Effects of plasticizer diisobutyl adipate on the Japanese medaka (Oryzias latipes) endocrine system

Plasticizer pollution of the water environment is one of the world's most serious environmental issues. Phthalate plasticizers can disrupt endocrine function in vertebrates. Therefore, this study analyzed thyroid‐related, reproduction‐related, and estrogen‐responsive genes in Japanese medaka (O...

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Veröffentlicht in:Journal of applied toxicology 2023-07, Vol.43 (7), p.982-992
Hauptverfasser: Horie, Yoshifumi, Ramaswamy, Babu Rajendran, Ríos, Juan Manuel, Yap, Chee Kong, Okamura, Hideo
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container_issue 7
container_start_page 982
container_title Journal of applied toxicology
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creator Horie, Yoshifumi
Ramaswamy, Babu Rajendran
Ríos, Juan Manuel
Yap, Chee Kong
Okamura, Hideo
description Plasticizer pollution of the water environment is one of the world's most serious environmental issues. Phthalate plasticizers can disrupt endocrine function in vertebrates. Therefore, this study analyzed thyroid‐related, reproduction‐related, and estrogen‐responsive genes in Japanese medaka (Oryzias latipes) to determine whether non‐phthalate diisobutyl adipate (DIBA) plasticizer could affect endocrine hormone activity or not. Developmental toxicity during fish embryogenesis was also evaluated. At a concentration of 11.57 mg/l, embryonic exposure to DIBA increased the mortality rate. Although abnormal development, including body curvature, edema, and lack of swim bladder inflation, was observed at 3.54 and 11.57 mg/l DIBA, growth inhibition and reduced swimming performance were also observed. In addition, DIBA exposure increased the levels of thyroid‐stimulating hormone beta‐subunit (tshβ) and deiodinase 1 (dio1) but decreased the levels of thyroid hormone receptor alpha (trα) and beta (trβ). These results suggest that DIBA has thyroid hormone‐disrupting activities in fish. However, kisspeptin (kiss1 and kiss2), gonadotropin‐releasing hormone (gnrh1), follicle‐stimulating hormone beta (fshβ), luteinizing hormone beta (lhβ), choriogenin H (chgH), and vitellogenin (vtg1) expression did not change dose‐dependently in response to DIBA exposure, whereas gnrh2 and vtg2 expression was elevated. These results indicate that DIBA has low estrogenic activity and does not disrupt the endocrine reproduction system in fish. Overall, this is the first report indicating that non‐phthalate DIBA plasticizer is embryotoxic and disrupt thyroid hormone activity in fish. Embryonic exposure to non‐phthalate plasticizer, DIBA resulted in abnormal embryo development, increased swim bladder non‐inflation in larvae, decreased swimming performance, and alterations in thyroid hormone‐related gene expression, indicating DIBA's potential to disrupt thyroid hormone activity in fish. However, this exposure had no dose‐dependent effect on kisspeptin, gonadotropin, chgH, and vtg1 expression, indicating DIBA's weak estrogenic activity and inability to disrupt the endocrine reproductive system in fish.
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Phthalate plasticizers can disrupt endocrine function in vertebrates. Therefore, this study analyzed thyroid‐related, reproduction‐related, and estrogen‐responsive genes in Japanese medaka (Oryzias latipes) to determine whether non‐phthalate diisobutyl adipate (DIBA) plasticizer could affect endocrine hormone activity or not. Developmental toxicity during fish embryogenesis was also evaluated. At a concentration of 11.57 mg/l, embryonic exposure to DIBA increased the mortality rate. Although abnormal development, including body curvature, edema, and lack of swim bladder inflation, was observed at 3.54 and 11.57 mg/l DIBA, growth inhibition and reduced swimming performance were also observed. In addition, DIBA exposure increased the levels of thyroid‐stimulating hormone beta‐subunit (tshβ) and deiodinase 1 (dio1) but decreased the levels of thyroid hormone receptor alpha (trα) and beta (trβ). These results suggest that DIBA has thyroid hormone‐disrupting activities in fish. 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Phthalate plasticizers can disrupt endocrine function in vertebrates. Therefore, this study analyzed thyroid‐related, reproduction‐related, and estrogen‐responsive genes in Japanese medaka (Oryzias latipes) to determine whether non‐phthalate diisobutyl adipate (DIBA) plasticizer could affect endocrine hormone activity or not. Developmental toxicity during fish embryogenesis was also evaluated. At a concentration of 11.57 mg/l, embryonic exposure to DIBA increased the mortality rate. Although abnormal development, including body curvature, edema, and lack of swim bladder inflation, was observed at 3.54 and 11.57 mg/l DIBA, growth inhibition and reduced swimming performance were also observed. In addition, DIBA exposure increased the levels of thyroid‐stimulating hormone beta‐subunit (tshβ) and deiodinase 1 (dio1) but decreased the levels of thyroid hormone receptor alpha (trα) and beta (trβ). These results suggest that DIBA has thyroid hormone‐disrupting activities in fish. 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Phthalate plasticizers can disrupt endocrine function in vertebrates. Therefore, this study analyzed thyroid‐related, reproduction‐related, and estrogen‐responsive genes in Japanese medaka (Oryzias latipes) to determine whether non‐phthalate diisobutyl adipate (DIBA) plasticizer could affect endocrine hormone activity or not. Developmental toxicity during fish embryogenesis was also evaluated. At a concentration of 11.57 mg/l, embryonic exposure to DIBA increased the mortality rate. Although abnormal development, including body curvature, edema, and lack of swim bladder inflation, was observed at 3.54 and 11.57 mg/l DIBA, growth inhibition and reduced swimming performance were also observed. In addition, DIBA exposure increased the levels of thyroid‐stimulating hormone beta‐subunit (tshβ) and deiodinase 1 (dio1) but decreased the levels of thyroid hormone receptor alpha (trα) and beta (trβ). These results suggest that DIBA has thyroid hormone‐disrupting activities in fish. However, kisspeptin (kiss1 and kiss2), gonadotropin‐releasing hormone (gnrh1), follicle‐stimulating hormone beta (fshβ), luteinizing hormone beta (lhβ), choriogenin H (chgH), and vitellogenin (vtg1) expression did not change dose‐dependently in response to DIBA exposure, whereas gnrh2 and vtg2 expression was elevated. These results indicate that DIBA has low estrogenic activity and does not disrupt the endocrine reproduction system in fish. Overall, this is the first report indicating that non‐phthalate DIBA plasticizer is embryotoxic and disrupt thyroid hormone activity in fish. Embryonic exposure to non‐phthalate plasticizer, DIBA resulted in abnormal embryo development, increased swim bladder non‐inflation in larvae, decreased swimming performance, and alterations in thyroid hormone‐related gene expression, indicating DIBA's potential to disrupt thyroid hormone activity in fish. However, this exposure had no dose‐dependent effect on kisspeptin, gonadotropin, chgH, and vtg1 expression, indicating DIBA's weak estrogenic activity and inability to disrupt the endocrine reproductive system in fish.</abstract><cop>England</cop><pub>Wiley Subscription Services, Inc</pub><pmid>36647207</pmid><doi>10.1002/jat.4437</doi><tpages>11</tpages><orcidid>https://orcid.org/0000-0002-4558-8624</orcidid></addata></record>
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subjects Adipates - metabolism
Animals
biomarker
chgH
diisobutyl adipate
ecotoxicity
Edema
Embryogenesis
Embryonic growth stage
endocrine disruptor
Endocrine disruptors
Endocrine System
Estrogenic activity
Estrogens
Estrogens - toxicity
Exposure
Fish reproduction
Gonadotropins
Iodide peroxidase
Kiss1 protein
Luteinizing hormone
Oryzias - metabolism
Oryzias latipes
Phthalates
Pituitary (anterior)
plasticizer
Plasticizers
Plasticizers - metabolism
Plasticizers - toxicity
Reproduction
Swim bladder
Swimming
Thyroid
Thyroid gland
thyroid hormones
Toxicity
Vertebrates
Vitellogenin
vtg
Water Pollutants, Chemical - metabolism
Water Pollutants, Chemical - toxicity
Water pollution
Xenoestrogens
title Effects of plasticizer diisobutyl adipate on the Japanese medaka (Oryzias latipes) endocrine system
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