Halogenated bisphenol A derivatives potently inhibit human and rat 11β‐hydroxysteroid dehydrogenase 1: Structure–activity relationship and molecular docking

Chlorinated bisphenol A (BPA) derivatives are formed during chlorination process of drinking water, whereas bisphenol S (BPS) and brominated BPA and BPS (TBBPA and TBBPS) were synthesized for many industrial uses such as fire retardants. However, the effect of halogenated BPA and BPS derivatives on...

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Veröffentlicht in:Environmental toxicology 2024-05, Vol.39 (5), p.2560-2571
Hauptverfasser: Wang, Hong, Sang, Jianmin, Ji, Zhongyao, Yu, Yang, Wang, Shaowei, Zhu, Yang, Li, Huitao, Wang, Yiyan, Ge, Ren‐shan
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container_end_page 2571
container_issue 5
container_start_page 2560
container_title Environmental toxicology
container_volume 39
creator Wang, Hong
Sang, Jianmin
Ji, Zhongyao
Yu, Yang
Wang, Shaowei
Zhu, Yang
Li, Huitao
Wang, Yiyan
Ge, Ren‐shan
description Chlorinated bisphenol A (BPA) derivatives are formed during chlorination process of drinking water, whereas bisphenol S (BPS) and brominated BPA and BPS (TBBPA and TBBPS) were synthesized for many industrial uses such as fire retardants. However, the effect of halogenated BPA and BPS derivatives on glucocorticoid metabolizing enzyme 11β‐hydroxysteroid dehydrogenase 1 (11β‐HSD1) remains unclear. The inhibitory effects of 6 BPA derivatives in the inhibition of human and rat 11β‐HSD1 were investigated. The potencies for inhibition on human 11β‐HSD1 were TBBPA (IC50, 3.87 μM) = monochloro BPA (MCBPA, 4.08 μM) = trichloro BPA (TrCBPA, 4.41 μM) > tetrachloro BPA (TCBPA, 9.75 μM) > TBBPS (>100 μM) = BPS (>100 μM), and those for rat 11β‐HSD1 were TrCBPA (IC50, 2.76 μM) = MCBPA (3.75 μM) > TBBPA (39.58 μM) > TCBPA = TBBPS = BPS. All these BPA derivatives are mixed/competitive inhibitors of both human and rat enzymes. Molecular docking studies predict that MCBPA, TrCBPA, TCBPA, and TBBPA all bind to the active site of human 11β‐HSD1, forming hydrogen bonds with catalytic residue Ser170 except TCBPA. Regression of the lowest binding energy with IC50 values revealed a significant inverse linear regression. In conclusion, halogenated BPA derivatives are mostly potent inhibitors of human and rat 11β‐HSD1, and there is structure‐dependent inhibition.
doi_str_mv 10.1002/tox.24124
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However, the effect of halogenated BPA and BPS derivatives on glucocorticoid metabolizing enzyme 11β‐hydroxysteroid dehydrogenase 1 (11β‐HSD1) remains unclear. The inhibitory effects of 6 BPA derivatives in the inhibition of human and rat 11β‐HSD1 were investigated. The potencies for inhibition on human 11β‐HSD1 were TBBPA (IC50, 3.87 μM) = monochloro BPA (MCBPA, 4.08 μM) = trichloro BPA (TrCBPA, 4.41 μM) &gt; tetrachloro BPA (TCBPA, 9.75 μM) &gt; TBBPS (&gt;100 μM) = BPS (&gt;100 μM), and those for rat 11β‐HSD1 were TrCBPA (IC50, 2.76 μM) = MCBPA (3.75 μM) &gt; TBBPA (39.58 μM) &gt; TCBPA = TBBPS = BPS. All these BPA derivatives are mixed/competitive inhibitors of both human and rat enzymes. Molecular docking studies predict that MCBPA, TrCBPA, TCBPA, and TBBPA all bind to the active site of human 11β‐HSD1, forming hydrogen bonds with catalytic residue Ser170 except TCBPA. Regression of the lowest binding energy with IC50 values revealed a significant inverse linear regression. 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However, the effect of halogenated BPA and BPS derivatives on glucocorticoid metabolizing enzyme 11β‐hydroxysteroid dehydrogenase 1 (11β‐HSD1) remains unclear. The inhibitory effects of 6 BPA derivatives in the inhibition of human and rat 11β‐HSD1 were investigated. The potencies for inhibition on human 11β‐HSD1 were TBBPA (IC50, 3.87 μM) = monochloro BPA (MCBPA, 4.08 μM) = trichloro BPA (TrCBPA, 4.41 μM) &gt; tetrachloro BPA (TCBPA, 9.75 μM) &gt; TBBPS (&gt;100 μM) = BPS (&gt;100 μM), and those for rat 11β‐HSD1 were TrCBPA (IC50, 2.76 μM) = MCBPA (3.75 μM) &gt; TBBPA (39.58 μM) &gt; TCBPA = TBBPS = BPS. All these BPA derivatives are mixed/competitive inhibitors of both human and rat enzymes. Molecular docking studies predict that MCBPA, TrCBPA, TCBPA, and TBBPA all bind to the active site of human 11β‐HSD1, forming hydrogen bonds with catalytic residue Ser170 except TCBPA. Regression of the lowest binding energy with IC50 values revealed a significant inverse linear regression. 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However, the effect of halogenated BPA and BPS derivatives on glucocorticoid metabolizing enzyme 11β‐hydroxysteroid dehydrogenase 1 (11β‐HSD1) remains unclear. The inhibitory effects of 6 BPA derivatives in the inhibition of human and rat 11β‐HSD1 were investigated. The potencies for inhibition on human 11β‐HSD1 were TBBPA (IC50, 3.87 μM) = monochloro BPA (MCBPA, 4.08 μM) = trichloro BPA (TrCBPA, 4.41 μM) &gt; tetrachloro BPA (TCBPA, 9.75 μM) &gt; TBBPS (&gt;100 μM) = BPS (&gt;100 μM), and those for rat 11β‐HSD1 were TrCBPA (IC50, 2.76 μM) = MCBPA (3.75 μM) &gt; TBBPA (39.58 μM) &gt; TCBPA = TBBPS = BPS. All these BPA derivatives are mixed/competitive inhibitors of both human and rat enzymes. Molecular docking studies predict that MCBPA, TrCBPA, TCBPA, and TBBPA all bind to the active site of human 11β‐HSD1, forming hydrogen bonds with catalytic residue Ser170 except TCBPA. Regression of the lowest binding energy with IC50 values revealed a significant inverse linear regression. In conclusion, halogenated BPA derivatives are mostly potent inhibitors of human and rat 11β‐HSD1, and there is structure‐dependent inhibition.</abstract><cop>Hoboken, USA</cop><pub>John Wiley &amp; Sons, Inc</pub><pmid>38189224</pmid><doi>10.1002/tox.24124</doi><tpages>12</tpages></addata></record>
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subjects 11β‐hydroxysteroid dehydrogenase 1
binding mode analysis
Bisphenol A
Bromination
Chlorination
cortisol
Dehydrogenase
Dehydrogenases
Drinking water
Flame retardants
glucocorticoid
Glucocorticoids
halogenated bisphenols
Hydrogen bonding
Hydrogen bonds
Hydroxysteroids
Industrial applications
Inhibitors
Molecular docking
Molecular structure
title Halogenated bisphenol A derivatives potently inhibit human and rat 11β‐hydroxysteroid dehydrogenase 1: Structure–activity relationship and molecular docking
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