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AOP: 305
Title
5α-reductase inhibition leading to short anogenital distance (AGD) in male (mammalian) offspring
Short name
Graphical Representation
Point of Contact
Contributors
- Terje Svingen
Coaches
- Judy Choi
- Shihori Tanabe
OECD Information Table
OECD Project # | OECD Status | Reviewer's Reports | Journal-format Article | OECD iLibrary Published Version |
---|---|---|---|---|
1.90 | Under Development |
This AOP was last modified on September 24, 2024 15:39
Revision dates for related pages
Page | Revision Date/Time |
---|---|
Inhibition, 5α-reductase | April 05, 2024 08:23 |
Decrease, dihydrotestosterone (DHT) level | April 05, 2024 08:10 |
Decrease, androgen receptor activation | April 05, 2024 08:19 |
anogenital distance (AGD), decreased | December 22, 2022 05:18 |
Altered, Transcription of genes by the androgen receptor | April 05, 2024 09:28 |
Inhibition, 5α-reductase leads to Decrease, DHT level | April 05, 2024 08:40 |
Decrease, AR activation leads to AGD, decreased | August 08, 2024 12:45 |
Decrease, DHT level leads to Decrease, AR activation | April 05, 2024 08:48 |
Altered, Transcription of genes by the AR leads to AGD, decreased | May 11, 2020 07:04 |
Decrease, AR activation leads to Altered, Transcription of genes by the AR | April 05, 2024 08:50 |
Finasteride | November 29, 2016 18:42 |
Abstract
This AOP links 5α-reductase inhibition during fetal life with short anogenital distance (AGD) in male offspring. A short AGD around birth is a marker for feminization of male fetuses and is associated with male reproductive disorders, including reduced fertility in adulthood (Schwartz et al 2019). Although a short AGD is not necessarily ‘adverse’ from a human health perspective, it is considered an ‘adverse outcome’ in OECD test guidelines; AGD measurements are mandatory in specific tests for developmental and reproductive toxicity in chemical risk assessment (TG 443, TG 421/422, TG 414), with measurement guidance provided in OECD guidance documents 43 (OECD, 2008) and 151 (OECD, 2013)
5α-reductase is an enzyme responsible for the conversion of testosterone to DHT in target tissues (Azzouni et al 2012; Davey and Grossmann, 2016). DHT is more potent agonist of the Androgen receptor (AR) than testosterone, so that DHT is necessary for proper masculinization of e.g. male external genitalia. Under normal physiological conditions, testosterone produced mainly by the testes, is converted in peripheral tissues by 5α-reductase into DHT, which in turn binds AR and activates downstream target genes (Davey and Grossmann, 2016). AR signaling is necessary for masculinization of the developing fetus, including differentiation of the levator ani/bulbocavernosus (LABC) muscle complex in males (Keller et al, 1996; Robitaille and Langlois, 2020). The LABC complex does not develop in the absence, or low levels of, androgen signaling, as in female fetuses.
A key step of this pathway is the inhibition of 5α-reductase, which converts testosterone into the more potent dihydrotestosterone (DHT) in androgen-sensitive tissues. In the developing perineal region, low or absent DHT levels result in inactivation of the androgen receptor (AR), leading to failure in proper masculinization of the perineum and the levator ani-bulbocavernosus (LABC) complex.
AOP Development Strategy
Context
Androgen signaling is critical for male sex differentiation during fetal life and suboptimal action during critical life stages leads to under-masculinized offspring. Testosterone is a main androgen, but during fetal differentiation, particularly in tissues distant to the testes, the more potent androgen receptor ligand dihydro-testosterone (DHT) is critical. The formation of DHT from testosterone requires the enzyme 5α-reductase, hence the role of both this enzyme and DHT must be considered when assessing overall effects of disrupted androgen signaling on sex differentiation.
Strategy
For the AOP network development, the OECD AOP Developer’s Handbook was followed alongside pragmatic approaches (Svingen et al., 2021). Key events (KEs) and key event relationships (KERs) based on canonical knowledge from the ‘upstream anti-androgenic network’ (Draskau et al., 2024) were treated less stringently, while new units adhered to more rigorous systematic literature retrieval methods.
KER-2820, linking KE-1614 (decreased AR activation) with AO-1688 (decreased AGD), was developed using a systematic weight of evidence (WoE) approach (Holmer et al., 2024). From an initial 826 publications, 557 were retained, with 71 selected for data extraction (82 datasets). Ultimately, 25 reliable datasets from in vivo studies on five model compounds (flutamide, procymidone, vinclozolin, finasteride, di-2-ethylhexyl phthalate) provided strong empirical support. Conversely, KER-2127, linking KE-286 (altered AR transcription) with AO-1688, was developed semi-systematically, yielding only two relevant studies due to limited transcriptional data from perineal tissue exposed to anti-androgenic chemicals.
The overall AOP assessments followed the AOP Developer’s Handbook guidelines.
Summary of the AOP
Events:
Molecular Initiating Events (MIE)
Key Events (KE)
Adverse Outcomes (AO)
Type | Event ID | Title | Short name |
---|
MIE | 1617 | Inhibition, 5α-reductase | Inhibition, 5α-reductase |
KE | 1613 | Decrease, dihydrotestosterone (DHT) level | Decrease, DHT level |
KE | 1614 | Decrease, androgen receptor activation | Decrease, AR activation |
KE | 286 | Altered, Transcription of genes by the androgen receptor | Altered, Transcription of genes by the AR |
AO | 1688 | anogenital distance (AGD), decreased | AGD, decreased |
Relationships Between Two Key Events (Including MIEs and AOs)
Title | Adjacency | Evidence | Quantitative Understanding |
---|
Decrease, AR activation leads to AGD, decreased | non-adjacent | ||
Altered, Transcription of genes by the AR leads to AGD, decreased | non-adjacent | Moderate |
Network View
Prototypical Stressors
Name |
---|
Finasteride |
Life Stage Applicability
Life stage | Evidence |
---|---|
Pregnancy | High |
Taxonomic Applicability
Sex Applicability
Sex | Evidence |
---|---|
Male | High |
Overall Assessment of the AOP
Domain of Applicability
The upstream part of the AOP, culminating at KE-286 (altered transcription of genes by the AR), has a broad applicability domain. It is built primarily on mammalian data and includes all life stages and both sexes. It could be extended to cover non-mammalian vertebrates by adding additional relevant knowledge, as previously discussed (Draskau et al, 2024). The overall applicability domain is limited by AO-1688 (decreased AGD). The AGD is strongly influenced by androgen action during critical fetal stages in mammals, with evidence from humans (Murashima et al, 2015; Thankamony et al, 2016), and from numerous gestational exposure studies in rats and mice to anti-androgenic chemicals (Gray et al, 2001; Schwartz et al, 2019a). The male masculinisation programming window occurs at a developmental stage included in the applicability domain of these AOPs and corresponds to around gestational day 16-20 in rats and gestation weeks 8-14 in humans (Welsh et al, 2008). Only males are included in the applicability domain since the male AGD, but not the female AGD, is shortened by decreased androgen action (Schwartz et al, 2019a).
Essentiality of the Key Events
The essentiality of each key event (KE) was evaluated, meaning that if an upstream KE is blocked or does not occur, subsequent downstream KEs or the adverse outcome (AO) are prevented or altered. Both direct and indirect evidence of essentiality were assessed according to the OECD developer’s handbook, with a summary provided in Table 1.
Table 1: Essentiality assessment of KEs of AOP 305-307.
Event |
Direct evidence |
Indirect evidence |
Contradictory evidence |
Overall essentiality assessment |
MIE-1617 |
* |
* |
|
Low |
KE-1613 |
|
** |
|
Intermediate |
KE-1614 |
*** |
*** |
|
High |
KE-286 |
|
*** |
|
High |
Evidence Assessment
Evidence for anti-androgenicity, by perturbing DHT signaling through the AR, is strong. In this AOP, most KERs are considered highly biologically plausible with strong empirical evidence in support of this assessment, both from human data and animal studies. The overall evidence assessment scores for each KER is summarized in the below Table:
ID |
Assessment score |
Rationale |
KER-1880 |
High |
It is well established that 5α-reductase converts testosterone to DHT and that decreased 5α-reductase activity leads to decreased DHT levels. |
KER-1935 |
High |
It is well established that DHT activates the AR and that decreased DHT levels leads to decreased AR activation. |
KER-2124 |
High |
It is well established that the AR regulates gene transcription, and that decreased AR activity leads to altered gene transcription. |
KER-2820 |
High |
It is well established that decreased AR activity leads to decreased AGD in male offspring. |
KER-2127 |
Moderate |
It is highly plausible that altered gene transcription in the perineum leads to decreased AGD in male offspring. |
Known Modulating Factors
Modulating Factor (MF) | Influence or Outcome | KER(s) involved |
---|---|---|
Age | Tissue-specific changes in AR expression with aging (Supakar et al., 1993; Wu et al., 2009) |
Identified in KER-1935 and KER-2124, but also relevant for KER-2127. |
Genotype | Decreased AR activation with increased number of CAG repeats in the first axon of the AR (Chamberlain et al., 1994; Tut et al., 1997). | Identified in KER-1935 and KER-2124, but also relevant for KER-2127. |
Androgen deficiency syndrome | Decreased AR activation with increased number of CAG repeats in the first axon of the AR (Chamberlain et al., 1994; Tut et al., 1997). | Identified in KER-1935 and KER-2124, but also relevant for KER-2127. |
Castration | Reduced level of circulating testosterone in affected individuals. | Identified in KER-1935. |
Quantitative Understanding
The quantitative understanding of the AOP is limited. A major challenge is that it is difficult to measure upstream and downstream events in the same study since MIE-26 and MIE-1617 are measured in vitro and KE-1614 focus on AR activation in vivo with no methods currently available to measure it.
Considerations for Potential Applications of the AOP (optional)
References
Azzouni F, Godoy A, Li Y, Mohler J (2012). The 5 alpha-reductase isozyme family: a review of basic biology and their role in human diseases. Adv Urol 2012:530121.
Bhasin S, Cunningham GR, Hayes FJ, Matsumoto AM, Snyder PJ, Swerdloff RS, Montori VM; Task Force, Endocrine Society (2010). Testosterone therapy in men with androgen deficiency syndromes: an Endocrine Society clinical practice guideline. J Clin Endocrinol Metab 95(6):2536-59.
Chamberlain NL, Driver ED, Miesfeld RL (1994). The length and location of CAG trinucleotide repeats in the androgen receptor N-terminal domain affect transactivation function. Nucleic Acids Res 22(15):3181-6.
Davey RA, Grossmann M (2016). Androgen Receptor Structure, Function and Biology: From Bench to Bedside. Clin Biochem Rev 37(1):3-15.
Draskau MK, Rosenmai AK, Bouftas N, Johansson HKL, Panagiotou EM, Holmer ML, Elmelund E, Zilliacus J, Beronius A, Damdimopolou P, van Duursen M, Svingen T (2024). AOP Report: An Upstream Network for Reduced Androgen Signaling Leading to Altered Gene Expression of Androgen Receptor-Responsive Genes in Target Tissues. Environ Toxicol Chem In Press (doi: 10.1002/etc.5972).
Gray LE, Ostby J, Furr J, Wolf CJ, Lambright C, Parks L, Veeramachaneni DN, Wilson V, Price M, Hotchkiss A, Orlando E, Guillette L (2001). Effects of environmental antiandrogens on reproductive development in experimental animals. Hum Reprod Update 7(3):248-64.
Holmer ML, Zilliacus J, Draskau MK, Hlisníková H, Beronius A, Svingen T (2024). Methodology for developing data-rich Key Event Relationships for Adverse Outcome Pathways exemplified by linking decreased androgen receptor activity with decreased anogenital distance. Reprod Toxicol 128:108662.
Keller ET, Ershler WB, Chang C (1996). The androgen receptor: a mediator of diverse responses. Front Biosci 1:d59-71.
Murashima A, Kishigami S, Thomson A, Yamada G (2015). Androgens and mammalian male reproductive tract development. Biochim Biophys Acta 1849(2):163-70.
OECD (2008), Guidance Document on Mammalian Reproductive Toxicity Testing and Assessment, OECD Series on Testing and Assessment, No. 43, OECD Publishing, Paris.
OECD (2013) Guidance document in support of the test guideline on the extended one generation reproductive toxicity study no. 151.
Robitaille J, Langlois VS (2020). Consequences of steroid-5α-reductase deficiency and inhibition in vertebrates. Gen Comp Endocrinol 290:113400.
Schwartz CL, Christiansen S, Vinggaard AM, Axelstad M, Hass U, Svingen T (2019). Anogenital distance as a toxicological or clinical marker for fetal androgen action and risk for reproductive disorders. Arch Toxicol 93(2):253-272.
Supakar PC, Song CS, Jung MH, Slomczynska MA, Kim JM, Vellanoweth RL, Chatterjee B, Roy AK (1993). A novel regulatory element associated with age-dependent expression of the rat androgen receptor gene. J Biol Chem 268(35):26400-8.
Svingen T, Villeneuve DL, Knapen D, Panagiotou EM, Draskau MK, Damdimopoulou P, O'Brien JM (2021). A Pragmatic Approach to Adverse Outcome Pathway Development and Evaluation. Toxicol Sci 184(2):183-190.
Thankamony A, Pasterski V, Ong KK, Acerini CL, Hughes IA (2016). Anogenital distance as a marker of androgen exposure in humans. Andrology 4(4):616-25.
Tut TG, Ghadessy FJ, Trifiro MA, Pinsky L, Yong EL (1997). Long polyglutamine tracts in the androgen receptor are associated with reduced trans-activation, impaired sperm production, and male infertility. J Clin Endocrinol Metab 82(11):3777-82.
Welsh M, Saunders PT, Fisken M, Scott HM, Hutchison GR, Smith LB, Sharpe RM (2008). Identification in rats of a programming window for reproductive tract masculinization, disruption of which leads to hypospadias and cryptorchidism. J Clin Invest 118(4):1479-90.
Wu D, Lin G, Gore AC (2009). Age-related changes in hypothalamic androgen receptor and estrogen receptor alpha in male rats. J Comp Neurol 512(5):688-701.