Relationship: 1880: Inhibition, 5α-reductase leads to Decrease, DHT level

AOPs Referencing Relationship

Evidence Supporting Applicability of this Relationship

This KE is applicable for both sexes, across developmental stages into adulthood, in numerous cells and tissues and across mammalian taxa. It is, however, acknowledged that this KER most likely has a much broader domain of applicability extending to non-mammalian vertebrates. AOP developers are encouraged to add additional relevant knowledge to expand on the applicability to also include other vertebrates.

Key Event Relationship Description

This key event relationship (KER) links inhibition of 5α-reductase activity to decreased dihydrotestosterone (DHT) levels.

There are three isozymes of 5α-reductase: type 1, 2, and 3. 5α-reductase type 2 is mainly involved in the synthesis of 5α-DHT from testosterone (T) (Robitaille & Langlois, 2020), although 5α-reductase type 1 can also facilitate this reaction, but with lower affinity for T (Nikolaou et al., 2021). The type 1 isoform is also involved in the alternative (‘backdoor’) pathway for DHT formation, facilitating the conversion of progesterone or 17OH-progesterone to dihydroprogesterone or 5α-pregnan-17α-ol-3,20-dione, respectively, whereafter several subsequent reactions will ultimately lead to the formation of DHT (Miller & Auchus, 2019). The quantitative importance of the alternative pathway remains unclear (Alemany, 2022). The type 1 and type 2 isoforms of 5α-reductase are the primary focus of this KER.

The direct conversion of T to 5α-DHT mainly takes place in the target tissue (Robitaille & Langlois, 2020). In mammals, the type 1 isoform is found in the scalp and other peripheral tissues (Miller & Auchus, 2011), such as liver, skin, prostate (Azzouni et al., 2012), bone, ovaries, and adipose tissue (Nikolaou et al., 2021). The type 2 isoform is expressed mainly in male reproductive tissues (Miller & Auchus, 2011), but also in liver, scalp and skin (Nikolaou et al., 2021). The expression level of both isoforms depend on the developmental stage and the tissue.

Evidence Supporting this KER

The biological plausibility of this KER is considered high.

5α-reductase can catalyze the conversion of T to DHT. The substrates for 5α-reductases are 3-oxo (3-keto), Δ^4,5 C19/C21 steroids such as testosterone and progesterone. The enzymatic reaction leads to an irreversible breakage of the double bond between carbon 4 and 5 and subsequent insertion of a hydride anion at carbon 5 and insertion of a proton at carbon 4. The reaction is aided by the cofactor NADPH (Azzouni et al., 2012). By inhibiting this enzyme, the described catalyzed reaction will be inhibited leading to a decrease in DHT levels.

In both humans and rodents, DHT is important for the in utero differentiation and growth of the prostate and male external genitalia. Besides its critical role during fetal development, DHT also induces growth of facial and body hair during puberty in humans (Azzouni et al., 2012).

The empirical evidence for this KER is considered high

Dose concordance

Several inhibitors of 5α-reductases have been developed for pharmacological uses. Inhibition of the enzymatic conversion of radiolabeled substrate has been illustrated (Table 1) and data display dose-concordance, with increasing concentrations of inhibitor leading to lower 5α-reductase product formation. These studies at large rely on conversion of radiolabeled substrate and hence serve as an indirect measurement.

Table 1: Dose concordance from selected in vitro test systems

 These in vitro studies clearly show effects on the enzymatic reaction induced by 5α-reductases in a concentration dependent manner (Andersson & Russell, 1990; Thigpens et al., 1993; Yamana et al., 2010).

In the intact organism, when 5α-reductase type 2 activity is lacking through e.g. inhibitor treatment or knockout, this will results in decreased 5α-DHT locally in the tissues, but also in blood (Robitaille & Langlois, 2020). This has been demonstrated in humans, rats, monkeys, and mice  (Robitaille et al. 2020).

Finasteride is a specific inhibitor of 5α-reductase type 2 (Russell & Wilson, 1994). Men with androgenic alopecia were treated with increasing concentrations of finasteride and presented with decreased DHT levels in biopsies from scalp, as well as a decrease in serum DHT levels with dose dependency being most apparent in serum, up to about 70% decrease (Drake et al., 1999). Likewise, men treated with dutasteride exhibited a clear dose dependent decrease in serum DHT after 24 weeks treatment with a maximum efficacy of about 98% (Clark et al., 2004).

Other evidence

The phenotype of males with deficiency in 5α-reductases are typically born with ambiguous external genitalia. They also present with small prostate, minimal facial hair and acne, or temporal hair loss. Comparison of affected individuals to non-affected individuals in regard to T/DHT ratio, conversion of infused radioactive T, and ratios of urinary metabolites of 5α-reductase and 5β-reductase concluded that these phenotypic characteristics were due to 5α-reductase defects that resulted in less conversion of T to DHT (Okeigwe et al. 2014). Mutations in the 5α-reductase gene can result in boys being born with moderate to severe undervirilization phenotypes (Elzenaty 2022).

Quantitative Understanding of the Linkage

Inhibitors of 5α-reductase are important for the prevention and treatment of many diseases. There are several compounds that have been developed for pharmaceutical purposes and they can target the different isoforms with different affinity. Examples of inhibitors are finasteride and dutasteride. Finasteride mainly has specificity for the type 2 isoform, whereas dutasteride inhibits both type 1 and 2 isoforms (Miller & Auchus, 2011).

These differences in isoform specificity reflects in the effects on DHT serum levels, hence the broader specificity of dutasteride leads to > 90% decrease in patients with benign prostatic hyperplasia, in comparison to 70% with finasteride administration (Nikolaou et al., 2021).

Enzyme inhibition can occur in different ways e.g. both competitive and noncompetitive. The inhibition model depends on the specific inhibitor and hence a generic quantitative response-response relationship is difficult to derive.

An inhibition of 5α-reductases would lead to an immediate change in DHT levels at the molecular level. However, the time-scale for systemic effects on hormone levels are challenging to estimate.

Androgens can regulate gene expression of 5α-reductases (Andersson et al., 1989; Berman & Russell, 1993).

References

Alemany, M. (2022). The Roles of Androgens in Humans: Biology, Metabolic Regulation and Health. In International Journal of Molecular Sciences (Vol. 23, Issue 19). MDPI. https://doi.org/10.3390/ijms231911952

Andersson, S., Bishop, R. W., & Russell$, D. W. (1989). THE JOURNAL OF BIOLOGICAL CHEMISTRY Expression Cloning and Regulation of Steroid 5cw-Reductase, an Enzyme Essential for Male Sexual Differentiation* (Vol. 264, Issue 27).

Andersson, S., & Russell, D. W. (1990). Structural and biochemical properties of cloned and expressed human and rat steroid 5a-reductases. Proc. Natl. Acad. Sci. USA, 87, 3640–3644. https://www.pnas.org

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. In Advances in Urology. https://doi.org/10.1155/2012/530121

Berman, D. M., & Russell, D. W. (1993). Cell-type-specific expression of rat steroid 5a-reductase isozymes (sexual development/androgens/prostate/stroma/epithelium). In Proc. Natl. Acad. Sci. USA (Vol. 90). https://www.pnas.org

Clark, R. V., Hermann, D. J., Cunningham, G. R., Wilson, T. H., Morrill, B. B., & Hobbs, S. (2004). Marked Suppression of Dihydrotestosterone in Men with Benign Prostatic Hyperplasia by Dutasteride, a Dual 5α-Reductase Inhibitor. Journal of Clinical Endocrinology and Metabolism, 89(5), 2179–2184. https://doi.org/10.1210/jc.2003-030330

Drake, L., Hordinsky, M., Fiedler, V., Swinehart, J., Unger, W. P., Cotterill, P. C., Thiboutot, D. M., Lowe, N., Jacobson, C., Whiting, D., Stieglitz, S., Kraus, S. J., Griffin, E. I., Weiss, D., Carrington, P., Gencheff, C., Cole, G. W., Pariser, D. M., Epstein, E. S., … City, O. (1999). The effects of finasteride on scalp skin and serum androgen levels in men with androgenetic alopecia.

Miller, W. L., & Auchus, R. J. (2011). The molecular biology, biochemistry, and physiology of human steroidogenesis and its disorders. Endocrine Reviews, 32(1), 81–151. https://doi.org/10.1210/er.2010-0013

Miller, W. L., & Auchus, R. J. (2019). The “backdoor pathway” of androgen synthesis in human male sexual development. PLoS Biology, 17(4). https://doi.org/10.1371/journal.pbio.3000198

Nikolaou, N., Hodson, L., & Tomlinson, J. W. (2021). The role of 5-reduction in physiology and metabolic disease: evidence from cellular, pre-clinical and human studies. In Journal of Steroid Biochemistry and Molecular Biology (Vol. 207). Elsevier Ltd. https://doi.org/10.1016/j.jsbmb.2021.105808

Peng, H. M., Valentin-Goyco, J., Im, S. C., Han, B., Liu, J., Qiao, J., & Auchus, R. J. (2020). Expression in escherichia coli, purification, and functional reconstitution of human steroid 5α-reductases. Endocrinology (United States), 161(8), 1–11. https://doi.org/10.1210/ENDOCR/BQAA117

Robitaille, J., & Langlois, V. S. (2020). Consequences of steroid-5α-reductase deficiency and inhibition in vertebrates. In General and Comparative Endocrinology (Vol. 290). Academic Press Inc. https://doi.org/10.1016/j.ygcen.2020.113400

Russell, D. W., & Wilson, J. D. (1994). STEROID Sa-REDUCTASE: TWO GENES/TWO ENZYMES. www.annualreviews.org

Thigpens, A. E., Cala, K. M., & Russell, D. W. (1993). Characterization of Chinese Hamster Ovary Cell Lines Expressing Human Steroid 5a-Reductase Isozymes. The Journal of Biological Chemistry, 268(23), 17404–17412.

Yamana, K., Fernand, L., Luu-The, V., & Luu-The, V. (2010). Human type 3 5α-reductase is expressed in peripheral tissues at higher levels than types 1 and 2 and its activity is potently inhibited by finasteride and dutasteride. Hormone Molecular Biology and Clinical Investigation, 2(3), 293–299. https://doi.org/10.1515/HMBCI.2010.035

Relationship: 1935: Decrease, DHT level leads to Decrease, AR activation

AOPs Referencing Relationship

Evidence Supporting Applicability of this Relationship

Taxonomic applicability

KER1935 is assessed applicable to mammals, as DHT and AR activation are known to be related in mammals. It is, however, acknowledged that this KER most likely has a much broader domain of applicability extending to non-mammalian vertebrates. AOP developers are encouraged to add additional relevant knowledge to expand on the applicability to also include other vertebrates.

Sex applicability

KER1935 is assessed applicable to both sexes, as DHT activates AR in both males and females.

Life-stage applicability

KER1935 is considered applicable to developmental and adult life stages, as DHT-mediated AR activation is relevant from the AR is expressed.

Key Event Relationship Description

Dihydrotestosterone (DHT) is a primary ligand for the Androgen receptor (AR), a nuclear receptor and transcription factor. DHT is an endogenous sex hormone that is synthesized from e.g. testosterone by the enzyme 5α-reductase in different tissues and organs (Davey & Grossmann, 2016; Marks, 2004). In the absence of ligand (e.g. DHT) the AR is localized in the cytoplasm in complex with molecular chaperones. Upon ligand binding, AR is activated, translocated into the nucleus, and dimerizes to carry out its ‘genomic function’ (Davey & Grossmann, 2016). Hence, AR transcriptional function is directly dependent on the presence of ligands, with DHT being a more potent AR activator than testosterone (Grino et al, 1990). Reduced levels of DHT may thus lead to reduced AR activation. Besides its genomic actions, the AR can also mediate rapid, non-genomic second messenger signaling (Davey and Grossmann, 2016). Decreased DHT levels that lead to reduced AR activation can thus entail downstream effects on both genomic and non-genomic signaling.

Evidence Supporting this KER

The biological plausibility of KER1935 is considered high.

The activation of AR is dependent on binding of ligands (though a few cases of ligand-independent AR activation has been shown, see uncertainties and inconsistencies), primarily testosterone and DHT in mammals (Davey and Grossmann, 2016; Schuppe et al., 2020). Without ligand activation, the AR will remain in the cytoplasm associated with heat-shock and other chaperones and not be able to carry out its canonical (‘genomic’) function. Upon androgen binding, the AR undergoes a conformational change, chaperones dissociate, and a nuclear localization signal is exposed. The androgen/AR complex can now translocate to the nucleus, dimerize and bind AR response elements to regulate target gene expression (Davey and Grossmann, 2016; Eder et al., 2001). AR transcriptional activity and specificity is regulated by co-activators and co-repressors in a cell-specific manner (Heinlein and Chang, 2002).

The requirement for androgens binding to the AR for transcriptional activity has been extensively studied and proven and is generally considered textbook knowledge. The OECD test guideline no. 458 uses DHT as the reference chemical for testing androgen receptor activation in vitro (OECD, 2020). In the absence of DHT during development caused by 5α-reductase deficiency (i.e. still in the presence of testosterone) male fetuses fail to masculinize properly. This is evidenced by, for instance, individuals with congenital 5α-reductase deficiency conditions (Costa et al., 2012); conditions not limited to humans (Robitaille and Langlois, 2020), testifying to the importance of specifically DHT for AR activation and subsequent masculinization of certain reproductive tissues.

Binding of testosterone or DHT has differential effects in different tissues. E.g. in the developing mammalian male; testosterone is required for development of the internal sex organs (epididymis, vas deferens and the seminal vesicles), whereas DHT is crucial for development of the external sex organs (Keller et al., 1996; Robitaille and Langlois, 2020).

The empirical support for KER1935 is considered high.

Dose concordance:

• Increasing concentrations of DHT lead to increasing AR activation in vitro in AR reporter gene assays (OECD, 2020; Williams et al., 2017).

Indirect (supporting) evidence:

• In cell lines where proliferation can be induced by androgens (such as prostate cancer cells) proliferation can be used as a readout for AR-activation. Finasteride, a 5α-reductase inhibitor, dose-dependently decreases AR-mediated prostate cancer cell line proliferation (Bologna et al., 1995). 0.001 µM finasteride decreased the growth rate with 44%, 0.1 µM decreased the growth rate with 80%.
• Specific events of masculinization during development are dependent on AR activation by DHT, including the development and length of the perineum which can be measured as the anogenital distance (AGD, (Schwartz et al., 2019)). E.g. a dose-dependent effect of rat in utero exposure to the 5α-reductase inhibitor finasteride was observed on the length of the AGD, where 0.01 mg/kg bw/day finasteride reduced the AGD measured at pup day 1 by 8%, whereas 1 mg/kg bw/day reduced the AGD by 23% (Bowman et al., 2003).

Other evidence:

• Male individuals with congenital 5α-reductase deficiency (absence of DHT) fail to masculinize properly (Costa et al., 2012).
• A major driver of prostate cancer growth is AR activation (Davey and Grossmann, 2016; Huggins and Hodges, 1941). Androgen deprivation is used as treatment including 5α-reductase inhibitors to reduce DHT levels (Aggarwal et al., 2010).

Ligand-independent actions of the AR have been identified. To what extent and of which biological consequences is not well defined (Bennesch and Picard, 2015).

It should be noted, that in tissues, that are not DHT-dependent but rather respond to T, a decrease in DHT level may not influence AR activation significantly in that specific tissue.

Quantitative Understanding of the Linkage

There is a positive dose-response relationship between increasing concentrations of DHT and AR activation (Dalton et al., 1998; OECD, 2020). However, there is not enough data, or overview of the data, to define a quantitative linkage in vivo, and such a relationship will differ between biological systems (species, tissue, cell type).

Upon DHT binding to the AR, a conformational change that brings the amino (N) and carboxy (C) termini into close proximity occurs with a t_1/2 of approximately 3.5 minutes, around 6 minutes later the AR dimerizes as shown in transfected HeLa cells (Schaufele et al., 2005). Addition of 5 nM DHT to the culture medium of ‘AR-resistant’ transfected prostatic cancer cells resulted in a rapid (from 15 minutes, maximal at 30 minutes) nuclear translocation of the AR with minimal residual cytosolic expression (Nightingale et al., 2003). AR and promoter interactions occur within 15 minutes of ligand binding, and RNA polymerase II and coactivator recruitment are then proposed to occur transiently with cycles of approximately 90 minutes (Kang et al., 2002).

Androgens have been shown to upregulate and downregulate AR expression as well as 5α-reductase expression, but for 5α-reductase, each isoform in each tissue is differently regulated by androgens and can display sexual dimorphism (Lee and Chang, 2003; Robitaille and Langlois, 2020). The quantitative impact of such adaptive expression changes is unknown.

References

Aggarwal, S., Thareja, S., Verma, A., Bhardwaj, T.R., Kumar, M., 2010. An overview on 5α-reductase inhibitors. Steroids 75, 109–153. https://doi.org/10.1016/j.steroids.2009.10.005

Bennesch, M.A., Picard, D., 2015. Minireview: Tipping the Balance: Ligand-Independent Activation of Steroid Receptors. Mol. Endocrinol. 29, 349–363. https://doi.org/10.1210/ME.2014-1315

Bhasin, S., Cunningham, G.R., Hayes, F.J., Matsumoto, A.M., Snyder, P.J., Swerdloff, R.S., Montori, V.M., 2010. Testosterone Therapy in Men with Androgen Deficiency Syndromes: An Endocrine Society Clinical Practice Guideline. J. Clin. Endocrinol. Metab. 95, 2536–2559. https://doi.org/10.1210/JC.2009-2354

Bologna, M., Muzi, P., Biordi, L., Festuccia, C., Vicentini, C., 1995. Finasteride dose-dependently reduces the proliferation rate of the LnCap human prostatic cancer cell line in vitro. Urology 45, 282–290. https://doi.org/10.1016/0090-4295(95)80019-0

Bowman, C.J., Barlow, N.J., Turner, K.J., Wallace, D.G., Foster, P.M.D., 2003. Effects of in Utero Exposure to Finasteride on Androgen-Dependent Reproductive Development in the Male Rat. Toxicol. Sci. 74, 393–406. https://doi.org/10.1093/TOXSCI/KFG128

Chamberlain, N.L., Driver, E.D., Miesfeld, R.L., 1994. The length and location of CAG trinucleotide repeats in the androgen receptor N-terminal domain affect transactivation function. Nucleic Acids Res. 22, 3181. https://doi.org/10.1093/NAR/22.15.3181

Costa, E.F., Domenice, S., Sircili, M., Inacio, M., Mendonca, B., 2012. DSD due to 5α-reductase 2 deficiency - From diagnosis to long term outcome. Semin. Reprod. Med. 30, 427–431. https://doi.org/10.1055/S-0032-1324727/ID/JR00766-20/BIB

Dalton, J.T., Mukherjee, A., Zhu, Z., Kirkovsky, L., Miller, D.D., 1998. Discovery of nonsteroidal androgens. Biochem. Biophys. Res. Commun. 244, 1–4. https://doi.org/10.1006/bbrc.1998.8209

Davey, R.A., Grossmann, M., 2016. Androgen Receptor Structure, Function and Biology: From Bench to Bedside. Clin. Biochem. Rev. 37, 3–15.

Eder, I.E., Culig, Z., Putz, T., Nessler-Menardi, C., Bartsch, G., Klocker, H., 2001. Molecular Biology of the Androgen Receptor: From Molecular Understanding to the Clinic. Eur. Urol. 40, 241–251. https://doi.org/10.1159/000049782

Grino, P.B., Griffin, J.E., Wilson, J.D., 1990. Testosterone at High Concentrations Interacts with the Human Androgen Receptor Similarly to Dihydrotestosterone. Endocrinology 126, 1165–1172. https://doi.org/10.1210/endo-126-2-1165

Heinlein, C.A., Chang, C., 2002. Androgen Receptor (AR) Coregulators: An Overview. Endocr. Rev. 23, 175–200. https://doi.org/10.1210/EDRV.23.2.0460

Huggins, C., Hodges, C. V., 1941. Studies on prostatic cancer: I. The effect of castration, of estrogen and of androgen injection on serum phosphatases in metastatic carcinoma of the prostate. Cancer Res. 1, 293–297.

Kang, Z., Pirskanen, A., Jänne, O.A., Palvimo, J.J., 2002. Involvement of proteasome in the dynamic assembly of the androgen receptor transcription complex. J. Biol. Chem. 277, 48366–48371. https://doi.org/10.1074/jbc.M209074200

Keller, E.T., Ershler, W.B., Chang, C., 1996. The androgen receptor: a mediator of diverse responses. Front. Biosci. (Landmark Ed) 1, 59–71. https://doi.org/10.2741/A116

Krotkiewski, M., Kral, J.G., Karlsson, J., 1980. Effects of castration and testosterone substitution on body composition and muscle metabolism in rats. Acta Physiol. Scand. 109, 233–237. https://doi.org/10.1111/J.1748-1716.1980.TB06592.X

Lee, D.K., Chang, C., 2003. Expression and Degradation of Androgen Receptor: Mechanism and Clinical Implication. J. Clin. Endocrinol. Metab. 88, 4043–4054. https://doi.org/10.1210/JC.2003-030261

Marks, L.S., 2004. 5Alpha-Reductase: History and Clinical Importance. Rev. Urol. 6 Suppl 9, S11-21.

Nightingale, J., Chaudhary, K.S., Abel, P.D., Stubbs, A.P., Romanska, H.M., Mitchell, S.E., Stamp, G.W.H., Lalani, E.N., 2003. Ligand Activation of the Androgen Receptor Downregulates E-Cadherin-Mediated Cell Adhesion and Promotes Apoptosis of Prostatic Cancer Cells. Neoplasia 5, 347. https://doi.org/10.1016/S1476-5586(03)80028-3

OECD, 2020. Test No. 458: Stably Transfected Human Androgen Receptor Transcriptional Activation Assay for Detection of Androgenic Agonist and Antagonist Activity of Chemicals, OECD Guidelines for the Testing of Chemicals, Section 4. OECD Publishing, Paris. https://doi.org/10.1787/9789264264366-en

Robitaille, J., Langlois, V.S., 2020. Consequences of steroid-5α-reductase deficiency and inhibition in vertebrates. Gen. Comp. Endocrinol. 290. https://doi.org/10.1016/j.ygcen.2020.113400

Schaufele, F., Carbonell, X., Guerbadot, M., Borngraeber, S., Chapman, M.S., Ma, A.A.K., Miner, J.N., Diamond, M.I., 2005. The structural basis of androgen receptor activation: Intramolecular and intermolecular amino-carboxy interactions. Proc. Natl. Acad. Sci. U. S. A. 102, 9802–9807. https://doi.org/10.1073/pnas.0408819102

Schuppe, E.R., Miles, M.C., Fuxjager, M.J., 2020. Evolution of the androgen receptor: Perspectives from human health to dancing birds. Mol. Cell. Endocrinol. 499, 110577. https://doi.org/10.1016/J.MCE.2019.110577

Schwartz, C.L., Christiansen, S., Vinggaard, A.M., 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, 253–272. https://doi.org/10.1007/s00204-018-2350-5

Supakar, P.C., Song, C.S., Jung, M.H., Slomczynska, M.A., Kim, J.M., Vellanoweth, R.L., Chatterjee, B., Roy, A.K., 1993. A novel regulatory element associated with age-dependent expression of the rat androgen receptor gene. J. Biol. Chem. 268, 26400–26408. https://doi.org/10.1016/S0021-9258(19)74328-2

Tut, T.G., Ghadessy, F.J., Trifiro, M.A., Pinsky, L., Yong, E.L., 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, 3777–3782. https://doi.org/10.1210/JCEM.82.11.4385

Williams, A.J., Grulke, C.M., Edwards, J., McEachran, A.D., Mansouri, K., Baker, N.C., Patlewicz, G., Shah, I., Wambaugh, J.F., Judson, R.S., Richard, A.M., 2017. The CompTox Chemistry Dashboard: a community data resource for environmental chemistry. J. Cheminform. 9, 61. https://doi.org/10.1186/s13321-017-0247-6

Wu, D., Lin, G., Gore, A.C., 2009. Age-related Changes in Hypothalamic Androgen Receptor and Estrogen Receptor α in Male Rats. J. Comp. Neurol. 512, 688. https://doi.org/10.1002/CNE.21925

Relationship: 2124: Decrease, AR activation leads to Altered, Transcription of genes by the AR

AOPs Referencing Relationship

Evidence Supporting Applicability of this Relationship

This KER is applicable for both sexes, across developmental stages into adulthood, in numerous cells and tissues and across mammalian taxa. It is, however, acknowledged that this KER most likely has a much broader domain of applicability extending to non-mammalian vertebrates. AOP developers are encouraged to add additional relevant knowledge to expand on the applicability to also include other vertebrates.

Key Event Relationship Description

The androgen receptor (AR) is a ligand-dependent nuclear transcription factor that upon activation translocates to the nucleus, dimerizes, and binds androgen response elements (AREs) to modulate transcription of target genes (Lamont and Tindall, 2010, Roy et al. 2001). Decreased activation of the AR affects its transcription factor activity, therefore leading to altered AR-target gene expression. This KER refers to decreased AR activation and altered gene expression occurring in complex systems, such as in vivo and the specific effect on transcription of AR target genes will depend on species, life stage, tissue, cell type etc.

Evidence Supporting this KER

The biological plausibility for this KER is considered high

The AR is a ligand-activated transcription factor part of the steroid hormone nuclear receptor family. Non-activated AR is found in the cytoplasm as a multiprotein complex with heat-shock proteins, immunophilins and, other chaperones (Roy et al. 2001). Upon activation through ligand binding, the AR dissociates from the protein complex, translocates to the nucleus and homodimerizes. Facilitated by co-regulators, AR can bind to DNA regions containing AREs and initiate transcription of target genes, that thus will be different in e.g. different tissues, life-stages, species etc.

Through mapping of AREs and ChIP sequencing studies, several AR target genes have been identified, mainly studied in prostate cells (Jin, Kim, and Yu 2013). Different co-regulators and ligands lead to altered expression of different sets of genes (Jin et al. 2013; Kanno et al. 2022). Alternative splicing of the AR can lead to different AR variants that also affects which genes are transcribed (Jin et al. 2013).

Apart from this canonical signaling pathway, the AR can suppress gene expression, indirectly regulate miRNA transcription, and have non-genomic effects by rapid activation of second messenger pathways in either presence or absence of a ligand (Jin et al. 2013).

The empirical evidence for this KER is considered high

In humans, altered gene expression profiling in individuals with androgen insensitivity syndrome (AIS) can provide supporting empirical evidence (Holterhus et al. 2003; Peng et al. 2021). In rodent AR knockout (KO) models, gene expression profiling studies and gene-targeted approaches have provided information on differentially expressed genes in several organ systems including male and female reproductive, endocrine, muscular, cardiovascular and nervous systems (Denolet et al. 2006; Fan et al. 2005; Holterhus et al. 2003; Ikeda et al. 2005; Karlsson et al. 2016; MacLean et al. 2008; Rana et al. 2011; Russell et al. 2012; Shiina et al. 2006; Wang et al. 2006; Welsh et al. 2012; Willems et al. 2010; Yu et al. 2008, 2012; Zhang et al. 2006; Zhou et al. 2011).

Exposure to known antiandrogens has been shown to alter transcriptional profiles, for example of neonatal pig ovaries (Knapczyk-Stwora et al. 2019).

Dose concordance has also been observed for instance in zebrafish embryos; a dose of 50 µg/L of the AR antagonist flutamide resulted in 674 differentially expressed genes at 96 h post fertilization whereas 500 µg/L flutamide resulted in 2871 differentially expressed genes (Ayobahan et al., 2023).

AR action has been reported to occur also without ligand binding. However, not much is known about the extent and biological implications of such non-canonical, ligand-independent AR activation (Bennesch and Picard 2015).

Quantitative Understanding of the Linkage

There is not enough data to define a quantitative relationship between AR activation and alteration of AR target gene transcription, and such a relationship will differ between biological systems (species, tissue, cell type, life stage etc).

AR and promoter interactions occur within 15 minutes of ligand binding, RNA polymerase II and coactivator recruitment are proposed to occur transiently with cycles of approximately 90 minutes in LNCaP cells (Kang et al. 2002). RNA polymerase II elongation rates in mammalian cells have been shown to range between 1.3 and 4.3 kb/min (Maiuri et al. 2011). Therefore, depending on the cell type and the half-life of the AR target gene transcripts, changes are to be expected within hours.

AR has been hypothesized to auto-regulate its mRNA and protein levels (Mora and Mahesh 1999).

References

Ayobahan, S. U., Alvincz, J., Reinwald, H., Strompen, J., Salinas, G., Schäfers, C., et al. (2023). Comprehensive identification of gene expression fingerprints and biomarkers of sexual endocrine disruption in zebrafish embryo. Ecotoxicol. Environ. Saf. 250, 114514. doi:10.1016/J.ECOENV.2023.114514.

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Relationship: 2828: Decrease, AR activation leads to Hypospadias

AOPs Referencing Relationship

Evidence Supporting Applicability of this Relationship

Taxonomic applicability

In mammals, androgens are one of the primary drivers of penis differentiation. Hypospadias has been observed in several mammals, but most frequently reported in laboratory rodents and in humans (Chang et al., 2020; S. Wang & Zheng, 2025). In vivo studies in rats and mice show that in utero exposure to anti-androgenic chemicals can cause hypospadias in male offspring (see table 3). Many human case studies report boys born with hypospadias and associated deficiency in steroid hormone synthesis, 5α-reductase activity, or androgen receptor (AR) activity (see table 4).

The biologically plausible domain of applicability may extend beyond the empirical domain because androgen-controlled development of male external genitalia is evolutionary conserved in most mammals and, to some extent, also in other vertebrate classes (Gredler et al., 2014). Hypospadias can in principle occur in all animals that form a genital tubercle and have been observed in many domestic animal species including dog (Sonne et al., 2008; Switonski et al., 2018), cat (Nowacka-Woszuk et al., 2014), cattle (Murakami, 2008), sheep (Smith et al., 2012), and horse (De Lorenzi et al., 2010) as well as in wildlife species such as polar bear (Stamper et al., 1999), giraffe (Meuffels et al., 2020), and Tamar Wallaby (Leihy et al., 2011). The observed hypospadias in these animals is not, per se, linked to anti-androgenic exposure, which has only been sparsely investigated in other species than mice, rats, and humans. One study in monkeys did show hypospadias upon oral exposure to finasteride (Prahalada et al., 1997), and bicalutamide exposure induced hypospadias in guinea pigs (S. Wang et al., 2018). A study in rabbits exposed to procymidone did not find hypospadias in males (Inawaka et al., 2010). Another study in hyenas did also not find hypospadias in males after exposure to the anti-androgen finasteride (Drea et al., 1998), but it should be noted that the hyenas have a remarkable sexual development where penile growth occur in both females and males before androgen synthesis is initiated (Cunha et al., 2014) (the studies in hyena and rabbit were identified in our evidence collection but were judged as ‘unreliable’ and therefore not included as empirical evidence).

Sex applicability

The androgen receptor is expressed in the fetal genital tubercle of both females and males (Amato & Yao, 2021; Baskin et al., 2020), but hypospadias is primarily a term used for a malformation of the penis (Baskin & Ebbers, 2006), limiting the applicability of this KER to males.

Life stage applicability

Differentiation of the penis occurs during fetal life in the masculinization programming window (MPW) (GD 16-20 in rats, around gestational weeks 8-14 in humans), when androgen production is high (Welsh et al., 2008; C. Wolf et al., 2000a). In rats, exposure to anti-androgenic chemicals outside of, or in the late part of the MPW does not cause hypospadias or only to a low degree (Clark et al., 1993; van den Driesche et al., 2017; C. Wolf et al., 2000a), while exposure in the earlier (or full) MPW causes a higher frequency of hypospadias (depending on dose and chemical) (table 3). In humans, hypospadias can be diagnosed at birth (X. Yu et al., 2019), while in rodents, some parts of penis development occur postnatally (Schlomer et al., 2013; Sinclair et al., 2017). In these species, hypospadias may be observed at birth but is optimally diagnosed and severity classified weeks later. Given that disruptions to androgen programming takes place in fetal life, even though the AO is best detected postnatally, the life stage applicability is defined as fetal life.

Key Event Relationship Description

This non-adjacent KER describes a fetal decrease in androgen receptor (AR) activation in the genital tubercle causing hypospadias in male offspring, postnatally. During fetal development, androgens induce differentiation of the bipotential genital tubercle to a penis, including closure of the urethra. Androgens signal through AR and reduced fetal AR activation can therefore disrupt penis differentiation and lead to the genital malformation hypospadias. Reduced AR activation may happen both through reduced ligand availability (testosterone or dihydrotestosterone (DHT)) and by direct antagonism of AR (Amato et al., 2022; Mattiske & Pask, 2021).

The upstream KE ‘decrease, androgen receptor activation’ (KE 1614) refers to the in vivo event of overall reduction in AR activation. In this case, it therefore refers to a reduction in AR activation in the genital tubercle. Currently, decreased AR activation in mammals is only directly measured in vitro and not in vivo. Instead, indirect assessment of this KE may come from assays measuring AR antagonism, 5α-reductase activity (the enzyme converting testosterone to DHT), or decreased androgen levels (Draskau et al., 2024).

Evidence Supporting this KER

The biological plausibility for this KER is judged as high. This is largely based on canonical knowledge on normal reproductive development.

The penis originates from a sexually bipotential structure, the genital tubercle, which may differentiate to either a penis or a clitoris, depending on internal cues during fetal development. In males, the fetal testes produce large amounts of testosterone, which can subsequently be converted to the more potent androgen DHT by 5α-reductase in peripheral tissues. Testosterone and DHT both signal through AR in target tissues to initiate masculinization (Amato et al., 2022; Murashima et al., 2015). The critical developmental window for androgen programming of masculinization has been identified in rats as GD16-20, and is proposed to be gestational weeks 8-14 in humans (Sharpe, 2020; Welsh et al., 2008). As part of the masculinization process orchestrated by androgens, the genital tubercle differentiates to a penis, which at this point expresses AR in both humans and rodents (Amato & Yao, 2021; Baskin et al., 2020). This includes androgen-mediated elongation of the tubercle, formation of the prepuce, and tubular internalization of urethra, which is closed at the distal tip of the glans penis (Amato et al., 2022). Failure of full closure of the urethra can result in hypospadias, in which the urethra terminates at the ventral side of the penis instead of at the tip (Baskin & Ebbers, 2006; Cohn, 2011).

The dependency of androgens for penile development has been demonstrated in mice with conditional or full knockout of Ar, which results in partly or full sex-reversal of males, including a female-like urethral opening (Willingham et al., 2006; Yucel et al., 2004; Zheng et al., 2015). Similarly, female rats and mice exposed in utero to testosterone present with varying degrees of intersexuality, including, in some cases, a penis (Greene & Ivy, 1937; Zheng et al., 2015).

The empirical evidence for this KER is generally judged high. This includes evidence from in vivo animal studies and evidence from studies in humans. The upstream KE ‘Decreased AR activity’ refers to an in vivo effect, for which no methods for measurement of this in vivo in mammals currently exist. The effects on the upstream KE were therefore indirectly informed as described in each section.

Animal studies

Effects on the upstream KE were indirectly informed by including animal studies with stressors that are known to reduce AR activity through antagonizing the AR, lowering testosterone production, or inhibiting 5α-reductase. Six stressors, with established anti-androgenic effects, were included (more detailed evaluation of these chemicals can be found in KER-2820 (Holmer et al., 2024)). Table 3 summarizes the empirical evidence and confidence level for each chemical. Details on included evidence is presented in Table 1 in Appendix 2, 9prbqyba2x_Appendix_2_KER_2828.pdf. In summary, all six substances were shown to cause hypospadias in male offspring, and the confidence level for all substances was judged as strong, as conflicting results could be explained (see the section ‘Uncertainties and inconsistencies’). Thus, antagonism or AR, inhibition of 5α-reductase, or reduction in testosterone synthesis, all lead to hypospadias.

Table 3 Summary of empirical evidence for the KER – animal studies. See Table 1 in Appendix 2 ( 9prbqyba2x_Appendix_2_KER_2828.pdf) for details.

Supporting human evidence

Effects on the upstream KE were indirectly informed by including studies in humans with a condition (genetic or other) that would reduce or disrupt either 1) function of AR, 2) conversion of testosterone to DHT by disrupting 5α-reductase activity, or 3) production of androgen hormones. Studies measuring low testosterone levels with no underlying cause were also included (see evidence collection strategy). Table 4 lists the studies, in which these conditions were linked to hypospadias in males.

Table 4 Supporting evidence for the KER – human studies. The table lists human studies reporting hypospadias in association with an upstream defect in AR activity, grouped according to the precise effect, and how it was diagnosed (mutation, in vitro activity, or blood hormone and metabolite profile). SRD5A2: 5α-reductase 2; HSD17B3: 17β-hydroxysteroid dehydrogenase 3; HSD3B2: 3β-hydroxysteroid dehydrogenase 2; CYP17A1: 17α-hydroxylase. See table 2 in Appendix 2  (9prbqyba2x_Appendix_2_KER_2828.pdf) for all included references.

Six case-control studies were extracted, all of which found a correlation between lower testosterone levels (basal or hCG-stimulated) and hypospadias (Austin et al., 2002; Okuyama et al., 1981; Raboch et al., 1976; Ratan et al., 2012; Svensson et al., 1979; Yadav et al., 2011). In two of these studies, the correlation was age-dependent (Austin et al., 2002; Raboch et al., 1976)

One epidemiologic study was extracted, which investigated the association between phthalate exposure and hypospadias risk.  Western Australian women exposed through their occupation to phthalates were more likely to have sons with hypospadias (Nassar et al., 2010). It should be noted that there are reported species differences in the effects of phthalates (including DEHP and DBP) on fetal testosterone production between humans, mice, and rats, and the direct translatability of the in vivo evidence is uncertain (Sharpe, 2020).

Dose concordance

Direct information about dose concordance is not available because AR activity currently cannot be measured in vivo.

Indirect information on dose concordance can be obtained from empirical evidence. In utero exposure of rats to DBP caused a dose-dependent decrease in serum testosterone levels at PND70 with LOAEL 250 mg/kg bw/day. Hypospadias was observed at this stage with LOAEL 500 mg/kg bw/day (Jiang et al., 2007). It should be noted that fetal testosterone levels were not measured.

Temporal concordance

Direct information about temporal concordance is not available because AR activity currently cannot be measured in vivo.

Indirect information on temporal concordance can be obtained from empirical evidence. In two studies, in which rats were exposed in utero to 750 mg/kg bw/day DBP, intratesticular testosterone levels were reduced in fetal testes, while hypospadias was identified in adult males. Plasma levels of testosterone were also measured in adults, and testosterone levels in exposed males were not significantly different from control males (van den Driesche et al., 2017, 2020). This has also been shown in a study with 500 mg/kg bw/day DBP (Drake et al., 2009). These studies indicate temporal concordance. Another study with DBP-induced hypospadias in rats saw a dose-dependent reduction in serum testosterone levels at PND70 after in utero exposure to as low as 250 mg/kg bw/day from GD14-18 (Jiang et al., 2007), though fetal testosterone levels were not measured in this study.

Incidence Concordance

Direct information about dose concordance is not available because AR activity currently cannot be measured in vivo.

Indirect information on incidence concordance can be obtained from empirical evidence. In the dose-response study with DBP, the incidence of hypospadias was 6.8% for 500 mg/kg bw/day DBP and 41.3% for 750 mg/kg bw/day. When separating hypospadias males from exposed males without hypospadias, plasma testosterone levels were decreased in both groups, indicating that DBP reduced testosterone levels at higher incidence than hypospadias (Jiang et al., 2007). The same was seen in another study with DBP, in which serum testosterone levels at PND7 were reduced in both hypospadiac and non-malformed males exposed to 750 mg/kg bw/day DBP from GD14-18 (Jiang et al., 2016).

The in vivo studies do not directly inform about the upstream KE, ‘decreased AR activity’. The direct concordance between the KEs can therefore not be determined from the evidence.

For flutamide, two studies reported 100% hypospadias frequencies at doses of 6.25 and 10 mg/kg bw/day (Goto et al., 2004; McIntyre et al., 2001), while another study found a frequency of 56.9% when giving 20 mg/kg bw/day (Kita et al., 2016). This might be explained by a longer exposure window in the first two studies and uncertainties in assessment of hypospadias.

For DBP, there were discrepancies in whether 250 mg/kg bw/day was LOAEL (Mylchreest et al., 1998, 1999) or NOAEL (Jiang et al., 2007) for DBP. This conflict was explained by differences in exposure windows, supported by the observation that the frequency of hypospadias at 250 mg/kg bw/day was reported as very low (Mylchreest et al., 1998, 1999).

One study with vinclozolin (Ostby J et al., 1999) and one with procymidone (Hass et al., 2012) did not find hypospadias after in utero exposure. In both cases, this was likely due to too low doses tested.

In most of the human studies of steroidogenesis deficiency, serum or plasma levels of testosterone were reduced at baseline and/or upon hCG stimulation (Al-Sinani et al., 2015; Ammini et al., 1997; Cara et al., 1985; Chen, Huang, et al., 2021; Dean et al., 1984; Galli-Tsinopoulou et al., 2018; Imperato-McGinley et al., 1979; Kaufman et al., 1983; Mendonca et al., 1987, 2000; Neocleous et al., 2012; New, 1970; Pang et al., 1983; Perrone et al., 1985; Rabbani et al., 2012; Sherbet et al., 2003), but in a few studies, testosterone levels were normal (Donadille et al., 2018; Kon et al., 2015; Luna et al., 2021). In these cases, the effect of these deficiencies on tissue AR activity is uncertain.

For AR CAG repeat length, a case-control study did not find an association with hypospadias (Radpour R et al., 2007), but this could be because the hypospadias cases included had other etiologies.

Lastly, as there are currently no universal guidelines for identification and scoring of hypospadias in rodents, there are large variations in methods of assessment, and minor cases of hypospadias may be overlooked in some studies and included in others. This poses an uncertainty in the frequency reports in the scientific evidence.

Quantitative Understanding of the Linkage

The quantitative understanding of the relationship is low. As there are currently no direct measurement methods of the upstream KE (reduced AR activity) in mammals, quantification of the relationship is difficult to assess.

A model for phthalates has been developed, aiming to predict the frequency of hypospadias in male offspring based on reductions in ex vivo testosterone production, an indirect indication of AR activity. In this model, hypospadias was induced from around a 60% reduction in testosterone levels. The model does not consider hypospadias severity and is only for phthalate chemicals (Earl Gray et al., 2024).

The time-scale of this KER depends on the species but is likely days to weeks.

AR activation happens within minutes, from ligand binding to nuclear translocation and promotor activation (Nightingale et al., 2003; Schaufele et al., 2005), while transcriptional and translational effects are observed minutes to hours later (Kang et al., 2002). AR programming of the genital tubercle occurs during fetal development in the Masculinization Programming Window (Sharpe, 2020). The time-scale for morphological effects in the tissue then depends on the species. In humans, penis development is completed prior to birth and hypospadias can be observed at birth. In rodents, penis development is not fully completed until weeks after birth, but hypospadias can often be observed earlier than this (table 3). 

There are no known feedforward/feedback loops influencing this KER.

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