The peripubertal male rat assay as an alternative to the Hershberger castrated male rat assay for the detection of anti-androgens, oestrogens and metabolic modulators

A range of chemicals with various levels of activity as actual or potential endocrine disrupters have been evaluated for activity in the peripubertal male rat assay. The chemicals studied included anti‐androgens (vinclozolin), cyproterone acetate, flutamide, 2,2‐bis(4‐chlorophenyl)‐1,1‐dichloroethyl...

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Published inJournal of applied toxicology Vol. 20; no. 1; pp. 35 - 47
Main Authors Ashby, J., Lefevre, P. A.
Format Journal Article
LanguageEnglish
Published Chichester, UK John Wiley & Sons, Ltd 01.01.2000
Wiley
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ISSN0260-437X
1099-1263
DOI10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8

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Abstract A range of chemicals with various levels of activity as actual or potential endocrine disrupters have been evaluated for activity in the peripubertal male rat assay. The chemicals studied included anti‐androgens (vinclozolin), cyproterone acetate, flutamide, 2,2‐bis(4‐chlorophenyl)‐1,1‐dichloroethylene (DDE), metabolic modulators (anastrazole, finasteride, ketoconazole) and oestrogens (butyl benzyl phthalate (BBP), methoxychlor, bisphenol A (BPA), diethylstilboestrol (DES)), the suspected anti‐androgen dibutyl phthalate (DBP) and the non‐oestrogen fenitrothion. Dosing extended over postnatal days (pnd) 22–35, 36–50, 36–55 and 22–35, with recovery to pnd 55 or 22–55. The endpoints studied were changes in the weights of testes, epididymides, seminal vesicles and prostate. Changes in body weight and the weights of the liver and kidney were also monitored. In some experiments changes in the day of prepuce separation (PPS) were also determined. Only BBP and BPA were inactive in all the assays conducted. Changes in the weight of reproductive tissues provided a sensitive indicator of activity for the remaining chemicals with the exception of DDE, for which higher dose levels could have been used. However, none of the curtailed periods of exposure were able to detect all of the agents. Diethyl stilboestrol, and to a lesser extent DBP and DDE, delayed PPS when exposure occurred over the period pnd 22–55. A complex dependence of the day of PPS on the period of exposure and the body weight of the test animals was observed, and caution is recommended when assessing this endpoint in the presence of reductions in body weight. It is concluded that reproductive tissue weight changes in the peripubertal male have shown sensitivity to a range of biochemical modulators, oestrogens and anti‐androgens, and that as such the assay warrants further evaluation. Measurement of delays in PPS may be of value in cases of large delays, but delays of 1–2 days will be difficult to interpret with confidence. The present results are discussed within the context of the sexually mature male rat assay described by O’Connor and the castrated male rat assay described by Hershberger, both of which are the subject of current international study. It is concluded that a decision on the usefulness of the peripubertal male rat assay must await the generation of further data on each of these three assays. There is an urgent need for international agreement on a list of reference endocrine disrupters and their active dose levels, with which to validate individual endocrine disruption assays and batteries of assays. Copyright © 2000 John Wiley & Sons, Ltd.
AbstractList A range of chemicals with various levels of activity as actual or potential endocrine disrupters have been evaluated for activity in the peripubertal male rat assay. The chemicals studied included anti-androgens (vinclozolin), cyproterone acetate, flutamide, 2, 2-bis(4-chlorophenyl)-1,1-dichloroethylene (DDE), metabolic modulators (anastrazole, finasteride, ketoconazole) and oestrogens (butyl benzyl phthalate (BBP), methoxychlor, bisphenol A (BPA), diethylstilboestrol (DES)), the suspected anti-androgen dibutyl phthalate (DBP) and the non-oestrogen fenitrothion. Dosing extended over postnatal days (pnd) 22-35, 36-50, 36-55 and 22-35, with recovery to pnd 55 or 22-55. The endpoints studied were changes in the weights of testes, epididymides, seminal vesicles and prostate. Changes in body weight and the weights of the liver and kidney were also monitored. In some experiments changes in the day of prepuce separation (PPS) were also determined. Only BBP and BPA were inactive in all the assays conducted. Changes in the weight of reproductive tissues provided a sensitive indicator of activity for the remaining chemicals with the exception of DDE, for which higher dose levels could have been used. However, none of the curtailed periods of exposure were able to detect all of the agents. Diethyl stilboestrol, and to a lesser extent DBP and DDE, delayed PPS when exposure occurred over the period pnd 22-55. A complex dependence of the day of PPS on the period of exposure and the body weight of the test animals was observed, and caution is recommended when assessing this endpoint in the presence of reductions in body weight. It is concluded that reproductive tissue weight changes in the peripubertal male have shown sensitivity to a range of biochemical modulators, oestrogens and anti-androgens, and that as such the assay warrants further evaluation. Measurement of delays in PPS may be of value in cases of large delays, but delays of 1-2 days will be difficult to interpret with confidence. The present results are discussed within the context of the sexually mature male rat assay described by O'Connor and the castrated male rat assay described by Hershberger, both of which are the subject of current international study. It is concluded that a decision on the usefulness of the peripubertal male rat assay must await the generation of further data on each of these three assays. There is an urgent need for international agreement on a list of reference endocrine disrupters and their active dose levels, with which to validate individual endocrine disruption assays and batteries of assays.A range of chemicals with various levels of activity as actual or potential endocrine disrupters have been evaluated for activity in the peripubertal male rat assay. The chemicals studied included anti-androgens (vinclozolin), cyproterone acetate, flutamide, 2, 2-bis(4-chlorophenyl)-1,1-dichloroethylene (DDE), metabolic modulators (anastrazole, finasteride, ketoconazole) and oestrogens (butyl benzyl phthalate (BBP), methoxychlor, bisphenol A (BPA), diethylstilboestrol (DES)), the suspected anti-androgen dibutyl phthalate (DBP) and the non-oestrogen fenitrothion. Dosing extended over postnatal days (pnd) 22-35, 36-50, 36-55 and 22-35, with recovery to pnd 55 or 22-55. The endpoints studied were changes in the weights of testes, epididymides, seminal vesicles and prostate. Changes in body weight and the weights of the liver and kidney were also monitored. In some experiments changes in the day of prepuce separation (PPS) were also determined. Only BBP and BPA were inactive in all the assays conducted. Changes in the weight of reproductive tissues provided a sensitive indicator of activity for the remaining chemicals with the exception of DDE, for which higher dose levels could have been used. However, none of the curtailed periods of exposure were able to detect all of the agents. Diethyl stilboestrol, and to a lesser extent DBP and DDE, delayed PPS when exposure occurred over the period pnd 22-55. A complex dependence of the day of PPS on the period of exposure and the body weight of the test animals was observed, and caution is recommended when assessing this endpoint in the presence of reductions in body weight. It is concluded that reproductive tissue weight changes in the peripubertal male have shown sensitivity to a range of biochemical modulators, oestrogens and anti-androgens, and that as such the assay warrants further evaluation. Measurement of delays in PPS may be of value in cases of large delays, but delays of 1-2 days will be difficult to interpret with confidence. The present results are discussed within the context of the sexually mature male rat assay described by O'Connor and the castrated male rat assay described by Hershberger, both of which are the subject of current international study. It is concluded that a decision on the usefulness of the peripubertal male rat assay must await the generation of further data on each of these three assays. There is an urgent need for international agreement on a list of reference endocrine disrupters and their active dose levels, with which to validate individual endocrine disruption assays and batteries of assays.
A range of chemicals with various levels of activity as actual or potential endocrine disrupters have been evaluated for activity in the peripubertal male rat assay. The chemicals studied included anti‐androgens (vinclozolin), cyproterone acetate, flutamide, 2,2‐bis(4‐chlorophenyl)‐1,1‐dichloroethylene (DDE), metabolic modulators (anastrazole, finasteride, ketoconazole) and oestrogens (butyl benzyl phthalate (BBP), methoxychlor, bisphenol A (BPA), diethylstilboestrol (DES)), the suspected anti‐androgen dibutyl phthalate (DBP) and the non‐oestrogen fenitrothion. Dosing extended over postnatal days (pnd) 22–35, 36–50, 36–55 and 22–35, with recovery to pnd 55 or 22–55. The endpoints studied were changes in the weights of testes, epididymides, seminal vesicles and prostate. Changes in body weight and the weights of the liver and kidney were also monitored. In some experiments changes in the day of prepuce separation (PPS) were also determined. Only BBP and BPA were inactive in all the assays conducted. Changes in the weight of reproductive tissues provided a sensitive indicator of activity for the remaining chemicals with the exception of DDE, for which higher dose levels could have been used. However, none of the curtailed periods of exposure were able to detect all of the agents. Diethyl stilboestrol, and to a lesser extent DBP and DDE, delayed PPS when exposure occurred over the period pnd 22–55. A complex dependence of the day of PPS on the period of exposure and the body weight of the test animals was observed, and caution is recommended when assessing this endpoint in the presence of reductions in body weight. It is concluded that reproductive tissue weight changes in the peripubertal male have shown sensitivity to a range of biochemical modulators, oestrogens and anti‐androgens, and that as such the assay warrants further evaluation. Measurement of delays in PPS may be of value in cases of large delays, but delays of 1–2 days will be difficult to interpret with confidence. The present results are discussed within the context of the sexually mature male rat assay described by O’Connor and the castrated male rat assay described by Hershberger, both of which are the subject of current international study. It is concluded that a decision on the usefulness of the peripubertal male rat assay must await the generation of further data on each of these three assays. There is an urgent need for international agreement on a list of reference endocrine disrupters and their active dose levels, with which to validate individual endocrine disruption assays and batteries of assays. Copyright © 2000 John Wiley & Sons, Ltd.
A range of chemicals with various levels of activity as actual or potential endocrine disrupters have been evaluated for activity in the peripubertal male rat assay. The chemicals studied included anti-androgens (vinclozolin), cyproterone acetate, flutamide, 2, 2-bis(4-chlorophenyl)-1,1-dichloroethylene (DDE), metabolic modulators (anastrazole, finasteride, ketoconazole) and oestrogens (butyl benzyl phthalate (BBP), methoxychlor, bisphenol A (BPA), diethylstilboestrol (DES)), the suspected anti-androgen dibutyl phthalate (DBP) and the non-oestrogen fenitrothion. Dosing extended over postnatal days (pnd) 22-35, 36-50, 36-55 and 22-35, with recovery to pnd 55 or 22-55. The endpoints studied were changes in the weights of testes, epididymides, seminal vesicles and prostate. Changes in body weight and the weights of the liver and kidney were also monitored. In some experiments changes in the day of prepuce separation (PPS) were also determined. Only BBP and BPA were inactive in all the assays conducted. Changes in the weight of reproductive tissues provided a sensitive indicator of activity for the remaining chemicals with the exception of DDE, for which higher dose levels could have been used. However, none of the curtailed periods of exposure were able to detect all of the agents. Diethyl stilboestrol, and to a lesser extent DBP and DDE, delayed PPS when exposure occurred over the period pnd 22-55. A complex dependence of the day of PPS on the period of exposure and the body weight of the test animals was observed, and caution is recommended when assessing this endpoint in the presence of reductions in body weight. It is concluded that reproductive tissue weight changes in the peripubertal male have shown sensitivity to a range of biochemical modulators, oestrogens and anti-androgens, and that as such the assay warrants further evaluation. Measurement of delays in PPS may be of value in cases of large delays, but delays of 1-2 days will be difficult to interpret with confidence. The present results are discussed within the context of the sexually mature male rat assay described by O'Connor and the castrated male rat assay described by Hershberger, both of which are the subject of current international study. It is concluded that a decision on the usefulness of the peripubertal male rat assay must await the generation of further data on each of these three assays. There is an urgent need for international agreement on a list of reference endocrine disrupters and their active dose levels, with which to validate individual endocrine disruption assays and batteries of assays.
Author Ashby, J.
Lefevre, P. A.
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Issue 1
Keywords Drug
Mimetic hormone
Reproduction diseases
Rat
Toxicity
Acute
Chemical compound
Rodentia
Estrogen
Oral administration
Antiandrogen
Male
Endocrine disruptor
Antihormone
Vertebrata
Mammalia
Impuberal animal
Male genital diseases
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1986; 118
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1987; 187
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Nikoronow (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB26) 1973; 26
O'Connor (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB2) 1999; 51
Mylchreest (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB22) 1998; 43
vom Saal (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB28) 1998; 14
Ashby (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB6) 1987; 187
Bhasin (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB8) 1986; 118
Agarwal (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB16) 1986; 35
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Ashby (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB24) 1997; 26
Gray (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB10) 1989; 12
Oishi (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB17) 1980; 53
Monosson (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB5) 1999; 15
Nagel (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB27) 1997; 105
Cagen (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB29) 1999; 50
Cook (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB12) 1993; 119
Sharpe (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB23) 1995; 103
Hershberger (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB1) 1953; 83
Kelce (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB3) 1997; 75
(10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB14) 1982; 215
Wine (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB18) 1997; 105
Cater (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB25) 1977; 41
Ashby (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB4) 1997; 26
Peets (10.1002/(SICI)1099-1263(200001/02)20:1<35::AID-JAT633>3.0.CO;2-8-BIB11) 1974; 94
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Snippet A range of chemicals with various levels of activity as actual or potential endocrine disrupters have been evaluated for activity in the peripubertal male rat...
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SubjectTerms Androgen Antagonists - administration & dosage
Androgen Antagonists - analysis
Androgen Antagonists - pharmacology
androgens
Animals
Biological and medical sciences
Biological Assay
Body Weight - drug effects
Chemical and industrial products toxicology. Toxic occupational diseases
Dose-Response Relationship, Drug
endocrine disruption
Estrogens, Non-Steroidal - administration & dosage
Estrogens, Non-Steroidal - analysis
Estrogens, Non-Steroidal - pharmacology
Fenitrothion - pharmacology
Finasteride - pharmacology
Genitalia, Male - drug effects
Genitalia, Male - physiology
Humans
immature rats
Ketoconazole - pharmacology
Male
Medical sciences
Nitriles - pharmacology
oestrogens
Orchiectomy
Organ Size - drug effects
Puberty - physiology
Rats
sexual development
Sexual Maturation - drug effects
Toxicology
Triazoles - pharmacology
Various organic compounds
Title The peripubertal male rat assay as an alternative to the Hershberger castrated male rat assay for the detection of anti-androgens, oestrogens and metabolic modulators
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https://www.ncbi.nlm.nih.gov/pubmed/10641015
https://www.proquest.com/docview/70879656
Volume 20
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