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AOP: 307
Title
Decreased testosterone synthesis 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 25, 2024 03:33
Revision dates for related pages
Page | Revision Date/Time |
---|---|
Decrease, circulating testosterone levels | December 12, 2024 05:27 |
Decrease, androgen receptor activation | April 05, 2024 08:19 |
Altered, Transcription of genes by the androgen receptor | April 05, 2024 09:28 |
anogenital distance (AGD), decreased | December 22, 2022 05:18 |
Decrease, circulating testosterone levels leads to Decrease, AR activation | April 05, 2024 09:18 |
Decrease, AR activation leads to AGD, decreased | August 08, 2024 12:45 |
Decrease, AR activation leads to Altered, Transcription of genes by the AR | April 05, 2024 08:50 |
Altered, Transcription of genes by the AR leads to AGD, decreased | May 11, 2020 07:04 |
Dibutyl phthalate | November 29, 2016 18:42 |
Bis(2-ethylhexyl) phthalate | November 29, 2016 18:42 |
Abstract
This AOP links decreased testosterone levels with short anogenital distance (AGD) in male offspring. It does not yet contain an MIE, as the upstream events leading to ‘reduced testosterone’ synthesis in fetal testis can be many, for example by inhibiting various enzymes of the steroidogenesis pathway. The precursor molecule cholesterol is converted to testosterone via several enzymatic steps and includes, for instance, the CYP enzymes CYP11 and CYP17. Following synthesis, testosterone is released into the circulation and transported to target tissues and organs where it initiates masculinization processes, typically by binding to and activating the androgen receptor (AR) in target cells. Notably, testosterone can be converted to DHT by 5α-reductase, with DHT being a more potent AR agonist than testosterone; this testosterone-to-DHT conversion is critical during development for differentiation of male traits, including masculinization of the developing fetus, including differentiation of the levator ani/bulbocavernosus (LABC) muscle complex (Davey and Grossmann, 2016; 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 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).
A central event in this pathway is inhibition of testosterone synthesis by fetal testes. In turn, this results in reduced circulating testosterone levels and less DHT (converted by 5α-reductase). Low DHT fails to properly activate AR in target tissues, including the developing perineal region, which leads to failure to properly masculinize the perineum/LABC complex and ultimately a short AGD.
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. Androgens, primarily testosterone and dihydro-testosterone (DHT), act by binding to and activating the AR is target cells. Blocking the AR basically blocks androgen signaling and masculinization of tissues and organs that otherwise should masculinize in male fetuses. One morphometric marker for reduced fetal androgen action is a shorter than normal anogenital distance.
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 |
---|
KE | 1690 | Decrease, circulating testosterone levels | Decrease, circulating testosterone levels |
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, circulating testosterone levels leads to Decrease, AR activation | adjacent | High | Moderate |
Decrease, AR activation leads to Altered, Transcription of genes by the AR | adjacent | Moderate | Low |
Decrease, AR activation leads to AGD, decreased | non-adjacent | High | Moderate |
Altered, Transcription of genes by the AR leads to AGD, decreased | non-adjacent | Moderate | Low |
Network View
Prototypical Stressors
Life Stage Applicability
Life stage | Evidence |
---|---|
Foetal | High |
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, 2019). 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, 2019).
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 307.
Event |
Direct evidence |
Indirect evidence |
Contradictory evidence |
Overall essentiality assessment |
KE-1690 |
|
*** |
|
High |
KE-1614 |
*** |
*** |
|
High |
KE-286 |
|
*** |
|
High |
*Low level of evidence (some support for essentiality), ** Intermediate level of evidence (evidence for impact on one or more downstream KEs), ***High level of evidence (evidence for impact on AO).
Evidence Assessment
Evidence for anti-androgenicity, by antagonizing 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 are summarized in the below Table:
ID |
Assessment score |
Rationale |
KER-2131 |
High |
It is well established that testosterone activates the AR and that decreased testosterone 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-2131 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-2131, KER-2124 and KER-2820. |
Androgen deficiency syndrome | Low level of circulating testosterone in affected individuals (Bhasin et al, 2010). | Identified in KER-2131. |
Castration | Reduced level of circulating testosterone in affected individuals. | Identified in KER-2131. |
Quantitative Understanding
The quantitative understanding between in vitro test data and in vivo is low. There is good quantitative understanding about the magnitude of reduction in explanted fetal testis testosterone production and effect on AGD (and other masculinization parameters) in rats, related to phthalate exposures. The dose-response relationship appears non-linear, with a low incidence rate of male under-virilization effects when testosterone production is reduced to around 46%, but with a steep increase in rate of malformations when testosterone is reduced by more than 75% (Earl Gray 2023; Earl Gray et al, 2024). This relationship has not been systematically evaluated for other chemicals.
Considerations for Potential Applications of the AOP (optional)
References
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).
Earl Gray L Jr (2023). Biologically relevant reductions in fetal testosterone and Insl3 induced by in utero exposure to high levels of di-isononyl phthalate (DINP) in male rats. Toxicol Appl Pharmacol 465:116454.
Earl Gray L Jr, Lambright CS, Evans N, Ford J, Conley JM (2024). Using targeted fetal rat testis genomic and endocrine alterations to predict the effects of a phthalate mixture on the male reproductive tract. Curr Res Toxicol. 7:100180. doi: 10.1016/j.crtox.2024.100180
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.