Medical Scientist Training Program & Department of Pharmacology and Toxicology, University of Alabama at Birmingham, Birmingham, Alabama, 35294.
Department of Molecular and Cellular Biology, Center for Precision Environmental Health, Baylor College of Medicine, Houston, Texas, 77030.
Toxicol Sci. 2019 Jul 1;170(1):25-44. doi: 10.1093/toxsci/kfz075.
The aryl hydrocarbon receptor (AHR) is a ligand-activated transcription factor that binds environmental toxicants and regulates gene expression. AHR also regulates developmental processes, like craniofacial development and hematopoiesis, in the absence of environmental exposures. Zebrafish have 3 paralogs of AHR: ahr1a, ahr1b, and ahr2. Adult zebrafish with mutations in ahr2 exhibited craniofacial and fin defects. However, the degree to which ahr1a and ahr1b influence ahr2 signaling and contribute to fin and craniofacial development are not known. We compared morphology of adult ahr2 mutants and ahr1a;ahr1b single and double mutant zebrafish. We found that ahr1a;ahr1b single and double mutants were morphologically normal whereas ahr2 mutant zebrafish demonstrated fin and craniofacial malformations. At 5 days post fertilization, both ahr1a;ahr1b and ahr2 mutant larvae were normal, suggesting that adult phenotypes are due to defects in maturation or maintenance. Next, we analyzed the function of zebrafish AHRs activated by environmental ligands. The prototypical AHR ligand, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), induces toxicity in humans and rodents via AHR and causes cardiotoxicity in zebrafish embryos. It has been shown that embryos with mutations in ahr2 are resistant to TCDD toxicity, yet it is unclear whether ahr1 receptors are required. Furthermore, though AHR was shown to interact with estrogen receptor alpha following TCDD treatment, it is not known whether this interaction is constitutive or context-dependent. To determine whether estrogen receptors are constitutive cofactors for AHR signaling, we used genetic and pharmacologic techniques to analyze TCDD-dependent toxicity in estrogen receptor and ahr mutant embryos. We found that embryos with mutations in ahr1a;ahr1b or estrogen receptor genes are susceptible to TCDD toxicity whereas ahr2 mutant embryos are TCDD-resistant. Moreover, pharmacologic blockade of nuclear estrogen receptors failed to prevent TCDD toxicity. These findings suggest that ahr1 genes do not have overlapping functions with ahr2 in fin and craniofacial development or TCDD-dependent toxicity, and that estrogen receptors are not constitutive partners of ahr2.
芳香烃受体(AHR)是一种配体激活的转录因子,可结合环境毒物并调节基因表达。AHR 还可调节颅面发育和造血等发育过程,而无需暴露于环境中。斑马鱼有 3 种 AHR 基因的同源物:ahr1a、ahr1b 和 ahr2。ahr2 突变的成年斑马鱼表现出颅面和鳍缺陷。然而,ahr1a 和 ahr1b 影响 ahr2 信号转导的程度以及对鳍和颅面发育的贡献尚不清楚。我们比较了成年 ahr2 突变体和 ahr1a;ahr1b 单突变和双突变斑马鱼的形态。我们发现 ahr1a;ahr1b 单突变和双突变斑马鱼的形态正常,而 ahr2 突变斑马鱼则表现出鳍和颅面畸形。在受精后 5 天,ahr1a;ahr1b 和 ahr2 突变体幼虫均正常,这表明成年表型是由于成熟或维持过程中的缺陷所致。接下来,我们分析了环境配体激活的斑马鱼 AHR 的功能。典型的 AHR 配体 2,3,7,8-四氯二苯并对二恶英(TCDD)通过 AHR 诱导人类和啮齿动物的毒性,并导致斑马鱼胚胎的心脏毒性。已经表明,ahr2 突变体胚胎对 TCDD 毒性具有抗性,但尚不清楚 ahr1 受体是否需要。此外,尽管已经表明 AHR 在 TCDD 处理后与雌激素受体 alpha 相互作用,但尚不清楚这种相互作用是组成型的还是依赖于上下文的。为了确定雌激素受体是否是 AHR 信号的组成型共因子,我们使用遗传和药理学技术来分析雌激素受体和 ahr 突变体胚胎中的 TCDD 依赖性毒性。我们发现,ahr1a;ahr1b 或雌激素受体基因突变的胚胎对 TCDD 毒性敏感,而 ahr2 突变体胚胎对 TCDD 具有抗性。此外,核雌激素受体的药理学阻断未能阻止 TCDD 毒性。这些发现表明,ahr1 基因在鳍和颅面发育或 TCDD 依赖性毒性中与 ahr2 没有重叠功能,并且雌激素受体不是 ahr2 的组成型伴侣。