Multigenerational and Transgenerational Effects of Environmentally Relevant Concentrations of Endocrine Disruptors in an Estuarine Fish Model
Many pollutants cause endocrine disruption in aquatic organisms. While studies of the direct effects of toxicants on exposed organisms are commonplace, little is known about the potential for toxicant exposures in a parental (F0) generation to affect unexposed F1 or F2 generations (multigenerational...
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Published in | Environmental science & technology Vol. 54; no. 21; pp. 13849 - 13860 |
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Main Authors | , , , , , , , , , |
Format | Journal Article |
Language | English |
Published |
United States
American Chemical Society
03.11.2020
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Subjects | |
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Abstract | Many pollutants cause endocrine disruption in aquatic organisms. While studies of the direct effects of toxicants on exposed organisms are commonplace, little is known about the potential for toxicant exposures in a parental (F0) generation to affect unexposed F1 or F2 generations (multigenerational and transgenerational effects, respectively), particularly in estuarine fishes. To investigate this possibility, we exposed inland silversides (Menidia beryllina) to environmentally relevant (low ng/L) concentrations of ethinylestradiol, bifenthrin, trenbolone, and levonorgestrel from 8 hpf to 21 dph. We then measured development, immune response, reproduction, gene expression, and DNA methylation for two subsequent generations following the exposure. Larval exposure (F0) to each compound resulted in negative effects in the F0 and F1 generations, and for ethinylestradiol and levonorgestrel, the F2 also. The specific endpoints that were responsive to exposure in each generation varied, but included increased incidence of larval deformities, reduced larval growth and survival, impaired immune function, skewed sex ratios, ovarian atresia, reduced egg production, and altered gene expression. Additionally, exposed fish exhibited differences in DNA methylation in selected genes, across all three generations, indicating epigenetic transfer of effects. These findings suggest that assessments across multiple generations are key to determining the full magnitude of adverse effects from contaminant exposure in early life. |
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AbstractList | Many pollutants cause endocrine disruption in aquatic organisms. While studies of the direct effects of toxicants on exposed organisms are commonplace, little is known about the potential for toxicant exposures in a parental (F0) generation to affect unexposed F1 or F2 generations (multigenerational and transgenerational effects, respectively), particularly in estuarine fishes. To investigate this possibility, we exposed inland silversides (Menidia beryllina) to environmentally relevant (low ng/L) concentrations of ethinylestradiol, bifenthrin, trenbolone, and levonorgestrel from 8 hpf to 21 dph. We then measured development, immune response, reproduction, gene expression, and DNA methylation for two subsequent generations following the exposure. Larval exposure (F0) to each compound resulted in negative effects in the F0 and F1 generations, and for ethinylestradiol and levonorgestrel, the F2 also. The specific endpoints that were responsive to exposure in each generation varied, but included increased incidence of larval deformities, reduced larval growth and survival, impaired immune function, skewed sex ratios, ovarian atresia, reduced egg production, and altered gene expression. Additionally, exposed fish exhibited differences in DNA methylation in selected genes, across all three generations, indicating epigenetic transfer of effects. These findings suggest that assessments across multiple generations are key to determining the full magnitude of adverse effects from contaminant exposure in early life.Many pollutants cause endocrine disruption in aquatic organisms. While studies of the direct effects of toxicants on exposed organisms are commonplace, little is known about the potential for toxicant exposures in a parental (F0) generation to affect unexposed F1 or F2 generations (multigenerational and transgenerational effects, respectively), particularly in estuarine fishes. To investigate this possibility, we exposed inland silversides (Menidia beryllina) to environmentally relevant (low ng/L) concentrations of ethinylestradiol, bifenthrin, trenbolone, and levonorgestrel from 8 hpf to 21 dph. We then measured development, immune response, reproduction, gene expression, and DNA methylation for two subsequent generations following the exposure. Larval exposure (F0) to each compound resulted in negative effects in the F0 and F1 generations, and for ethinylestradiol and levonorgestrel, the F2 also. The specific endpoints that were responsive to exposure in each generation varied, but included increased incidence of larval deformities, reduced larval growth and survival, impaired immune function, skewed sex ratios, ovarian atresia, reduced egg production, and altered gene expression. Additionally, exposed fish exhibited differences in DNA methylation in selected genes, across all three generations, indicating epigenetic transfer of effects. These findings suggest that assessments across multiple generations are key to determining the full magnitude of adverse effects from contaminant exposure in early life. Many pollutants cause endocrine disruption in aquatic organisms. While studies of the direct effects of toxicants on exposed organisms are commonplace, little is known about the potential for toxicant exposures in a parental (F0) generation to affect unexposed F1 or F2 generations (multigenerational and transgenerational effects, respectively), particularly in estuarine fishes. To investigate this possibility, we exposed inland silversides (Menidia beryllina) to environmentally relevant (low ng/L) concentrations of ethinylestradiol, bifenthrin, trenbolone, and levonorgestrel from 8 hpf to 21 dph. We then measured development, immune response, reproduction, gene expression, and DNA methylation for two subsequent generations following the exposure. Larval exposure (F0) to each compound resulted in negative effects in the F0 and F1 generations, and for ethinylestradiol and levonorgestrel, the F2 also. The specific endpoints that were responsive to exposure in each generation varied, but included increased incidence of larval deformities, reduced larval growth and survival, impaired immune function, skewed sex ratios, ovarian atresia, reduced egg production, and altered gene expression. Additionally, exposed fish exhibited differences in DNA methylation in selected genes, across all three generations, indicating epigenetic transfer of effects. These findings suggest that assessments across multiple generations are key to determining the full magnitude of adverse effects from contaminant exposure in early life. Many pollutants cause endocrine disruption in aquatic organisms. While studies of the direct effects of toxicants on exposed organisms are commonplace, little is known about the potential for toxicant exposures in a parental (F0) generation to affect unexposed F1 or F2 generations (multigenerational and transgenerational effects, respectively), particularly in estuarine fishes. To investigate this possibility, we exposed inland silversides ( ) to environmentally relevant (low ng/L) concentrations of ethinylestradiol, bifenthrin, trenbolone, and levonorgestrel from 8 hpf to 21 dph. We then measured development, immune response, reproduction, gene expression, and DNA methylation for two subsequent generations following the exposure. Larval exposure (F0) to each compound resulted in negative effects in the F0 and F1 generations, and for ethinylestradiol and levonorgestrel, the F2 also. The specific endpoints that were responsive to exposure in each generation varied, but included increased incidence of larval deformities, reduced larval growth and survival, impaired immune function, skewed sex ratios, ovarian atresia, reduced egg production, and altered gene expression. Additionally, exposed fish exhibited differences in DNA methylation in selected genes, across all three generations, indicating epigenetic transfer of effects. These findings suggest that assessments across multiple generations are key to determining the full magnitude of adverse effects from contaminant exposure in early life. |
Author | Roark, Hunter K Major, Kaley M Brander, Susanne M White, J. Wilson Connon, Richard E DeCourten, Bethany M Li, Jie Mehinto, Alvine C Forbes, Joshua P Burns, Nathan P |
AuthorAffiliation | Department of Environmental and Molecular Toxicology Department of Fisheries and Wildlife, Coastal Oregon Marine Experiment Station Bioinformatics Core, Genome Center Department of Biology and Marine Biology University of California, Davis Department of Anatomy, Physiology & Cell Biology, School of Veterinary Medicine |
AuthorAffiliation_xml | – name: Department of Anatomy, Physiology & Cell Biology, School of Veterinary Medicine – name: Bioinformatics Core, Genome Center – name: Department of Fisheries and Wildlife, Coastal Oregon Marine Experiment Station – name: Department of Biology and Marine Biology – name: Department of Environmental and Molecular Toxicology – name: University of California, Davis |
Author_xml | – sequence: 1 givenname: Bethany M orcidid: 0000-0002-1880-6809 surname: DeCourten fullname: DeCourten, Bethany M email: bmdecourten@ucdavis.edu organization: Department of Anatomy, Physiology & Cell Biology, School of Veterinary Medicine – sequence: 2 givenname: Joshua P surname: Forbes fullname: Forbes, Joshua P organization: Department of Biology and Marine Biology – sequence: 3 givenname: Hunter K surname: Roark fullname: Roark, Hunter K organization: Department of Biology and Marine Biology – sequence: 4 givenname: Nathan P surname: Burns fullname: Burns, Nathan P organization: Department of Biology and Marine Biology – sequence: 5 givenname: Kaley M surname: Major fullname: Major, Kaley M organization: Department of Environmental and Molecular Toxicology – sequence: 6 givenname: J. Wilson orcidid: 0000-0003-3242-2454 surname: White fullname: White, J. Wilson organization: Department of Fisheries and Wildlife, Coastal Oregon Marine Experiment Station – sequence: 7 givenname: Jie surname: Li fullname: Li, Jie organization: University of California, Davis – sequence: 8 givenname: Alvine C surname: Mehinto fullname: Mehinto, Alvine C – sequence: 9 givenname: Richard E surname: Connon fullname: Connon, Richard E organization: Department of Anatomy, Physiology & Cell Biology, School of Veterinary Medicine – sequence: 10 givenname: Susanne M surname: Brander fullname: Brander, Susanne M organization: Department of Fisheries and Wildlife, Coastal Oregon Marine Experiment Station |
BackLink | https://www.ncbi.nlm.nih.gov/pubmed/32989987$$D View this record in MEDLINE/PubMed |
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Snippet | Many pollutants cause endocrine disruption in aquatic organisms. While studies of the direct effects of toxicants on exposed organisms are commonplace, little... |
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SubjectTerms | abnormal development Animals Aquatic organisms bifenthrin Contaminants Deoxyribonucleic acid DNA DNA methylation Ecotoxicology and Public Health Egg production Endocrine disruptors Endocrine Disruptors - toxicity Environmental effects Epigenetics Estuaries estuarine fish Estuarine pollution Ethinyl Estradiol - toxicity Ethinylestradiol Exposure Fishes Gene expression Immune response Immune system Insecticides larvae Larval development Menidia beryllina Pollutants Reproduction technology toxic substances Toxicants Trenbolone Water Pollutants, Chemical - toxicity |
Title | Multigenerational and Transgenerational Effects of Environmentally Relevant Concentrations of Endocrine Disruptors in an Estuarine Fish Model |
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