Monitoring of methoxychlor residues in the Athabasca River system in northern Alberta after treatment for control of black fly larval populations

Kumar, Yogesh; Byrtus, G.

doi:10.1007/bf00547209

Cited by 6 publications

(3 citation statements)

References 3 publications

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“…Nevertheless, these observations are relevant to public health because MXC occurs in the environment at comparable levels. For example, the level of MXC in fish can reach levels as high as 128 μg/kg (Kumar & Byrtus, 1993). Such concentrations of MXC or HPTE have the potential to affect 3β‐HSD and 17β‐HSD3 activity.…”

Section: Discussionmentioning

confidence: 99%

Effects of methoxychlor and 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane on 3β-hydroxysteroid dehydrogenase and 17β-hydroxysteroid dehydrogenase-3 activities in human and rat testes

Zhao

Chu

et al. 2010

International Journal of Andrology

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Human and rat testis microsomes were used to investigate direct inhibitory activities of methoxychlor (MXC) and its metabolite 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE) on 3β-hydroxysteroid dehydrogenase (3β-HSD) and 17β-hydroxysteroid dehydrogenase type 3 (17β-HSD3). The 3β-HSD and 17β-HSD3 enzymes are involved in the reactions that culminate in androgen biosynthesis in Leydig cells. The results demonstrated that MXC and HPTE inhibited human 3β-HSD activity at a concentration of 10 nm. The half maximal inhibitory concentration (IC(50) ) for MXC inhibition of 3β-HSD was 53.21 ± 15.52 μm (human) and 46.15 ± 17.94 μm (rat), and for HPTE, it was 8.29 ± 2.49 μm (human) and 13.82 ± 2.26 μm (rat). At the higher concentration of 100 μm, MXC did not affect human and rat 17β-HSD3 activity. However, the IC(50) for HPTE inhibition of 17β-HSD3 was 12.1 ± 1.9 μm (human) and 32 .0 ± 8.6 μm (rat). The mode of action of MXC and HPTE on 3β-HSD activity was non-competitive with the substrate pregnenolone, but was competitive with the cofactor NAD(+) . The mode of HPTE inhibition of 17β-HSD3 was non-competitive with the substrate androstenedione, but was competitive with the cofactor NADPH. In summary, our results showed that HPTE, which is the biologically active metabolite of MXC, has the capacity for direct inhibition of 3β-HSD and 17β-HSD3 enzyme activity. Inhibition of enzyme activity is presumably associated with suppression of steroidogenesis in gonadal tissues and has implications for testis function.

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Section: Discussionmentioning

confidence: 99%

Effects of methoxychlor and 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane on 3β-hydroxysteroid dehydrogenase and 17β-hydroxysteroid dehydrogenase-3 activities in human and rat testes

Zhao

Chu

et al. 2010

International Journal of Andrology

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“…This indicates that this inhibition may be involved in the reduced metabolism of estrogen. The level of MXC in stream water can reach levels as high as 128 µg/l [30]. Thus, these observations are relevant to public health, and such concentrations of MXC or HPTE have the potential to affect CYP2C9 activity.…”

Section: Discussionmentioning

confidence: 99%

Effects of Methoxychlor and 2,2-bis (<b><i>p</i></b>-Hydroxyphenyl)-1,1,1-Trichloroethane on Cytochrome P450 Enzyme Activities in Human and Rat Livers

Chen

Pan²,

Wang³

et al. 2015

Pharmacology

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Cytochrome P450 (CYP) enzymes are involved in the metabolism of endogenous and exogenous compounds. Human and rat liver microsomes were used to investigate the inhibitory effects of methoxychlor (MXC) and its metabolite 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE) on the activities of corresponding human and rat CYPs. Probe drugs were used to test the inhibitory effects of MXC and HPTE on human and rat CYPs. The results showed that MXC and HPTE inhibited both human CYP2C9 and rat liver CYP2C11 activity, with half-maximal inhibitory concentration (IC₅₀) values of 15.47 ± 0.36 (MXC) and 8.87 ± 0.53 μmol/l (HPTE) for human CYP2C9, and of 22.45 ± 1.48 (MXC) and 24.63 ± 1.35 μmol/l (HPTE) for rat CYP2C11. MXC and HPTE had no effects on human CYP2C19 activity but inhibited rat CYP2C6 activity with IC₅₀ values of 14.84 ± 0.04 (MXC) and 8.72 ± 0.25 μmol/l (HPTE). With regard to human CYP2D6 and rat CYP2D2 activity, only HPTE potently inhibited human CYP2D6 activity, with an IC₅₀ value of 16.56 ± 0.69 μmol/l. Both chemicals had no effect on human CYP3A4 and rat CYP3A1 activity. In summary, MXC and HPTE are potent inhibitors of some human and rat CYPs.

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“…* * * Indicates significantly different when compared to control. high as 128 μg/kg [16] . Such concentrations of MXC or HPTE have the potential to affect HSD3B1 activity.…”

Section: Discussionmentioning

confidence: 99%

Effects of Methoxychlor and Its Metabolite Hydroxychlor on Human Placental 3β-Hydroxysteroid Dehydrogenase 1 and Aromatase in JEG-3 Cells

Liu¹,

Mao²,

Bai

et al. 2016

Pharmacology

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Progesterone and estradiol produced by the human placenta are critical for maintenance of pregnancy and fetal development. In the human placenta, 3β-hydroxysteroid dehydrogenase 1 (HSD3B1) is responsible for the formation of progesterone from pregnenolone and aromatase (CYP19A1) for the production of estradiol from androgen. Insecticide methoxychlor (MXC) and its metabolite hydroxychlor (HPTE) may disrupt the activities of these 2 enzymes. In this study, we investigated the effects of MXC and HPTE on steroid production in human placental JEG-3 cells and on HSD3B1 and CYP19A1 activities. MXC and HPTE inhibited progesterone and estradiol production in JEG-3 cells. MXC and HPTE were potent HSD3B1 inhibitors with the half maximal inhibitory concentration (IC₅₀) values of 2.339 ± 0.096 and 1.918 ± 0.078 μmol/l, respectively. MXC had no inhibition on CYP19A1 at 100 μmol/l, while HPTE was a weak inhibitor with IC₅₀ of 97.16 ± 0.10 μmol/l. When pregnenolone was used to determine the inhibitory mode, MXC and HPTE were found to be competitive inhibitors of HSD3B1. When cofactor NAD⁺ was used, MXC and HPTE were the noncompetitive inhibitors of HSD3B1. When testosterone was used, HPTE was a mixed inhibitor of CYP19A1. In conclusion, MXC and HPTE are potent inhibitors of human HSD3B1, and HPTE is a weak CYP19A1 inhibitor.

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Monitoring of methoxychlor residues in the Athabasca River system in northern Alberta after treatment for control of black fly larval populations

Cited by 6 publications

References 3 publications

Effects of methoxychlor and 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane on 3β-hydroxysteroid dehydrogenase and 17β-hydroxysteroid dehydrogenase-3 activities in human and rat testes

Effects of methoxychlor and 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane on 3β-hydroxysteroid dehydrogenase and 17β-hydroxysteroid dehydrogenase-3 activities in human and rat testes

Effects of Methoxychlor and 2,2-bis (<b><i>p</i></b>-Hydroxyphenyl)-1,1,1-Trichloroethane on Cytochrome P450 Enzyme Activities in Human and Rat Livers

Effects of Methoxychlor and Its Metabolite Hydroxychlor on Human Placental 3β-Hydroxysteroid Dehydrogenase 1 and Aromatase in JEG-3 Cells

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