hormone synthesis inhibitors. Nonetheless, possible thyroid-independent actions of MBT on anterior swim bladder inflation cannot be ruled out based on the present results. Overall, although anterior swim bladder inflation has not been directly linked to survival as posterior swim bladder inflation has, potential links to adverse ecological outcomes are plausible given involvement of the anterior chamber in sound production and detection.
在本研究中,通过两个实验对一条假定的不良结局途径进行了研究,该途径将甲状腺过氧化物酶(TPO)活性的抑制与鱼鳔充气受损联系起来,实验中黑头呆鱼(Pimephales promelas)暴露于2-巯基苯并噻唑(MBT)。连续暴露于1mg MBT/L长达22天,对受精后约6天通常会充气的鱼鳔后室的充气没有影响,据推测在这一时期存在母体来源的甲状腺激素。相比之下,受精后约14天发生的鱼鳔前室的充气受到了影响。具体而言,在14天受精期时,暴露于1mg MBT/L的鱼中约50%没有充气的鱼鳔前室。在暴露于MBT直至21或22天受精期的鱼中,鱼鳔前室能够充气,但与对照组相比,前/后室长度比显著降低。甲状腺过氧化物酶mRNA的丰度和甲状腺滤泡组织学均表明,黑头呆鱼对MBT假定的TPO活性抑制产生了代偿反应。时间进程特征表明,在正常鱼鳔前室充气前至少4天暴露于MBT的鱼,与对照组相比,其鱼鳔前室相对于后室的大小显著减小。这些结果,以及在斑马鱼中观察到的类似结果(见本期第二部分),与甲状腺激素信号在介导鲤科鱼类鱼鳔前室充气和发育中起重要作用的假设一致,并且该作用可因暴露于甲状腺激素合成抑制剂而受到干扰。尽管如此,基于目前的结果,不能排除MBT对鱼鳔前室充气可能存在的非甲状腺依赖性作用。总体而言,虽然鱼鳔前室充气尚未像鱼鳔后室充气那样直接与生存相关联,但鉴于前室参与声音产生和检测,与不良生态结果的潜在联系似乎是合理的。