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1.
Aquat Toxicol ; 189: 77-86, 2017 Aug.
Article in English | MEDLINE | ID: mdl-28601011

ABSTRACT

One of the primary sources of polycyclic aromatic hydrocarbons (PAHs) in marine environments is oil. Photochemical oxidation and microbial transformation of PAH-containing oils can result in the formation of oxygenated products. Among the PAHs in crude oil, chrysene is one of the most persistent within the water column and may be transformed to 2- and 6-hydroxychrysene (OHCHR). Both of these compounds have been shown to activate (2-OHCHR) and antagonize (6-OHCHR) the estrogen receptor (ER). Previous studies in our lab have shown that estrogen can significantly alter zebrafish development. However, little is known about the developmental toxicity of hydroxylated PAHs. Zebrafish embryos were exposed to 0.5-10µM of 2- or 6-OHCHR from 2h post-fertilization (hpf) until 76hpf. A significant decrease in survival was observed following exposure to 6-OHCHR - but not 2-OHCHR. Both OHCHRs significantly increased the percentage of overall deformities after treatment. In addition to cardiac malformations, ocular and circulatory defects were also observed in embryos exposed to both compounds, while 2-OHCHR generally resulted in a higher prevalence of effect. Moreover, treatment with 2-OHCHR resulted in a significant decrease in hemoglobin levels. ER nor G-Protein coupled estrogen receptor (GPER) antagonists and agonists did not rescue the observed defects. We also analyzed the expression of cardiac-, eye- and circulation-related genes previously shown to be affected by oil. Rhodopsin mRNA expresssion was significantly decreased by both compounds equally. However, exposure to 2-OHCHR significantly increased the expression of the hematopoietic regulator, runx1 (runt related transcription factor 1). These results indicate the toxicity of oxygenated photoproducts of PAHs and suggest that other targets and signaling pathways may contribute to developmental toxicity of weathered oil. Our findings also demonstrate the regio-selective toxicity of hydroxy-PAHs in the effects on eye and circulatory development and raise the need to identify mechanisms and ecological risks of oxy-PAHs to fish populations.


Subject(s)
Chrysenes/toxicity , Embryo, Nonmammalian/drug effects , Petroleum/toxicity , Water Pollutants, Chemical/toxicity , Zebrafish/embryology , Animals , Chrysenes/metabolism , Dose-Response Relationship, Drug , Embryo, Nonmammalian/abnormalities , Embryo, Nonmammalian/metabolism , Gene Expression Regulation, Developmental/drug effects , Heart/drug effects , Heart/embryology , Organogenesis/drug effects , Organogenesis/genetics , Water Pollutants, Chemical/metabolism , Zebrafish/abnormalities , Zebrafish/genetics , Zebrafish/metabolism
2.
Aquat Toxicol ; 186: 180-187, 2017 May.
Article in English | MEDLINE | ID: mdl-28284154

ABSTRACT

Exposure to 17ß-estradiol (E2) influences the regulation of multiple signaling pathways, and E2-mediated disruption of signaling events during early development can lead to malformations such as cardiac defects. In this study, we investigated the potential role of the G-protein estrogen receptor 1 (GPER) in E2-induced developmental toxicity. Zebrafish embryos were exposed to E2 from 2h post fertilization (hpf) to 76 hpf with subsequent transcriptional measurements of heart and neural crest derivatives expressed 2 (hand2), leucine rich repeat containing 10 (lrrc10), and gper at 12, 28 and 76 hpf. Alteration in the expression of lrrc10, hand2 and gper was observed at 12 hpf and 76 hpf, but not at 28 hpf. Expression of these genes was also altered after exposure to G1 (a GPER agonist) at 76 hpf. Expression of lrrc10, hand2 and gper all coincided with the formation of cardiac edema at 76 hpf as well as other developmental abnormalities. While co-exposure of G1 with G36 (a GPER antagonist) rescued G1-induced abnormalities and altered gene expression, co-exposure of E2 with G36, or ICI 182,780 (an estrogen receptor antagonist) did not rescue E2-induced cardiac deformities or gene expression. In addition, no effects on the concentrations of downstream ER and GPER signaling molecules (cAMP or calcium) were observed in embryo homogenates after E2 treatment. These data suggest that the impacts of E2 on embryonic development at this stage are complex and may involve multiple receptor and/or signaling pathways.


Subject(s)
Embryonic Development/drug effects , Estradiol/toxicity , Receptors, G-Protein-Coupled/metabolism , Toxicity Tests , Zebrafish Proteins/metabolism , Zebrafish/embryology , Animals , Gene Expression Regulation, Developmental/drug effects , Heart/drug effects , Heart/embryology , RNA, Messenger/genetics , RNA, Messenger/metabolism , Receptors, G-Protein-Coupled/agonists , Signal Transduction/drug effects , Water Pollutants, Chemical/toxicity , Zebrafish/genetics , Zebrafish Proteins/agonists , Zebrafish Proteins/genetics
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