AOP ID and Title:
Graphical Representation
Status
| Author status | OECD status | OECD project | SAAOP status |
|---|---|---|---|
| Under development: Not open for comment. Do not cite | Under Development | 1.90 | Included in OECD Work Plan |
Abstract
This AOP links Androgen receptor (AR) antagonism 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).
The AR is a nuclear receptor involved in the transcriptional regulation of various target genes during development and adulthood across species (Heemers & Tindall, 2007; Davey and Grossmann, 2016). Its main ligand is testosterone and dihydrotestosterone (DHT). Under normal physiological conditions, testosterone produced mainly by the testicles, 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 normal masculinization of the developing fetus, including differentiation of the levator ani/bulbocavernosus (LABC) muscle complex in male fetuses (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 central step in this pathway is antagonism of the AR in target cells of the undifferentiated perineal region, which leads to inactivation of the AR and failure to properly masculinize the perineum/LABC complex. In this instance, the local levels of testosterone or DHT may be physiologically normal (or sufficient) levels, but prevented from binding the AR.
Background
This AOP was developed as part of an AOP network for developmental androgen signalling-inhibition leading to short AGD in male offspring. The other AOPs in this network are AOP 305 (5α-reductase inhibition leading to short AGD) and 307 (Decreased testosterone synthesis leading to short AGD).
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.
Summary of the AOP
Events
Molecular Initiating Events (MIE), Key Events (KE), Adverse Outcomes (AO)
| Sequence | Type | Event ID | Title | Short name |
|---|---|---|---|---|
| MIE | 26 | Antagonism, Androgen receptor | Antagonism, Androgen receptor | |
| 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 |
Key Event Relationships
| Upstream Event | Relationship Type | Downstream Event | Evidence | Quantitative Understanding |
|---|---|---|---|---|
| Antagonism, Androgen receptor | adjacent | Decrease, androgen receptor activation | High | High |
| Decrease, androgen receptor activation | adjacent | Altered, Transcription of genes by the androgen receptor | Moderate | |
| Decrease, androgen receptor activation | non-adjacent | anogenital distance (AGD), decreased | High | |
| Altered, Transcription of genes by the androgen receptor | non-adjacent | anogenital distance (AGD), decreased | Moderate |
Stressors
| Name | Evidence |
|---|---|
| Finasteride | High |
| Flutamide | High |
Finasteride
Intrauterine exposure in rats can result in shorter male AGD in male offspring as reported in:
Bowman et al (2003), Toxicol Sci 74:393-406; doi: 10.1093/toxsci/kfg128
Christiansen et al (2009), Environ Health Perspect 117:1839-1846; doi: 10.1289/ehp.0900689
Schwartz et al (2019), Toxicol Sci 169:303-311; doi: 10.1093/toxsci/kfz046
Flutamide
Finasteride is a selective androgen receptor (AR) antagonist (Simard et al 1986) that has been shown to induce shorter male AGD in rats after in utero exposure (Foster & Harris 2005; Hass et al 2007; Kita et al 2016; McIntyre et al 2001; Mylchreest et al 1999; Scott et al 2007; Welsh et al 2007).
References:
Foster & Harris (2005), Toxicol Sci 85:1024-1032; doi: 10.1093/toxsci/kfi159
Hass et al (2007), Environ Health Perspect 115(suppl 1):122-128; doi: 10.1289/ehp.0360
Kita et al (2016), Toxicology 368-369:152-161; doi: 10.1016/j.tox.2016.08.021
McIntyre et al (2001), Toxicol Sci 62:236-249; doi: 10.1093/toxsci/62.2.236
Mylchreest et al (1999), Toxicol Appl Pharmacol 156:81-95; doi: 10.1006/taap.1999.8643
Scott et al (2007), Endocrinology 148:2027-2036; doi: 10.1210/en.2006-1622
Simard et al (1986), Mol Cell Endocrinol 44:261-270; doi: 10.1016/0303-7207(86)90132-2
Overall Assessment of the AOP
Domain of Applicability
Life Stage Applicability| Life Stage | Evidence |
|---|---|
| Foetal | High |
| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| human | Homo sapiens | Moderate | NCBI |
| rat | Rattus norvegicus | High | NCBI |
| mouse | Mus musculus | Moderate | NCBI |
| mammals | mammals | Moderate | NCBI |
| Sex | Evidence |
|---|---|
| Male | High |
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 (see Supplementary Table S1, 8oqfwwo772_Supplementary_Table_S1_Essentiality_table_AOPs_305_307.pdf), with a summary provided in Table 1.
Table 1: Essentiality assessment of KEs of AOP 306:
|
Event |
Direct evidence |
Indirect evidence |
Contradictory evidence |
Overall essentiality assessment |
|
MIE-26 |
*** |
* |
|
High |
|
KE-1614 |
*** |
*** |
|
High |
|
KE-286 |
|
*** |
|
Moderate |
*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).
Weight of Evidence Summary
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 |
|
Upstream KERs in AOP 306 |
||
|
KER-2130 |
High |
It is well established that antagonism of the AR leads to decreased AR activity. |
|
Upstream KERs in AOP 305 |
||
|
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. |
|
Upstream KERs in AOP 307 |
||
|
KER-2131 |
High |
It is well established that testosterone activates the AR and that decreased testosterone levels leads to decreased AR activation. |
|
Downstream KERs shared by AOP 305-307 |
||
|
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. |
Quantitative Consideration
The quantitative understanding of this AOP remains low.
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).
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.
Heemers HV, Tindall DJ (2007). Androgen receptor (AR) coregulators: a diversity of functions converging on and regulating the AR transcriptional complex. Endocr Rev 28(7):778-808.
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.
Appendix 1
List of MIEs in this AOP
Event: 26: Antagonism, Androgen receptor
Short Name: Antagonism, Androgen receptor
Key Event Component
| Process | Object | Action |
|---|---|---|
| androgen receptor activity | androgen receptor | decreased |
AOPs Including This Key Event
| AOP ID and Name | Event Type |
|---|---|
| Aop:306 - Androgen receptor (AR) antagonism leading to short anogenital distance (AGD) in male (mammalian) offspring | MolecularInitiatingEvent |
| Aop:344 - Androgen receptor (AR) antagonism leading to nipple retention (NR) in male (mammalian) offspring | MolecularInitiatingEvent |
| Aop:345 - Androgen receptor (AR) antagonism leading to decreased fertility in females | MolecularInitiatingEvent |
| Aop:372 - Androgen receptor antagonism leading to testicular cancer | MolecularInitiatingEvent |
| Aop:477 - Androgen receptor (AR) antagonism leading to hypospadias in male (mammalian) offspring | MolecularInitiatingEvent |
| Aop:476 - Adverse Outcome Pathways diagram related to PBDEs associated male reproductive toxicity | MolecularInitiatingEvent |
| Aop:19 - Androgen receptor antagonism leading to adverse effects in the male foetus (mammals) | MolecularInitiatingEvent |
Stressors
| Name |
|---|
| Mercaptobenzole |
| Triticonazole |
| Flusilazole |
| Epoxiconazole |
| Prochloraz |
| Propiconazole |
| Tebuconazole |
| Flutamide |
| Cyproterone acetate |
| Vinclozolin |
Biological Context
| Level of Biological Organization |
|---|
| Molecular |
Cell term
| Cell term |
|---|
| eukaryotic cell |
Domain of Applicability
Taxonomic Applicability| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| mammals | mammals | High | NCBI |
| Life Stage | Evidence |
|---|---|
| During development and at adulthood | High |
| Sex | Evidence |
|---|---|
| Mixed | High |
Both the DNA-binding and ligand-binding domains of the AR are highly evolutionary conserved, whereas the transactivation domain show more divergence which may affect AR-mediated gene regulation across species (Davey & Grossmann, 2016). Despite certain inter-species differences, AR function mediated through gene expression is highly conserved, with mutations studies from both humans and rodents showing strong correlation for AR-dependent development and function (Walters et al, 2010).
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 KE 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 Description
The androgen receptor (AR) and its function
The AR is a ligand-activated transcription factor belonging to the steroid hormone nuclear receptor family (Davey & Grossmann, 2016). The AR has three domains: the N-terminal domain, the DNA-binding domain and the ligand-binding domain, with the latter being most evolutionary conserved. Testosterone (T) and the more biologically active dihydrotestosterone (DHT) are endogenous ligands for the AR (MacLean et al, 1993; MacLeod et al, 2010; Schwartz et al, 2019). In teleost fishes, 11-ketotestosterone is the second main ligand (Schuppe et al, 2020). Human AR mutations and mouse knock-out models have established a pivotal role for the AR in masculinization and spermatogenesis (Walters et al, 2010). Apart from the essential role for AR in male reproductive development and function (Walters et al, 2010), the AR is also expressed in many other tissues and organs such as bone, muscles, ovaries, and the immune system (Rana et al, 2014).
AR antagonism as Key Event
The main function of the AR is to activate gene transcription in cells. Canonical signaling occurs by ligands (androgens) binding to AR in the cytoplasm which results in translocation to the cell nucleus, receptor dimerization and binding to specific regulatory DNA sequences (Heemers & Tindall, 2007). The gene targets regulated by AR activation depends on cell/tissue type and what stage of development activation occur, and is, for instance, dependent on available co-factors. Apart from the canonical signaling pathway, AR can also initiate cytoplasmic signaling pathways with other functions than the nuclear pathway, for instance rapid change in cell function by ion transport changes (Heinlein & Chang, 2002) and association with Src kinase to activate MAPK/ERK signaling and activation of the PI3K/Akt pathway (Leung & Sadar, 2017).
How it is Measured or Detected
AR antagonism can be measured in vitro by transient or stable transactivation assays to evaluate nuclear receptor activation. There is already a validated test guideline for AR (ant)agonism adopted by the OECD, Test No. 458: Stably Transfected Human Androgen Receptor Transcriptional Activation Assay for Detection of Androgenic Agonist and Antagonist Activity of Chemicals (OECD, 2016). This test guideline contains three different methods. More information on limitations, advantages, protocols, and availability and description of cells are given in the test guideline.
Besides these validated methods, other transiently or stably transfected reporter cell lines are available as well as yeast based systems (Campana et al, 2015; Körner et al, 2004). AR nuclear translocation can be monitored by various assays (Campana et al 2015), for example by monitoring fluorescent rat AR movement in living cells (Tyagi et al 2020), with several human AR translocation assays being commercially available; e.g. Fluorescent AR Nuclear Translocation Assay (tGFP-hAR/HEK293) or Human Androgen NHR Cell Based Antagonist Translocation LeadHunter Assay.
Additional information on AR interaction can be obtained employing competitive AR binding assays (Freyberger et al 2010, Shaw et al 2018), which can also inform on relative potency of the compounds, though not on downstream effect of the AR binding.
The recently developed AR dimerization assay provides an assay with an improved ability to measure potential stressor-mediated disruption of dimerization/activation (Lee et al, 2021).
References
Campana C, Pezzi V, Rainey WE (2015) Cell based assays for screening androgen receptor ligands. Semin Reprod Med 33: 225-234.
Freyberger A, Weimer M, Tran HS, Ahr HJ. Assessment of a recombinant androgen receptor binding assay: initial steps towards validation. Reprod Toxicol. 2010 Aug;30(1):2-8. doi: 10.1016/j.reprotox.2009.10.001. Epub 2009 Oct 13. PMID: 19833195.
OECD (2022). Test No. 251: Rapid Androgen Disruption Activity Reporter (RADAR) assay. Paris: OECD Publishing doi:10.1787/da264d82-en.
Shaw J, Leveridge M, Norling C, Karén J, Molina DM, O'Neill D, Dowling JE, Davey P, Cowan S, Dabrowski M, Main M, Gianni D. Determining direct binders of the Androgen Receptor using a high-throughput Cellular Thermal Shift Assay. Sci Rep. 2018 Jan 9;8(1):163. doi: 10.1038/s41598-017-18650-x. PMID: 29317749; PMCID: PMC5760633.
Tyagi RK, Lavrovsky Y, Ahn SC, Song CS, Chatterjee B, Roy AK (2000) Dynamics of intracellular movement and nucleocytoplasmic recycling of the ligand-activated androgen receptor in living cells. Mol Endocrinol 14: 1162-1174
List of Key Events in the AOP
Event: 1614: Decrease, androgen receptor activation
Short Name: Decrease, AR activation
Key Event Component
| Process | Object | Action |
|---|---|---|
| androgen receptor activity | androgen receptor | decreased |
AOPs Including This Key Event
Biological Context
| Level of Biological Organization |
|---|
| Tissue |
Domain of Applicability
Taxonomic Applicability| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| mammals | mammals | High | NCBI |
| Life Stage | Evidence |
|---|---|
| During development and at adulthood | High |
| Sex | Evidence |
|---|---|
| Mixed | High |
This KE is considered broadly applicable across mammalian taxa as all mammals express the AR in numerous cells and tissues where it regulates gene transcription required for developmental processes and functions. It is, however, acknowledged that this KE 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 Description
This KE refers to decreased activation of the androgen receptor (AR) as occurring in complex biological systems such as tissues and organs in vivo. It is thus considered distinct from KEs describing either blocking of AR or decreased androgen synthesis.
The AR is a nuclear transcription factor with canonical AR activation regulated by the binding of the androgens such as testosterone or dihydrotestosterone (DHT). Thus, AR activity can be decreased by reduced levels of steroidal ligands (testosterone, DHT) or the presence of compounds interfering with ligand binding to the receptor (Davey & Grossmann, 2016; Gao et al., 2005).
In the inactive state, AR is sequestered in the cytoplasm of cells by molecular chaperones. In the classical (genomic) AR signaling pathway, AR activation causes dissociation of the chaperones, AR dimerization and translocation to the nucleus to modulate gene expression. AR binds to the androgen response element (ARE) (Davey & Grossmann, 2016; Gao et al., 2005). Notably, for transcriptional regulation the AR is closely associated with other co-factors that may differ between cells, tissues and life stages. In this way, the functional consequence of AR activation is cell- and tissue-specific. This dependency on co-factors such as the SRC proteins also means that stressors affecting recruitment of co-activators to AR can result in decreased AR activity (Heinlein & Chang, 2002).
Ligand-bound AR may also associate with cytoplasmic and membrane-bound proteins to initiate cytoplasmic signaling pathways with other functions than the nuclear pathway. Non-genomic AR signaling includes association with Src kinase to activate MAPK/ERK signaling and activation of the PI3K/Akt pathway. Decreased AR activity may therefore be a decrease in the genomic and/or non-genomic AR signaling pathways (Leung & Sadar, 2017).
How it is Measured or Detected
This KE specifically focuses on decreased in vivo activation, with most methods that can be used to measure AR activity carried out in vitro. They provide indirect information about the KE and are described in lower tier MIE/KEs (see for example MIE/KE-26 for AR antagonism, KE-1690 for decreased T levels and KE-1613 for decreased dihydrotestosterone levels). Assays may in the future be developed to measure AR activation in mammalian organisms.
References
Davey, R. A., & Grossmann, M. (2016). Androgen Receptor Structure, Function and Biology: From Bench to Bedside. The Clinical Biochemist. Reviews, 37(1), 3–15.
Gao, W., Bohl, C. E., & Dalton, J. T. (2005). Chemistry and structural biology of androgen receptor. Chemical Reviews, 105(9), 3352–3370. https://doi.org/10.1021/cr020456u
Heinlein, C. A., & Chang, C. (2002). Androgen Receptor (AR) Coregulators: An Overview. https://academic.oup.com/edrv/article/23/2/175/2424160
Leung, J. K., & Sadar, M. D. (2017). Non-Genomic Actions of the Androgen Receptor in Prostate Cancer. Frontiers in Endocrinology, 8. https://doi.org/10.3389/fendo.2017.00002
OECD (2022). Test No. 251: Rapid Androgen Disruption Activity Reporter (RADAR) assay. Paris: OECD Publishing doi:10.1787/da264d82-en.
|
|
|
Event: 286: Altered, Transcription of genes by the androgen receptor
Short Name: Altered, Transcription of genes by the AR
Key Event Component
| Process | Object | Action |
|---|---|---|
| regulation of gene expression | androgen receptor | decreased |
AOPs Including This Key Event
Stressors
| Name |
|---|
| Bicalutamide |
| Cyproterone acetate |
| Epoxiconazole |
| Flutamide |
| Flusilazole |
| Prochloraz |
| Propiconazole |
| Stressor:286 Tebuconazole |
| Triticonazole |
| Vinclozalin |
Biological Context
| Level of Biological Organization |
|---|
| Tissue |
Domain of Applicability
Taxonomic Applicability| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| mammals | mammals | High | NCBI |
| Life Stage | Evidence |
|---|---|
| During development and at adulthood | High |
| Sex | Evidence |
|---|---|
| Mixed | High |
Both the DNA-binding and ligand-binding domains of the AR are highly evolutionary conserved, whereas the transactivation domain show more divergence, which may affect AR-mediated gene regulation across species (Davey and Grossmann 2016). Despite certain inter-species differences, AR function mediated through gene expression is highly conserved, with mutation studies from both humans and rodents showing strong correlation for AR-dependent development and function (Walters et al. 2010).
This KE is considered broadly applicable across mammalian taxa, sex and developmental stages, as all mammals express the AR in numerous cells and tissues where it regulates gene transcription required for developmental processes and function. It is, however, acknowledged that this KE 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 Description
This KE refers to transcription of genes by the androgen receptor (AR) as occurring in complex biological systems such as tissues and organs in vivo. Rather than measuring individual genes, this KE aims to capture patterns of effects at transcriptome level in specific target cells/tissues. In other words, it can be replaced by specific KEs for individual adverse outcomes as information becomes available, for example the transcriptional toxicity response in prostate tissue for AO: prostate cancer, perineum tissue for AO: reduced AGD, etc. AR regulates many genes that differ between tissues and life stages and, importantly, different gene transcripts within individual cells can go in either direction since AR can act as both transcriptional activator and suppressor. Thus, the ‘directionality’ of the KE cannot be either reduced or increased, but instead describe an altered transcriptome.
The Androgen Receptor and its function
The AR belongs to the steroid hormone nuclear receptor family. It is a ligand-activated transcription factor with three domains: the N-terminal domain, the DNA-binding domain, and the ligand-binding domain with the latter being the most evolutionary conserved (Davey and Grossmann 2016). Androgens (such as dihydrotestosterone and testosterone) are AR ligands and act by binding to the AR in androgen-responsive tissues (Davey and Grossmann 2016). Human AR mutations and mouse knockout models have established a fundamental role for AR in masculinization and spermatogenesis (Maclean et al.; Walters et al. 2010; Rana et al. 2014). The AR is also expressed in many other tissues such as bone, muscles, ovaries and within the immune system (Rana et al. 2014).
Altered transcription of genes by the AR as a Key Event
Upon activation by ligand-binding, the AR translocates from the cytoplasm to the cell nucleus, dimerizes, binds to androgen response elements in the DNA to modulate gene transcription (Davey and Grossmann 2016). The transcriptional targets vary between cells and tissues, as well as with developmental stages and is also dependent on available co-regulators (Bevan and Parker 1999; Heemers and Tindall 2007). It should also be mentioned that the AR can work in other ‘non-canonial’ ways such as non-genomic signaling, and ligand-independent activation (Davey & Grossmann, 2016; Estrada et al, 2003; Jin et al, 2013).
A large number of known, and proposed, target genes of AR canonical signaling have been identified by analysis of gene expression following treatments with AR agonists (Bolton et al. 2007; Ngan et al. 2009, Jin et al. 2013).
How it is Measured or Detected
Altered transcription of genes by the AR can be measured by measuring the transcription level of known downstream target genes by RT-qPCR or other transcription analyses approaches, e.g. transcriptomics.
Since this KE aims to capture AR-mediated transcriptional patterns of effect, downstream bioinformatics analyses will typically be required to identify and compare effect footprints. Clusters of genes can be statistically associated with, for example, biological process terms or gene ontology terms relevant for AR-mediated signaling. Large transcriptomics data repositories can be used to compare transcriptional patterns between chemicals, tissues, and species (e.g. TOXsIgN (Darde et al, 2018a; Darde et al, 2018b), comparisons can be made to identified sets of AR ‘biomarker’ genes (e.g. as done in (Rooney et al, 2018)), and various methods can be used e.g. connectivity mapping (Keenan et al, 2019).
References
Bevan C, Parker M (1999) The role of coactivators in steroid hormone action. Exp. Cell Res. 253:349–356
Bolton EC, So AY, Chaivorapol C, et al (2007) Cell- and gene-specific regulation of primary target genes by the androgen receptor. Genes Dev 21:2005–2017. doi: 10.1101/gad.1564207
Darde, T. A., Gaudriault, P., Beranger, R., Lancien, C., Caillarec-Joly, A., Sallou, O., et al. (2018a). TOXsIgN: a cross-species repository for toxicogenomic signatures. Bioinformatics 34, 2116–2122. doi:10.1093/bioinformatics/bty040.
Darde, T. A., Chalmel, F., and Svingen, T. (2018b). Exploiting advances in transcriptomics to improve on human-relevant toxicology. Curr. Opin. Toxicol. 11–12, 43–50. doi:10.1016/j.cotox.2019.02.001.
Davey RA, Grossmann M (2016) Androgen Receptor Structure, Function and Biology: From Bench to Bedside. Clin Biochem Rev 37:3–15
Estrada M, Espinosa A, Müller M, Jaimovich E (2003) Testosterone Stimulates Intracellular Calcium Release and Mitogen-Activated Protein Kinases Via a G Protein-Coupled Receptor in Skeletal Muscle Cells. Endocrinology 144:3586–3597. doi: 10.1210/en.2002-0164
Heemers H V., Tindall DJ (2007) Androgen receptor (AR) coregulators: A diversity of functions converging on and regulating the AR transcriptional complex. Endocr. Rev. 28:778–808
Jin, Hong Jian, Jung Kim, and Jindan Yu. 2013. “Androgen Receptor Genomic Regulation.” Translational Andrology and Urology 2(3):158–77. doi: 10.3978/j.issn.2223-4683.2013.09.01
Keenan, A. B., Wojciechowicz, M. L., Wang, Z., Jagodnik, K. M., Jenkins, S. L., Lachmann, A., et al. (2019). Connectivity Mapping: Methods and Applications. Annu. Rev. Biomed. Data Sci. 2, 69–92. doi:10.1146/ANNUREV-BIODATASCI-072018-021211.
Maclean HE, Chu S, Warne GL, Zajact JD Related Individuals with Different Androgen Receptor Gene Deletions
MacLeod DJ, Sharpe RM, Welsh M, et al (2010) Androgen action in the masculinization programming window and development of male reproductive organs. In: International Journal of Andrology. Blackwell Publishing Ltd, pp 279–287
Ngan S, Stronach EA, Photiou A, et al (2009) Microarray coupled to quantitative RT–PCR analysis of androgen-regulated genes in human LNCaP prostate cancer cells. Oncogene 28:2051–2063. doi: 10.1038/onc.2009.68
Rana K, Davey RA, Zajac JD (2014) Human androgen deficiency: Insights gained from androgen receptor knockout mouse models. Asian J. Androl. 16:169–177
Rooney, J. P., Chorley, B., Kleinstreuer, N., and Corton, J. C. (2018). Identification of Androgen Receptor Modulators in a Prostate Cancer Cell Line Microarray Compendium. Toxicol. Sci. 166, 146–162. doi:10.1093/TOXSCI/KFY187.
Walters KA, Simanainen U, Handelsman DJ (2010) Molecular insights into androgen actions in male and female reproductive function from androgen receptor knockout models. Hum Reprod Update 16:543–558. doi: 10.1093/humupd/dmq003
List of Adverse Outcomes in this AOP
Event: 1688: anogenital distance (AGD), decreased
Short Name: AGD, decreased
Key Event Component
| Process | Object | Action |
|---|---|---|
| androgen receptor signaling pathway | Musculature of male perineum | disrupted |
AOPs Including This Key Event
Stressors
| Name |
|---|
| Butylparaben |
| p,p'-DDE |
| Bis(2-ethylhexyl) phthalate |
| Dexamethasone |
| Fenitrothion |
| Finasteride |
| Flutamide |
| Ketoconazole |
| Linuron |
| Prochloraz |
| Procymidone |
| Triticonazole |
| Vinclozolin |
| di-n-hexyl phthalate |
| Dicyclohexyl phthalate |
| butyl benzyl phthalate |
| monobenzyl phthalate |
| di-n-heptyl phthalate |
Biological Context
| Level of Biological Organization |
|---|
| Tissue |
Organ term
| Organ term |
|---|
| perineum |
Domain of Applicability
Taxonomic Applicability| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| human | Homo sapiens | Moderate | NCBI |
| rat | Rattus norvegicus | High | NCBI |
| mouse | Mus musculus | High | NCBI |
| Life Stage | Evidence |
|---|---|
| Foetal | High |
| Sex | Evidence |
|---|---|
| Male | High |
A short AGD in male offspring is a marker of insufficient androgen action during critical fetal developmental stages (Schwartz et al, 2019; Welsh et al, 2008). A short AGD is thus a sign of undervirilization, which is also associated with a series of male reproductive disorders, including genital malformations and infertility in humans (Juul et al, 2014; Skakkebaek et al, 2001).
There are numerous human epidemiological studies showing associations with intrauterine exposure to anti-androgenic chemicals and short AGD in newborn boys alongside other reproductive disorders (Schwartz et al, 2019). This underscores the human relevance of this AO. However, in reproductive toxicity studies and chemical risk assessment, rodents (rats and mice) are what is tested on. The list of chemicals inducing short male AGD in male rat offspring is extensive, as evidenced by the ‘stressor’ list and reviewed by (Schwartz et al, 2019).
Key Event Description
The anogenital distance (AGD) refers to the distance between anus and the external genitalia. In rodents and humans, the male AGD is approximately twice the length as the female AGD (Salazar-Martinez et al, 2004; Schwartz et al, 2019). This sexual dimorphisms is a consequence of sex hormone-dependent development of secondary sexual characteristics (Schwartz et al, 2019). In males, it is believed that androgens (primarily DHT) activate AR-positive cells in non-myotic cells in the fetal perineum region to initiate differentiation of the perineal levator ani and bulbocavernosus (LABC) muscle complex (Ipulan et al, 2014). This AR-dependent process occurs within a critical window of development, around gestational days 15-18 in rats (MacLeod et al, 2010). In females, the absence of DHT prevents this masculinization effect from occurring.
The involvement of androgens in masculinization of the male fetus, including the perineum, has been known for a very long time (Jost, 1953), and AGD has historically been used to, for instance, sex newborn kittens. It is now well established that the AGD in newborns is a proxy readout for the intrauterine sex hormone milieu the fetus was developing. Too low androgen levels in XY fetuses makes the male AGD shorter, whereas excess (ectopic) androgen levels in XX fetuses makes the female AGD longer, in humans and rodents (Schwartz et al, 2019).
How it is Measured or Detected
The AGD is a morphometric measurement carried out by trained technicians (rodents) or medical staff (humans).
In rodent studies AGD is assessed as the distance between the genital papilla and the anus, and measured using a stereomicroscope with a micrometer eyepiece. The AGD index (AGDi) is often calculated by dividing AGD by the cube root of the body weight. It is important in statistical analysis to use litter as the statistical unit. This is done when more than one pup from each litter is examined. Statistical analyses is adjusted using litter as an independent, random and nested factor. AGD are analysed using body weight as covariate as recommended in Guidance Document 151 (OECD, 2013).
Regulatory Significance of the AO
In regulatory toxicology, the AGD is mandatory inclusions in OECD test guidelines used to test for developmental and reproductive toxicity of chemicals. Guidelines include ‘TG 443 extended one-generation study’, ‘TG 421/422 reproductive toxicity screening studies’ and ‘TG 414 developmental toxicity study’.
References
Appendix 2
List of Key Event Relationships in the AOP
List of Adjacent Key Event Relationships
Relationship: 2130: Antagonism, Androgen receptor leads to Decrease, AR activation
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| Androgen receptor (AR) antagonism leading to short anogenital distance (AGD) in male (mammalian) offspring | adjacent | High | High |
| Androgen receptor (AR) antagonism leading to nipple retention (NR) in male (mammalian) offspring | adjacent | High | |
| Androgen receptor (AR) antagonism leading to hypospadias in male (mammalian) offspring | adjacent | High | |
| Androgen receptor (AR) antagonism leading to decreased fertility in females | adjacent | High | Moderate |
Evidence Supporting Applicability of this Relationship
| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| mammals | mammals | High | NCBI |
| Life Stage | Evidence |
|---|---|
| During development and at adulthood | High |
| Sex | Evidence |
|---|---|
| Mixed | High |
This KER is applicable to mammals as AR expression and activity is highly conserved (Davey & Grossmann, 2016). AR activity is important for sexual development and reproduction in both males and females (Prizant et al., 2014; Walters et al., 2010). AR function is required during development, puberty, and adulthood. 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-activated steroid hormone nuclear receptor (Davey & Grossmann, 2016). In its inactive state, the AR locates to the cytoplasm (Roy et al., 2001). When activated, the AR translocates to the nucleus, dimerizes, and, together with co-regulators, binds to specific DNA regulatory sequences to regulate gene transcription (Davey & Grossmann, 2016) (Lamont and Tindall, 2010). This is considered the canonical AR signaling pathway. The AR can also activate non-genomic signalling (Jin et al., 2013). However, this KER focuses on the canonical pathway.
The two main AR ligands are the androgens testosterone (T) and the more potent dihydrotestosterone (DHT). Androgens bind to the AR to mediate downstream androgenic responses, such as male development and masculinization (Rey, 2021; Walters et al., 2010). Antagonism of the AR would decrease AR activation and therefore the downstream AR-mediated effects.
Evidence Supporting this KER
Biological PlausibilityThe biological plausibility for this KER is considered high.
The AR belongs to the steroid hormone nuclear receptor family. The AR has 3 main domains essential for its activity, the N-terminal domain, the ligand binding domain, and the DNA binding domain (Roy et al., 2001). Ligands, such as T and DHT, must bind to the ligand binding domain to activate AR allowing it to fulfill its role as a transcription factor. The binding of the ligand induces a change in AR conformation allowing it to translocate to the nucleus and congregate into a subnuclear compartment (Marcelli et al., 2006; Roy et al., 2001) homodimerize and bind to the DNA target sequences and regulate transcription of target genes. Regulation of AR target genes is greatly facilitated by numerous co-factors. Active AR signaling is essential for male reproduction and sexual development and is also crucial in several other tissues and organs such as ovaries, the immune system, bones, and muscles (Ogino et al., 2011; Prizant et al., 2014; Rey, 2021; William H. Walker, 2021).
AR antagonists can compete with or prevent in different ways AR ligand binding, thereby preventing AR activation. Antagonism of the AR can prevent translocation to the nucleus, compartmentalization, dimerization and DNA binding. Consequently, AR cannot regulate transcription of target genes and androgen signalling is disrupted. This can be observed using different AR activation assays such as AR dimerization, translocation, DNA binding or transcriptional activity assays (Brown et al., 2023; OECD, 2020).
Empirical EvidenceThe empirical evidence for this KER is considered high
The effects of AR antagonism have been shown in many studies in vivo and in vitro.
Several stressors can act as antagonists of the AR and lead to decreased AR activation. Some of these are detailed in an AOP key event relationship report by (Pedersen et al., 2022) and shown below, exhibiting evidence of dose-concordance:
Stressors
- Cyproterone acetate: Using the AR-CALUX reporter assay in antagonism mode, cyproterone acetate showed an IC50 of 7.1 nM (Sonneveld, 2005)
- Epoxiconazole: Using transiently AR-transfected CHO cells, epoxiconazole showed a LOEC of 1.6 µM and an IC50 of 10 µM (Kjærstad et al., 2010).
- Flutamide: Using the AR-CALUX reporter assay in antagonism mode, flutamide showed an IC50 of 1.3 µM (Sonneveld, 2005).
- Flusilazole: Using hAR-EcoScreen Assay, triticonazole showed a LOEC for antagonisms of 0.8 µM and an IC50 of 2.8 (±0.1) µM (Draskau et al., 2019).
- Prochloraz: Using transiently AR-transfected CHO cells, prochloraz showed a LOEC of 6.3 µM and an IC50 of 13 µM (Kjærstad et al., 2010).
- Propiconazole: Using transiently AR-transfected CHO cells, propiconazole showed a LOEC of 12.5 µM and an IC50 of 18 µM (Kjærstad et al., 2010).
- Tebuconazole: Using transiently AR-transfected CHO cells, tebuconazole showed a LOEC of 3.1 µM and an IC50 of 8.1 µM (Kjærstad et al., 2010).
- Triticonazole: Using hAR-EcoScreen Assay, triticonazole showed a LOEC for antagonisms of 0.2 µM and an IC50 of 0.3 (±0.01) µM (Draskau et al., 2019).
- Vinclozolin: Using the AR-CALUX reporter assay in antagonism mode, vinclozolin showed an IC50of 1.0 µM(Sonneveld, 2005).”(Pedersen et al., 2022)
Other evidence:
Known AR antagonists are used for treatment of AR-sensitive cancers such as flutamide for prostate cancer (Mahler et al., 1998).
Uncertainties and Inconsistencies
Known antiandrogenic compounds like hydroxyflutamide have been shown to act as agonists when the AR carries certain mutations, therefore contributing to uncertainties (Yeh et al., 1997). Additionally, the levels of endogenous androgens (e.g., testosterone or dihydrotestosterone) and the variability in the presence and function of AR co-activators may modulate the effect of AR antagonism.
Quantitative Understanding of the Linkage
Response-response relationshipThe quantitative relationship between AR antagonism and AR activation will depend on the type of antagonist.
Time-scaleNuclear translocation in HeLa cells transfected with AR-GFP show a response within 2 hours after ligand exposure (Marcelli et al., 2006; Szafran et al., 2008). Another assay focusing on AR binding to promoters in LNCaP cells has shown that after ligand binding, AR is able to translocate and bind to the DNA sequences within 15min showing the speed of AR activation (Kang et al., 2002).
Known Feedforward/Feedback loops influencing this KERAR antagonism can lead to increased AR transcript stability and levels as a compensatory mechanism in prostate cancer cells (Dart et al., 2020). In turn, in presence of increased AR levels, AR antagonists can exhibit agonistic activity (Chen et al., 2003).
References
Brown, E. C., Hallinger, D. R., Simmons, S. O., Puig-Castellví, F., Eilebrecht, E., Arnold, L., & Bioscience, P. A. (2023). High-throughput AR dimerization assay identifies androgen disrupting chemicals and metabolites. Front. Toxicol, 5, 1134783. https://doi.org/10.3389/ftox.2023.1134783
Chen, C. D., Welsbie, D. S., Tran, C., Baek, S. H., Chen, R., Vessella, R., Rosenfeld, M. G., & Sawyers, C. L. (2003). A R T I C L E S Molecular determinants of resistance to antiandrogen therapy. NATURE MEDICINE, 10(1). https://doi.org/10.1038/nm972
Dart, D. A., Ashelford, K., & Jiang, W. G. (2020). AR mRNA stability is increased with AR-antagonist resistance via 3′UTR variants. https://doi.org/10.1530/EC-19-0340
Davey, R. A., & Grossmann, M. (2016). Androgen Receptor Structure, Function and Biology: From Bench to Bedside. In Androgen Receptor Biology Clin Biochem Rev (Vol. 37, Issue 1).
Draskau, M. K., Boberg, J., Taxvig, C., Pedersen, M., Frandsen, H. L., Christiansen, S., & Svingen, T. (2019). In vitro and in vivo endocrine disrupting effects of the azole fungicides triticonazole and flusilazole. Environmental Pollution, 255, 113309. https://doi.org/10.1016/j.envpol.2019.113309
Jin, H. J., Kim, J., & Yu, J. (2013). Androgen receptor genomic regulation. In Translational Andrology and Urology (Vol. 2, Issue 3, pp. 158–177). AME Publishing Company. https://doi.org/10.3978/j.issn.2223-4683.2013.09.01
Kang, Z., Pirskanen, A., Jänne, O. A., & Palvimo, J. J. (2002). Involvement of Proteasome in the Dynamic Assembly of the Androgen Receptor Transcription Complex. Journal of Biological Chemistry, 277(50), 48366–48371. https://doi.org/10.1074/jbc.M209074200
Kjærstad, M. B., Taxvig, C., Nellemann, C., Vinggaard, A. M., & Andersen, H. R. (2010). Endocrine disrupting effects in vitro of conazole antifungals used as pesticides and pharmaceuticals. Reproductive Toxicology, 30(4), 573–582. https://doi.org/10.1016/j.reprotox.2010.07.009
Lamont, K. R., and Tindall, D. J. (2010). Androgen Regulation of Gene Expression. Adv. Cancer Res. 107, 137–162. doi:10.1016/S0065-230X(10)07005-3.
Mahler, C., Verhelst, J., and Denis, L. (1998). Clinical pharmacokinetics of the antiandrogens and their efficacy in prostate cancer. Clin. Pharmacokinet. 34, 405–417. doi:10.2165/00003088-199834050-00005/METRICS.
Marcelli, M., Stenoien, D. L., Szafran, A. T., Simeoni, S., Agoulnik, I. U., Weigel, N. L., Moran, T., Mikic, I., Price, J. H., & Mancini, M. A. (2006). Quantifying effects of ligands on androgen receptor nuclear translocation, intranuclear dynamics, and solubility. Journal of Cellular Biochemistry, 98(4), 770–788. https://doi.org/10.1002/jcb.20593
OECD (2020). Test No. 458: Stably Transfected Human Androgen Receptor Transcriptional Activation Assay for Detection of Androgenic Agonist and Antagonist Activity of Chemicals. OECD Guide. Paris: OECD Publishing doi:10.1787/9789264264366-en.
Ogino, Y., Miyagawa, S., Katoh, H., Prins, G. S., Iguchi, T., & Yamada, G. (2011). Essential functions of androgen signaling emerged through the developmental analysis of vertebrate sex characteristics. Evolution & Development, 13(3), 315–325. https://doi.org/10.1111/j.1525-142X.2011.00482.x
Pedersen, E. B., Christiansen, S., & Svingen, T. (2022). AOP key event relationship report: Linking androgen receptor antagonism with nipple retention. Current Research in Toxicology, 3, 100085. https://doi.org/10.1016/j.crtox.2022.100085
Prizant, H., Gleicher, N., & Sen, A. (2014). Androgen actions in the ovary: balance is key. Journal of Endocrinology, 222(3), R141–R151. https://doi.org/10.1530/JOE-14-0296
Rey, R. A. (2021). The Role of Androgen Signaling in Male Sexual Development at Puberty. Endocrinology, 162(2). https://doi.org/10.1210/endocr/bqaa215
Roy, A. K., Tyagi, R. K., Song, C. S., Lavrovsky, Y., Ahn, S. C., Oh, T. S., & Chatterjee, B. (2001). Androgen receptor: Structural domains and functional dynamics after ligand-receptor interaction. Annals of the New York Academy of Sciences, 949, 44–57. https://doi.org/10.1111/j.1749-6632.2001.tb04001.x
Sonneveld, E. (2005). Development of Androgen- and Estrogen-Responsive Bioassays, Members of a Panel of Human Cell Line-Based Highly Selective Steroid-Responsive Bioassays. Toxicological Sciences, 83(1), 136–148. https://doi.org/10.1093/toxsci/kfi005
Szafran, A. T., Szwarc, M., Marcelli, M., & Mancini, M. A. (2008). Androgen Receptor Functional Analyses by High Throughput Imaging: Determination of Ligand, Cell Cycle, and Mutation-Specific Effects. PLoS ONE, 3(11), e3605. https://doi.org/10.1371/journal.pone.0003605
Walters, K. A., Simanainen, U., & Handelsman, D. J. (2010). Molecular insights into androgen actions in male and female reproductive function from androgen receptor knockout models. In Human Reproduction Update (Vol. 16, Issue 5, pp. 543–558). Hum Reprod Update. https://doi.org/10.1093/humupd/dmq003
William H. Walker. (2021). Androgen Actions in the Testis and the Regulation of Spermatogenesis. In Advances in Experimental Medicine and Biology: Vol. volume 1381 (pp. 175–203).
Yeh, S., Miyamoto, H., & Chang, C. (1997). ARA70 and androgenic activity of hydroxyflutamide Hydroxyflutamide may not always be a pure antiandrogen (Vol. 349).
Relationship: 2124: Decrease, AR activation leads to Altered, Transcription of genes by the AR
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| Androgen receptor (AR) antagonism leading to nipple retention (NR) in male (mammalian) offspring | adjacent | Moderate | Moderate |
| Androgen receptor (AR) antagonism leading to decreased fertility in females | adjacent | High | Moderate |
| 5α-reductase inhibition leading to short anogenital distance (AGD) in male (mammalian) offspring | adjacent | High | |
| Androgen receptor (AR) antagonism leading to short anogenital distance (AGD) in male (mammalian) offspring | adjacent | Moderate | |
| Decreased testosterone synthesis leading to short anogenital distance (AGD) in male (mammalian) offspring | adjacent | Moderate | Low |
| Decreased testosterone synthesis leading to hypospadias in male (mammalian) offspring | adjacent | ||
| 5α-reductase inhibition leading to hypospadias in male (mammalian) offspring | adjacent | ||
| 5α-reductase inhibition leading to increased nipple retention (NR) in male (rodent) offspring | adjacent |
Evidence Supporting Applicability of this Relationship
| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| mammals | mammals | High | NCBI |
| Life Stage | Evidence |
|---|---|
| During development and at adulthood | High |
| Sex | Evidence |
|---|---|
| Mixed | High |
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
Biological PlausibilityThe 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).
Empirical EvidenceThe 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).
Uncertainties and InconsistenciesAR 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
Response-response relationshipThere 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).
Time-scaleAR 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.
Known modulating factors| Modulating Factor (MF) | MF Specification | Effect(s) on the KER | Reference(s) |
|---|---|---|---|
| Age | AR expression in aging male rats | Tissue-specific alterations in AR activity with aging | (Supakar et al. 1993; Wu, Lin, and Gore 2009) |
| Genotype | Number of CAG repeats in the first exon of AR | Decreased AR activation with increased number of CAGs |
(Tut et al. 1997; Chamberlain et al. 1994) |
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.
Bennesch, Marcela A., and Didier Picard. 2015. “Minireview: Tipping the Balance: Ligand-Independent Activation of Steroid Receptors.” Molecular Endocrinology 29(3):349–63.
Chamberlain, Nancy L., Erika D. Driverand, and Roger L. Miesfeldi. 1994. The Length and Location of CAG Trinucleotide Repeats in the Androgen Receptor N-Terminal Domain Affect Transactivation Function. Vol. 22.
Denolet, Evi, Karel De Gendt, Joke Allemeersch, Kristof Engelen, Kathleen Marchal, Paul Van Hummelen, Karen A. L. Tan, Richard M. Sharpe, Philippa T. K. Saunders, Johannes V. Swinnen, and Guido Verhoeven. 2006. “The Effect of a Sertoli Cell-Selective Knockout of the Androgen Receptor on Testicular Gene Expression in Prepubertal Mice.” Molecular Endocrinology 20(2):321–34. doi: 10.1210/me.2005-0113.
Fan, Wuqiang, Toshihiko Yanase, Masatoshi Nomura, Taijiro Okabe, Kiminobu Goto, Takashi Sato, Hirotaka Kawano, Shigeaki Kato, and Hajime Nawata. 2005. Androgen Receptor Null Male Mice Develop Late-Onset Obesity Caused by Decreased Energy Expenditure and Lipolytic Activity but Show Normal Insulin Sensitivity With High Adiponectin Secretion. Vol. 54.
Holterhus, Paul-Martin, Olaf Hiort, Janos Demeter, Patrick O. Brown, and James D. Brooks. 2003. Differential Gene-Expression Patterns in Genital Fibroblasts of Normal Males and 46,XY Females with Androgen Insensitivity Syndrome: Evidence for Early Programming Involving the Androgen Receptor. Vol. 4.
Ikeda, Yasumasa, Ken Ichi Aihara, Takashi Sato, Masashi Akaike, Masanori Yoshizumi, Yuki Suzaki, Yuki Izawa, Mitsunori Fujimura, Shunji Hashizume, Midori Kato, Shusuke Yagi, Toshiaki Tamaki, Hirotaka Kawano, Takahiro Matsumoto, Hiroyuki Azuma, Shigeaki Kato, and Toshio Matsumoto. 2005. “Androgen Receptor Gene Knockout Male Mice Exhibit Impaired Cardiac Growth and Exacerbation of Angiotensin II-Induced Cardiac Fibrosis.” Journal of Biological Chemistry 280(33):29661–66. doi: 10.1074/jbc.M411694200.
Jin, Hong Jian, Jung Kim, and Jindan Yu. 2013. “Androgen Receptor Genomic Regulation.” Translational Andrology and Urology 2(3):158–77.
Kang, Zhigang, Asta Pirskanen, Olli A. Jänne, and Jorma J. Palvimo. 2002. “Involvement of Proteasome in the Dynamic Assembly of the Androgen Receptor Transcription Complex.” Journal of Biological Chemistry 277(50):48366–71. doi: 10.1074/jbc.M209074200.
Kanno, Yuichiro, Nao Saito, Ryota Saito, Tomohiro Kosuge, Ryota Shizu, Tomofumi Yatsu, Takuomi Hosaka, Kiyomitsu Nemoto, Keisuke Kato, and Kouichi Yoshinari. 2022. “Differential DNA-Binding and Cofactor Recruitment Are Possible Determinants of the Synthetic Steroid YK11-Dependent Gene Expression by Androgen Receptor in Breast Cancer MDA-MB 453 Cells.” Experimental Cell Research 419(2). doi: 10.1016/j.yexcr.2022.113333.
Karlsson, Sara A., Erik Studer, Petronella Kettunen, and Lars Westberg. 2016. “Neural Androgen Receptors Modulate Gene Expression and Social Recognition but Not Social Investigation.” Frontiers in Behavioral Neuroscience 10(MAR). doi: 10.3389/fnbeh.2016.00041.
Knapczyk-Stwora, Katarzyna, Anna Nynca, Renata E. Ciereszko, Lukasz Paukszto, Jan P. Jastrzebski, Elzbieta Czaja, Patrycja Witek, Marek Koziorowski, and Maria Slomczynska. 2019. “Flutamide-Induced Alterations in Transcriptional Profiling of Neonatal Porcine Ovaries.” Journal of Animal Science and Biotechnology 10(1):1–15. doi: 10.1186/s40104-019-0340-y.
Lamont, K. R., and Tindall, D. J. (2010). Androgen Regulation of Gene Expression. Adv. Cancer Res. 107, 137–162. doi:10.1016/S0065-230X(10)07005-3.
MacLean, Helen E., W. S. Maria Chiu, Amanda J. Notini, Anna-Maree Axell, Rachel A. Davey, Julie F. McManus, Cathy Ma, David R. Plant, Gordon S. Lynch, and Jeffrey D. Zajac. 2008. “ Impaired Skeletal Muscle Development and Function in Male, but Not Female, Genomic Androgen Receptor Knockout Mice .” The FASEB Journal 22(8):2676–89. doi: 10.1096/fj.08-105726.
Maiuri, Paolo, Anna Knezevich, Alex De Marco, Davide Mazza, Anna Kula, Jim G. McNally, and Alessandro Marcello. 2011. “Fast Transcription Rates of RNA Polymerase II in Human Cells.” EMBO Reports 12(12):1280–85. doi: 10.1038/embor.2011.196.
Mora, Gloria R., and Virendra B. Mahesh. 1999. Autoregulation of the Androgen Receptor at the Translational Level: Testosterone Induces Accumulation of Androgen Receptor MRNA in the Rat Ventral Prostate Polyribosomes.
Peng, Yajie, Hui Zhu, Bing Han, Yue Xu, Xuemeng Liu, Huaidong Song, and Jie Qiao. 2021. “Identification of Potential Genes in Pathogenesis and Diagnostic Value Analysis of Partial Androgen Insensitivity Syndrome Using Bioinformatics Analysis.” Frontiers in Endocrinology 12. doi: 10.3389/fendo.2021.731107.
Rana, Kesha, Barbara C. Fam, Michele V Clarke, Tammy P. S. Pang, Jeffrey D. Zajac, and Helen E. Maclean. 2011. “Increased Adiposity in DNA Binding-Dependent Androgen Receptor Knockout Male Mice Associated with Decreased Voluntary Activity and Not Insulin Resistance.” Am J Physiol Endocrinol Me-Tab 301:767–78. doi: 10.1152/ajpendo.00584.2010.-In.
Roy, Arun K., Rakesh K. Tyagi, Chung S. Song, Yan Lavrovsky, Soon C. Ahn, Tae Sung Oh, and Bandana Chatterjee. 2001. “Androgen Receptor: Structural Domains and Functional Dynamics after Ligand-Receptor Interaction.” Pp. 44–57 in Annals of the New York Academy of Sciences. Vol. 949. New York Academy of Sciences.
Russell, Patricia K., Michele V. Clarke, Jarrod P. Skinner, Tammy P. S. Pang, Jeffrey D. Zajac, and Rachel A. Davey. 2012. “Identification of Gene Pathways Altered by Deletion of the Androgen Receptor Specifically in Mineralizing Osteoblasts and Osteocytes in Mice.” Journal of Molecular Endocrinology 49(1):1–10. doi: 10.1530/JME-12-0014.
Shiina, Hiroko, Takahiro Matsumoto, Takashi Sato, Katsuhide Igarashi, Junko Miyamoto, Sayuri Takemasa, Matomo Sakari, Ichiro Takada, Takashi Nakamura, Daniel Metzger, Pierre Chambon, Jun Kanno, Hiroyuki Yoshikawa, and Shigeaki Kato. 2006. Premature Ovarian Failure in Androgen Receptor-Deficient Mice. Vol. 103.
Supakar, P. C., C. S. Song, M. H. Jung, M. A. Slomczynska, J. M. Kim, R. L. Vellanoweth, B. Chatterjee, and A. K. Roy. 1993. “A Novel Regulatory Element Associated with Age-Dependent Expression of the Rat Androgen Receptor Gene.” Journal of Biological Chemistry 268(35):26400–408. doi: 10.1016/s0021-9258(19)74328-2.
Tut, Thein G., Farid J. Ghadessy, M. A. Trifiro, L. Pinsky, and E. L. Yong. 1997. Long Polyglutamine Tracts in the Androgen Receptor Are Associated with Reduced Trans-Activation, Impaired Sperm Production, and Male Infertility*. Vol. 82.
Wang, Ruey Sheng, Shuyuan Yeh, Lu Min Chen, Hung Yun Lin, Caixia Zhang, Jing Ni, Cheng Chia Wu, P. Anthony Di Sant’Agnese, Karen L. DeMesy-Bentley, Chii Ruey Tzeng, and Chawnshang Chang. 2006. “Androgen Receptor in Sertoli Cell Is Essential for Germ Cell Nursery and Junctional Complex Formation in Mouse Testes.” Endocrinology 147(12):5624–33. doi: 10.1210/en.2006-0138.
Welsh, M., L. Moffat, K. Belling, L. R. de França, T. M. Segatelli, P. T. K. Saunders, R. M. Sharpe, and L. B. Smith. 2012. “Androgen Receptor Signalling in Peritubular Myoid Cells Is Essential for Normal Differentiation and Function of Adult Leydig Cells.” International Journal of Andrology 35(1):25–40. doi: 10.1111/j.1365-2605.2011.01150.x.
Willems, Ariane, Sergio R. Batlouni, Arantza Esnal, Johannes V. Swinnen, Philippa T. K. Saunders, Richard M. Sharpe, Luiz R. França, Karel de Gendt, and Guido Verhoeven. 2010. “Selective Ablation of the Androgen Receptor in Mouse Sertoli Cells Affects Sertoli Cell Maturation, Barrier Formation and Cytoskeletal Development.” PLoS ONE 5(11). doi: 10.1371/journal.pone.0014168.
Wu, D. I., Grace Lin, and Andrea C. Gore. 2009. “Age-Related Changes in Hypothalamic Androgen Receptor and Estrogen Receptor in Male Rats.” The Journal of Comparative Neurology 512:688–701. doi: 10.1002/cne.21925.
Yu, I. Chen, Hung Yun Lin, Ning Chun Liu, Ruey Shen Wang, Janet D. Sparks, Shuyuan Yeh, and Chawnshang Chang. 2008. “Hyperleptinemia without Obesity in Male Mice Lacking Androgen Receptor in Adipose Tissue.” Endocrinology 149(5):2361–68. doi: 10.1210/en.2007-0516.
Yu, Shengqiang, Chiuan Ren Yeh, Yuanjie Niu, Hong Chiang Chang, Yu Chieh Tsai, Harold L. Moses, Chih Rong Shyr, Chawnshang Chang, and Shuyuan Yeh. 2012. “Altered Prostate Epithelial Development in Mice Lacking the Androgen Receptor in Stromal Fibroblasts.” Prostate 72(4):437–49. doi: 10.1002/pros.21445.
Zhang, Caixia, Shuyuan Yeh, Yen-Ta Chen, Cheng-Chia Wu, Kuang-Hsiang Chuang, Hung-Yun Lin, Ruey-Sheng Wang, Yu-Jia Chang, Chamindrani Mendis-Handagama, Liquan Hu, Henry Lardy, Chawnshang Chang, and † † George. 2006. Oligozoospermia with Normal Fertility in Male Mice Lacking the Androgen Receptor in Testis Peritubular Myoid Cells.
Zhou, Wei, Gensheng Wang, Christopher L. Small, Zhilin Liu, Connie C. Weng, Lizhong Yang, Michael D. Griswold, and Marvin L. Meistrich. 2011. “Erratum: Gene Expression Alterations by Conditional Knockout of Androgen Receptor in Adult Sertoli Cells of Utp14bjsd/Jsd (Jsd) Mice (Biology of Reproduction (2010) 83, (759-766) DOI: 10.1095/Biolreprod.110.085472).” Biology of Reproduction 84(2):400–408.
List of Non Adjacent Key Event Relationships
Relationship: 2820: Decrease, AR activation leads to AGD, decreased
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| 5α-reductase inhibition leading to short anogenital distance (AGD) in male (mammalian) offspring | non-adjacent | High | |
| Androgen receptor (AR) antagonism leading to short anogenital distance (AGD) in male (mammalian) offspring | non-adjacent | High | |
| Decreased testosterone synthesis leading to short anogenital distance (AGD) in male (mammalian) offspring | non-adjacent | High | Moderate |
Evidence Supporting Applicability of this Relationship
| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| human, mouse, rat | human, mouse, rat | High | NCBI |
| Life Stage | Evidence |
|---|---|
| Fetal to Parturition | High |
| Sex | Evidence |
|---|---|
| Male | High |
Fetal masculinization including the AGD is regulated by androgens interacting with the AR in all mammals, including humans (Murashima et al., 2015; Thankamony et al., 2016), although, the size of the AGD and difference between the sexes vary between species. A large number of studies exist showing that fetal exposure to anti-androgens causes shortened AGD in male rats and mice (Schwartz et al., 2019, see also Table 2). Some epidemiological studies find associations between exposure to anti-androgenic compounds and shorter AGD in boys (Thankamony et al., 2016). However, the associations are not very clear and confidence in the data is limited by conflicting results, possibly due to differences in study design and methods for exposure measurements and analyses. Nevertheless, the KER is considered applicable to humans, based on current understanding of the role of AR activation in fetal masculinization.
Life stage
Programming of the AGD occurs during the masculinization programming window in fetal life. This takes place in rats around embryonic days 15.5-19.5 (GD16-20) and likely gestation weeks 8-14 in humans (Welsh et al., 2008). It should be mentioned that though AGD is believed to be relatively stable throughout life, it can be responsive to postnatal changes in androgen levels (Schwartz et al., 2019).
Sex
Data presented in this KER support that disruption of androgen action during fetal life can lead to a short AGD in male offspring. While exposure to chemicals during fetal life can also shorten female AGD, the biological significance and the mechanism driving the effect is unknown (Schwartz et al., 2019).
Key Event Relationship Description
This KER refers to a decrease in androgen receptor (AR) activation during fetal development leading to decreased anogenital distance (AGD) in male offspring.
It should be noted that the upstream Key Event (KE) ‘decrease, androgen receptor activation’ (KE-1614 in AOP Wiki) specifically focuses on decreased activation of the androgen receptor in vivo, while most methods that can be used to measure AR activity are carried out in vitro. Indirect information about this KE may for example be provided from assays showing in vitro AR antagonism, decreased in vitro or in vivo testosterone production/levels or decreased in vitro or in vivo dihydrotestosterone (DHT) production/levels.
Evidence Supporting this KER
Biological PlausibilityThe biological plausibility for this KER is judged to be high based on the following:
- Sexual differentiation happens in fetal life. The testes are developed and start to produce testosterone that is converted in other tissues by the enzyme 5-alpha-reductase to the more potent androgen dihydrotestosterone (DHT). Both hormones bind and activate the nuclear receptor and transcription factor AR that in turn drives masculinization of the male fetus (Welsh et al., 2014; Schwartz et. al, 2019).
- Fetal masculinization depends on activation of androgen signaling during a critical time window, the masculinization programming window (MPW), from gestational day (GD) 15.5-18.5 in rats, 14.5-16.5 in mice and presumably gestation weeks (GWs) 8-14 in humans (Welsh et al., 2008; Amato et al., 2022). The onset of AR expression in the tissues of the reproductive tract follows the timing of the MPW (Welsh et al., 2008).
- The fetal masculinization process involves a range of tissues and organs, including the perineum. Perineum length can be measured as the AGD, which is the distance between the anus and the genitalia. The AGD is approximately twice as long in male as in female newborn rodents and humans (Schwartz et al., 2019).
- Male AR knockout mice present shorter AGD than wildtype males, so short that it is indistinguishable from wildtype female littermates (Yeh et al., 2002, Sato et al., 2004).
- In human males, mutations decreasing AR activity also lead to feminization. One example is the androgen insensitivity syndrome (AIS), where mutations in the AR lead to an impaired or abolished response to androgens, and thereby some degree of feminization of XY individuals and even XY sex reversal in individuals with complete AIS (CAIS) (Thankamony et al., 2016; Hughes et al., 2012; Crouch et al., 2011). XY individuals with CAIS present as women with internally placed testes. A study showed that the clitoral to urethral distance in these individuals was similar to a control group of women, but it is not clear whether this measurement can work as a proxy for measuring the AGD (Thankamony et al 2016, Crouch 2011). Unfortunately, it seems the AGD has not at present been measured in CAIS individuals. Another example is human males lacking 5-alpha-reductase, also presenting female-like genitalia (Batista & Mendonca, 2022).
- The detailed mechanism by which androgens regulate the AGD is not known but it is hypothesized that the AGD is influenced by the size of the levator-ani and bulbocavernosus (LABC) muscle complex in the perineum. The growth of this complex is stimulated by AR activation, it is sexually dimorphic and larger in males than in females and (Schwartz et al., 2019). AR is required for the development of the LABC complex as demonstrated by AR general and muscle specific knockout mice. AR is expressed in non-myocytic cells in the LABC complex, starting at E15.5 in mice, and knockout of AR in these cells results in defects in the muscle formation (Ipulan et al., 2016;). Differential gene expression profiles in the perineum of male and female rats as well as in antiandrogen-exposed male rats have been identified providing further mechanistic understanding (Schwartz et al, 2019; Draskau et al, 2022).
Empirical EvidenceAnimal in vivo data
The empirical support from studies in animals for this KER is overall judged as high.
It should be noted that the KE decreased androgen receptor activation (KE-1614 in AOP Wiki) specifically focuses on decreased activation of the androgen receptor in vivo, with no methods currently available to measure this. Examples of assays that provide indirect information about KE-1614 are described in upstream MIE/KEs.
The evidence for the upstream KE is mainly based on data from in vitro assays (AR antagonism or 5-alpha-reductase inhibition in vitro) whereas the evidence for the downstream KE is based on in vivo studies, and there is generally not evidence for both KEs from the same study. However, decreased testosterone levels can be measured in vivo, and Borch et al., 2004 measured the effect of developmental DEHP exposure on both testosterone levels and AGD (see section about “Dose concordance”).
The empirical animal evidence for the five substances is summarized in table 3.
Table 3. Summary of empirical evidence for decreased androgen receptor activation, leading to decreased male AGD. References for the studies supporting the empirical evidence are found in section “Evidence for decreased AR activation (KE1614) by flutamide, procymidone, and vinclozolin, finasteride and DEHP” and in table 2.
|
Upstream effect |
Downstream effect |
|
|
Flutamide |
AR antagonism in in vitro assay receptor binding and transactivation assays
|
Decreased male AGD after prenatal exposure in studies in rat
|
|
Procymidone |
AR antagonism in in vitro assay receptor binding and transactivation assays
|
Decreased male AGD after prenatal exposure in studies in rat
|
|
Vinclozolin |
AR antagonism in in vitro assay receptor binding and transactivation assays
|
Decreased male AGD after prenatal exposure in studies in rat and mouse
|
|
Finasteride |
Inhibition of 5-alpha-reductase enzyme in in vitro assays
|
Decreased male AGD after prenatal exposure in studies in rat
|
|
DEHP |
Reduced production of testosterone in fetal testis measured in ex vivo testis assays, reduced testosterone levels in testis and reduced fetal plasma or serum testosterone levels
|
Decreased male AGD after prenatal exposure in studies in rat
|
From table 3, it can be deducted that fetal exposure to substances known to decrease androgen receptor activation through antagonism of the AR (vinclozolin, procymidone, flutamide), inhibition of testosterone synthesis (DEHP) or inhibition of conversion of testosterone to DHT (finasteride), results in decreased AGD in rat and mouse male offspring.
Flutamide, a pharmaceutical, binds the AR and inhibits the receptor activity, thereby acting as an AR antagonist. It has been used as an antiandrogen for treatment of prostate cancer and is used as a reference chemical for antiandrogenic activity in the AR transactivation assays in the OECD test guideline No 458 (Goldspiel & Kohler, 1990; Labrie, 1993; OECD, 2023; Simard et al., 1986).
Procymidone and vinclozolin are fungicides that have been shown to be AR antagonists. Procymidone binds to the AR and inhibits the agonist binding as shown in AR binding assays using rat prostate cytosol (Hosokawa et al., 1993) or AR transfected COS cells (Ostby et al., 1999). Procymidone also inhibits agonist activated transcription in AR reporter assays (Hass et al., 2012; Kojima et al., 2004; Orton et al., 2011; Ostby et al., 1999; Scholze et al., 2020). Vinclozolin binds to the AR and inhibits the agonist binding as shown in AR binding assays using rat epididymis cytosol (Kelce et al., 1997) or AR transfected COS-1 cells (Wong et al., 1995).
Vinclozolin also inhibits agonist activated transcription in AR reporter assays (Euling et al, 2002; Kojima et al., 2004; Molina-Molina et al., 2006; Orton et al., 2011; Scholze et al., 2020; Shimamura et al., 2002; Wong et al., 1995). Finasteride is a pharmaceutical that inhibits the 5-alpha-reductase enzyme that converts testosterone to DHT. Finasteride is used to treat benign prostatic hypertrophy (Andersson & Russel, 1990; Rittmaster & Wood, 1994; Stoner, 1990).
Prenatal exposure to DEHP in rats results in reduced production of testosterone in fetal testis measured in ex vivo testis assays, reduced testosterone levels in testis and reduced fetal plasma or serum testosterone levels (Borch et al., 2004; Borch et al., 2006; Culty et al., 2008; Hannas et al., 2011; Hannas et al., 2012; Klinefelter et al., 2012; Parks et al., 2000; Wilson et al., 2004; Wilson et al., 2007; Vo et al., 2009). Two studies don’t show an effect on testosterone levels in testis or fetal plasma testosterone levels, respectively (Andrade et al., 2006; Borch et al., 2006). The precise underlying mechanism is presently unknown.
Evidence for decreased AGD in males (KE1688) by prenatal exposure to flutamide, procymidone, vinclozolin, finasteride and DEHP
All datasets that were used for the weight of evidence assessment were judged as reliable without or with restriction. The majority of datasets assessed showed a decreased male AGD. The conclusion was that the level of confidence was strong for all five substances. The studies are summarized in table 4.
Empirical evidence for the included substances
Table 4. Empirical evidence for decreased AGD in males (KE1688) by prenatal exposure to flutamide, procymidone, vinclozolin, finasteride and DEHP. *One dose only.
>>>>>TABLE 4<<<<<
|
Species |
Exposure window |
Measurement timepoint |
NOAEL (mg/kg bw/day) |
LOAEL (mg/kg bw/day) |
Reference |
|
Flutamide |
|||||
|
rat |
GD12-21 |
PND1 and PND100 |
No |
6.25 |
McIntyre et al., 2001 |
|
rat |
GD16, 17, 18 or 19 |
PND1 and PND100 |
--* |
50 |
Foster & Harris, 2005 |
|
rat |
GD7-21 |
PND1 |
No |
0.5 |
Hass et al., 2007 |
|
rat |
GD6-17 + GD16-21 |
GD21 |
No |
3 |
Goto et al., 2004 |
|
rat |
GD6-PND4 |
PND4 |
0.4 |
2 |
Yamasaki et al., 2005 |
|
rat |
GD6-PND1 |
PND1 |
0.25 |
2.5 |
Fussell et al., 2015 |
|
rat |
GD13-20 |
PND4 and PND23 |
--* |
20 |
Kita et al., 2016 |
|
rat |
GD11-21 |
PND 14, 21 and 120 |
--* |
5 mg per rat |
Casto et al., 2003 |
|
Procymidone |
|||||
|
rat |
GD7-PND16 |
at birth, GD22-24 |
No |
12.5 |
Hass et al., 2012 |
|
rat |
GD7-PND16 |
at birth, GD22-24 |
10 |
25 |
Hass et al., 2007 |
|
rabbit |
GD6-28 |
GD29 |
125 |
No effect |
Inawaka et al., 2010 |
|
rat |
GD14-PND3 |
PND2 |
No |
25 |
Ostby et al., 1999 |
|
Vinclozolin |
|||||
|
Rat |
GD16-17 + GD18-19 |
PND1 |
--* |
400 |
Wolf et al., 2000 |
|
Rat |
GD14-19 |
PND1 |
No |
200 |
Wolf et al., 2000 |
|
Rat |
GD7-21 |
PND1 |
5 |
10 |
Hass et al., 2007 |
|
Mouse |
GD10-18 |
PND1 and 7 |
--* |
100 |
Shimamura et al., 2002 |
|
Rat |
GD4-PND3 |
PND2 |
No |
3.125 |
Gray et al., 1994 |
|
Finasteride |
|||||
|
rat |
GD12-21 |
PND1 and PND90 |
No |
0.01 |
Bowman et al., 2003 |
|
rat |
GD7-21 |
PND0 |
0.01 |
0.1 |
Christiansen et al., 2009 |
|
rat |
GD15-21 |
PND1 |
0.0003 |
0.03 |
Clark et al., 1993 |
|
rat |
GD15-21 |
PND22 and PND114-117 |
0.03 |
3 |
Clark et al., 1993 |
|
rat |
GD12-21 |
PND1 and PND90 |
--* |
10 |
Martinez et al., 2011 |
The biggest relevant epidemiological dataset was identified on associations between DEHP and AGD.
Six prospective cohort studies and one cross-sectional study on the association between maternal DEHP metabolites and length of AGD (anopenile distance (APD) and anoscrotal distance (ASD)) in boys were assessed as reliable without or with restriction. Decreased AGD (anopenile distance (APD) and/or anoscrotal distance (ASD)) was observed in three prospective cohort studies (Martino-Adrade et al., 2016; Swan et al., 2005 reviewed and updated in Swan 2008; Wenzel et al., 2018). In contrast, no significant association was observed in three other prospective cohort studies (Arbuckle et al., 2018; Henriksen et al., 2023; Jensen et al., 2016) and the cross-sectional study (Sunman et al., 2019). This inconsistency introduces a level of uncertainty regarding the overall association. Therefore, the level of confidence was judged as weak.
Dose concordance
Dose concordance is challenging to assess for this KER since in vivo AR activity is currently not possible to measure, but only can be informed indirectly by measures of upstream events.
However, some studies provide useful information that support dose concordance between the KEs.
In a publication by Borch et al., rats were exposed in utero to DEHP at GD7-21. Fetal testosterone levels in testes and serum and testosterone production in fetal testes ex vivo were investigated at GD21, whereas AGD was investigated at PND3. The LOAELs for reduced testosterone production in ex vivo fetal testes and reduced testosterone levels in fetal testes were 300 mg/kg/d, whereas the LOAEL for decreased AGD in male offspring was 750 mg/kg/d (Borch et al., 2004).
In a publication by Scholze et al, AR antagonism and decreased testosterone synthesis was quantitatively assessed (IC50) in vitro for a list of substances. In addition, internal concentrations in male fetuses and effects on AGD were measured after fetal exposure to the same substances. In utero exposure to all the substances lead to reduced AGDIndex (AGDI) in the exposed male offspring. Further, for all substances except Cyprodinil, the internal exposure levels in the fetuses leading to reduced AGD exceeded the IC50 levels observed in one or both of the in vitro assays.
Three different doses of linuron exposure were included. The medium exposure dose led to a higher level of internal exposure and a higher degree of AGDI reduction than the low dose. AGDI could not be determined in the highest dose due to maternal toxicity (Scholze et al., 2020).
Temporal concordance
Temporal concordance can only be considered from a theoretical perspective since the downstream event, decreased AGD, is usually measured at GD21, PND0 or PND1 in rats, and due to the size of the fetuses is not feasible to measure at earlier timepoints.
Considering the biology, the upstream event – decreased AR activation in vivo – is foreseen to happen minutes to hours after exposure. If a substance decreases AR activation through inhibition of the AR, the upstream event is expected to happen immediately after exposure. If a substance decreases androgen receptor activation through inhibition of testosterone synthesis, the upstream event is expected to happen minutes to hours after the exposure, though it is uncertain exactly when the change will be big enough to be measurable. On the other hand, the downstream event – decreased AGD - is a measurement of relative growth of the perineal tissue, which is expected to take days in the developing fetus.
Uncertainties and InconsistenciesFor the model substances, there were some inconsistencies in the empirical evidence, but they could be explained by differences in study designs and uncertainties in measurements, see appendix 1: 8dh20j155i_FINAL_Appendix_KER2820_For_Wiki.pdf.
Species differences in effects of phthalates (including DEHP and DBP) on fetal testes testosterone production have been observed between humans, mice and rats. In human fetal testes exposed to DEHP or DBP in vitro or ex vivo, no suppression of testosterone production is observed, which contrasts observations in rat fetal testes under similar conditions. Also in mice, testosterone production in the fetal testes is unaffected by treatment with DEHP or DBP in vitro or in utero (Sharpe, 2020).
The species differences described above are specific for some phthalates and their interference with fetal testicular testosterone production. This uncertainty should not be reflected on other antiandrogenic substances, especially not those acting through other mechanisms of action.
The association between exposure to DEHP and reduced AGD in humans is judged to be weak, which may further support a species difference between rodents and humans, but it may also reflect the large uncertainties inherent in the epidemiological studies.
Observational epidemiological studies face challenges in proving cause-effect relationships as they cannot control conditions like experimental animal and in vitro studies. Human studies can identify associations between variables but cannot offer conclusive proof of causation (Lanzoni et al., 2019). Various study designs and statistical methods are employed to strengthen evidence within the inherent limitations of observational research (Song & Chung, 2010; Olier et al., 2023). Inconsistencies in epidemiological data arise from various factors, such as different methodologies used in exposure and outcome measurement and also in statistical analyses.
These differences collectively contribute to the complexity of interpreting and weighing the evidence in epidemiological research.
Quantitative Understanding of the Linkage
The quantitative understanding of the linkage is low. This is a consequence of it not being possible to measure the upstream and the downstream event in the same study.
Response-response relationshipIn one study, a quantitative model was developed to predict the decrease in AGD from in vitro AR antagonism or in vitro decreased testosterone synthesis. The authors conclude that predicting the effect on AGD in vivo based on the in vitro results is only possible on a qualitative level, but the model cannot predict AGD reductions quantitatively (Scholze et al., 2020).
Time-scaleAR activation operates on a time-scale of minutes. The AR is a ligand-activated nuclear receptor and transcription factor. Upon ligand binding a conformational change and subsequent dimerization of the AR takes place within 3-6 minutes (Schaufele et al., 2005). Nuclear translocation (Nightingale et al., 2003) 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).
For the downstream event, the time-scale for observing a measurable effect on growth of a tissue (in this case the perineum) is closer to days and weeks depending on species. For instance, in humans, the masculinization programming window is presumed to start around GW 8, while a sexual dimorphism of the AGD can first be observed from around GWs 11-13 (Thankamony et al., 2016) and reaches its maximum 2-fold difference around GWs 17-20 (Sharpe, 2020).
It has been demonstrated that exposure to flutamide for one day (Foster & Harris, 2005) or vinclozolin for two days (Wolf et al., 2000) during the sensitive window of exposure can elicit a detectable decrease in the AGD in male rat offspring.
Known modulating factorsA well established modulating factor is genetic variations in the AR which decrease the function of the receptor. For example, longer CAG repeat lengths have been associated with decreased AR activation (Tut et al 1997, Chamberlain et al 1994) and a shorter AGD in adult men (Eisenberg et al., 2013). Other modulating factors being discussed in the literature is maternal age and parity (Barrett et al., 2014), but these associations are only suggestive with more studies needed to confirm the associations (Barrett et al., 2014).
Known Feedforward/Feedback loops influencing this KERNot relevant for this KER.
References
Amato, Ciro M., Humphrey H-C. Yao, and Fei Zhao. “One Tool for Many Jobs: Divergent and Conserved Actions of Androgen Signaling in Male Internal Reproductive Tract and External Genitalia.” Frontiers in Endocrinology 13 (2022). https://www.frontiersin.org/articles/10.3389/fendo.2022.910964.
Andersson, S, and D W Russell. “Structural and Biochemical Properties of Cloned and Expressed Human and Rat Steroid 5 Alpha-Reductases.” Proceedings of the National Academy of Sciences 87, no. 10 (May 1990): 3640–44. https://doi.org/10.1073/pnas.87.10.3640.
Andrade AJ, Grande SW, Talsness CE, Grote K, Golombiewski A, Sterner-Kock A, and Chahoud I. “A Dose-Response Study Following in Utero and Lactational Exposure to Di-(2-Ethylhexyl) Phthalate (DEHP): Effects on Androgenic Status, Developmental Landmarks and Testicular Histology in Male Offspring Rats.” Toxicology 225, no. 1 (2006): 64–74. https://doi.org/10.1016/j.tox.2006.05.007.
Arbuckle TE, Agarwal A, MacPherson SH, Fraser WD, Sathyanarayana S, Ramsay T, Dodds L, et al. “Prenatal Exposure to Phthalates and Phenols and Infant Endocrine-Sensitive Outcomes: The MIREC Study.” Environment International 120 (2018): 572–83. https://doi.org/10.1016/j.envint.2018.08.034.
Barrett, E. S., L. E. Parlett, J. B. Redmon, and S. H. Swan. “Evidence for Sexually Dimorphic Associations Between Maternal Characteristics and Anogenital Distance, a Marker of Reproductive Development.” American Journal of Epidemiology 179, no. 1 (January 1, 2014): 57–66. https://doi.org/10.1093/aje/kwt220.
Batista, Rafael L., and Berenice B. Mendonca. “The Molecular Basis of 5α-Reductase Type 2 Deficiency.” Sexual Development 16, no. 2–3 (2022): 171–83. https://doi.org/10.1159/000525119.
Borch J, Ladefoged O, Hass U, and Vinggaard AM. “Steroidogenesis in Fetal Male Rats Is Reduced by DEHP and DINP, but Endocrine Effects of DEHP Are Not Modulated by DEHA in Fetal, Prepubertal and Adult Male Rats.” Reproductive Toxicology (Elmsford, N.Y.) 18, no. 1 (2004): 53–61. https://doi.org/10.1016/j.reprotox.2003.10.011.
Borch, Julie, Stine Broeng Metzdorff, Anne Marie Vinggaard, Leon Brokken, and Majken Dalgaard. “Mechanisms Underlying the Anti-Androgenic Effects of Diethylhexyl Phthalate in Fetal Rat Testis.” Toxicology 223, no. 1–2 (June 2006): 144–55. https://doi.org/10.1016/j.tox.2006.03.015.
Botelho, Giuliana G. K., Aedra C. Bufalo, Ana Claudia Boareto, Juliane C. Muller, Rosana N. Morais, Anderson J. Martino-Andrade, Karen R. Lemos, and Paulo R. Dalsenter. “Vitamin C and Resveratrol Supplementation to Rat Dams Treated with Di(2-Ethylhexyl)Phthalate: Impact on Reproductive and Oxidative Stress End Points in Male Offspring.” Archives of Environmental Contamination and Toxicology 57, no. 4 (November 2009): 785–93. https://doi.org/10.1007/s00244-009-9385-9.
Bowman, C. J., N. J. Barlow, K. J. Turner, D. G. Wallace, and P. M. D. Foster. “Effects of in Utero Exposure to Finasteride on Androgen-Dependent Reproductive Development in the Male Rat.” Toxicological Sciences 74, no. 2 (August 1, 2003): 393–406. https://doi.org/10.1093/toxsci/kfg128.
Casto, J, O Ward, and A Bartke. “Play, Copulation, Anatomy, and Testosterone in Gonadally Intact Male Rats Prenatally Exposed to Flutamide.” Physiology & Behavior 79, no. 4–5 (September 2003): 633–41. https://doi.org/10.1016/S0031-9384(03)00120-3.
Chamberlain, Nancy L., Erika D. Driver, and Roger L. Miesfeld. “The Length and Location of CAG Trinucleotide Repeats in the Androgen Receptor N-Terminal Domain Affect Transactivation Function.” Nucleic Acids Research 22, no. 15 (1994): 3181–86. https://doi.org/10.1093/nar/22.15.3181.
Christiansen, Sofie, Julie Boberg, Marta Axelstad, Majken Dalgaard, Anne Marie Vinggaard, Stine Broeng Metzdorff, and Ulla Hass. “Low-Dose Perinatal Exposure to Di(2-Ethylhexyl) Phthalate Induces Anti-Androgenic Effects in Male Rats.” Reproductive Toxicology 30, no. 2 (September 2010): 313–21. https://doi.org/10.1016/j.reprotox.2010.04.005.
Christiansen, Sofie, Martin Scholze, Majken Dalgaard, Anne Marie Vinggaard, Marta Axelstad, Andreas Kortenkamp, and Ulla Hass. “Synergistic Disruption of External Male Sex Organ Development by a Mixture of Four Antiandrogens.” Environmental Health Perspectives 117, no. 12 (December 2009): 1839–46. https://doi.org/10.1289/ehp.0900689.
Clark, R.L., C.A. Anderson, S. Prahalada, R.T. Robertson, E.A. Lochry, Y.M. Leonard, J.L. Stevens, and A.M. Hoberman. “Critical Developmental Periods for Effects on Male Rat Genitalia Induced by Finasteride, a 5α-Reductase Inhibitor.” Toxicology and Applied Pharmacology 119, no. 1 (March 1993): 34–40. https://doi.org/10.1006/taap.1993.1041.
Colbert NK, Pelletier NC, Cote JM, Concannon JB, Jurdak NA, Minott SB, and Markowski VP. “Perinatal Exposure to Low Levels of the Environmental Antiandrogen Vinclozolin Alters Sex-Differentiated Social Play and Sexual Behaviors in the Rat.” Environmental Health Perspectives 113, no. 6 (2005): 700–707. https://doi.org/10.1289/ehp.7509.
Crouch, Ns, Lina Michala, Sm Creighton, and Gs Conway. “Androgen-Dependent Measurements of Female Genitalia in Women with Complete Androgen Insensitivity Syndrome: Measurements of Female Genitalia in Women with Complete Androgen Insensitivity Syndrome.” BJOG: An International Journal of Obstetrics & Gynaecology 118, no. 1 (January 2011): 84–87. https://doi.org/10.1111/j.1471-0528.2010.02778.x.
Culty, Martine, Raphael Thuillier, Wenping Li, Yan Wang, Daniel B. Martinez-Arguelles, Carolina Gesteira Benjamin, Kostantinos M. Triantafilou, Barry R. Zirkin, and Vassilios Papadopoulos. “In Utero Exposure to Di-(2-Ethylhexyl) Phthalate Exerts Both Short-Term and Long-Lasting Suppressive Effects on Testosterone Production in the Rat1.” Biology of Reproduction 78, no. 6 (June 1, 2008): 1018–28. https://doi.org/10.1095/biolreprod.107.065649.
Do, Rylee Phuong, Richard W. Stahlhut, Davide Ponzi, Frederick S. Vom Saal, and Julia A. Taylor. “Non-Monotonic Dose Effects of in Utero Exposure to Di(2-Ethylhexyl) Phthalate (DEHP) on Testicular and Serum Testosterone and Anogenital Distance in Male Mouse Fetuses.” Reproductive Toxicology 34, no. 4 (December 2012): 614–21. https://doi.org/10.1016/j.reprotox.2012.09.006.
Draskau, Monica Kam, Anne-Sofie Ravn Ballegaard, Louise Ramhøj, Josephine Bowles, Terje Svingen, and Cassy M. Spiller. “AOP Key Event Relationship Report: Linking Decreased Retinoic Acid Levels with Disrupted Meiosis in Developing Oocytes.” Current Research in Toxicology 3 (2022): 100069. https://doi.org/10.1016/j.crtox.2022.100069.
Eisenberg ML, Hsieh TC, Pastuszak AW, McIntyre MG, Walters RC, Lamb DJ, and Lipshultz LI. “The Relationship between Anogenital Distance and the Androgen Receptor CAG Repeat Length.” Asian Journal of Andrology 15, no. 2 (2013): 286–89. https://doi.org/10.1038/aja.2012.126.
Euling, S. Y. “Response-Surface Modeling of the Effect of 5alpha-Dihydrotestosterone and Androgen Receptor Levels on the Response to the Androgen Antagonist Vinclozolin.” Toxicological Sciences 69, no. 2 (October 1, 2002): 332–43. https://doi.org/10.1093/toxsci/69.2.332.
Foster PM and Harris MW. “Changes in Androgen-Mediated Reproductive Development in Male Rat Offspring Following Exposure to a Single Oral Dose of Flutamide at Different Gestational Ages.” Toxicological Sciences : An Official Journal of the Society of Toxicology 85, no. 2 (2005): 1024–32. https://doi.org/10.1093/toxsci/kfi159.
Fussell, Karma C., Steffen Schneider, Roland Buesen, Sibylle Groeters, Volker Strauss, Stephanie Melching-Kollmuss, and Bennard Van Ravenzwaay. “Investigations of Putative Reproductive Toxicity of Low-Dose Exposures to Flutamide in Wistar Rats.” Archives of Toxicology 89, no. 12 (December 2015): 2385–2402. https://doi.org/10.1007/s00204-015-1622-6.
Goldspiel, Barry R., and David R. Kohler. “Flutamide: An Antiandrogen for Advanced Prostate Cancer.” DICP 24, no. 6 (June 1990): 616–23. https://doi.org/10.1177/106002809002400612.
Goto, Kazunori, Keiji Koizumi, Hitoshi Takaori, Yoshinobu Fujii, Yuko Furuyama, Osamu Saika, Hiroetsu Suzuki, Kenichi Saito, and Katsushi Suzuki. “EFFECTS OF FLUTAMIDE ON SEX MATURATION AND BEHAVIOR OF OFFSPRING BORN TO FEMALE RATS TREATED DURING LATE PREGNANCY.” The Journal of Toxicological Sciences 29, no. 5 (2004): 517–34. https://doi.org/10.2131/jts.29.517.
Gray, L. E., J Ostby, J Furr, M Price, D N Rao Veeramachaneni, and L Parks. “Perinatal Exposure to the Phthalates DEHP, BBP, and DINP, but Not DEP, DMP, or DOTP, Alters Sexual Differentiation of the Male Rat.” Toxicological Sciences 58, no. 2 (December 1, 2000): 350–65. https://doi.org/10.1093/toxsci/58.2.350.
Gray, L.E., J.S. Ostby, and W.R. Kelce. “Developmental Effects of an Environmental Antiandrogen: The Fungicide Vinclozolin Alters Sex Differentiation of the Male Rat.” Toxicology and Applied Pharmacology 129, no. 1 (November 1994): 46–52. https://doi.org/10.1006/taap.1994.1227.
Gray, Leon Earl, Norman J. Barlow, Kembra L. Howdeshell, Joseph S. Ostby, Johnathan R. Furr, and Clark L. Gray. “Transgenerational Effects of Di (2-Ethylhexyl) Phthalate in the Male CRL:CD(SD) Rat: Added Value of Assessing Multiple Offspring per Litter.” Toxicological Sciences 110, no. 2 (August 2009): 411–25. https://doi.org/10.1093/toxsci/kfp109.
Hannas, Bethany R., Christy S. Lambright, Johnathan Furr, Nicola Evans, Paul M. D. Foster, Earl L. Gray, and Vickie S. Wilson. “Genomic Biomarkers of Phthalate-Induced Male Reproductive Developmental Toxicity: A Targeted RT-PCR Array Approach for Defining Relative Potency.” Toxicological Sciences 125, no. 2 (February 2012): 544–57. https://doi.org/10.1093/toxsci/kfr315.
Hannas, Bethany R., Christy S. Lambright, Johnathan Furr, Kembra L. Howdeshell, Vickie S. Wilson, and Leon E. Gray. “Dose-Response Assessment of Fetal Testosterone Production and Gene Expression Levels in Rat Testes Following InUtero Exposure to Diethylhexyl Phthalate, Diisobutyl Phthalate, Diisoheptyl Phthalate, and Diisononyl Phthalate.” Toxicological Sciences 123, no. 1 (September 2011): 206–16. https://doi.org/10.1093/toxsci/kfr146.
Hass U, Scholze M, Christiansen S, Dalgaard M, Vinggaard AM, Axelstad M, Metzdorff SB, and Kortenkamp A. “Combined Exposure to Anti-Androgens Exacerbates Disruption of Sexual Differentiation in the Rat.” Environmental Health Perspectives 115 (2007): 122–28. https://doi.org/10.1289/ehp.9360.
Hass, Ulla, Julie Boberg, Sofie Christiansen, Pernille Rosenskjold Jacobsen, Anne Marie Vinggaard, Camilla Taxvig, Mette Erecius Poulsen, et al. “Adverse Effects on Sexual Development in Rat Offspring after Low Dose Exposure to a Mixture of Endocrine Disrupting Pesticides.” REPRODUCTIVE TOXICOLOGY 34, no. 2 (2012): 261–74. https://doi.org/10.1016/j.reprotox.2012.05.090.
Hellwig, J., B. Van Ravenzwaay, M. Mayer, and C. Gembardt. “Pre- and Postnatal Oral Toxicity of Vinclozolin in Wistar and Long–Evans Rats.” Regulatory Toxicology and Pharmacology 32, no. 1 (August 2000): 42–50. https://doi.org/10.1006/rtph.2000.1400.
Henriksen LS, Frederiksen H, Jørgensen N, Juul A, Skakkebæk NE, Toppari J, Petersen JH, and Main KM. “Maternal Phthalate Exposure during Pregnancy and Testis Function of Young Adult Sons.” The Science of the Total Environment, 2023, 161914. https://doi.org/10.1016/j.scitotenv.2023.161914.
Hosokawa, Shunji, Masakazu Murakami, Mariko Ineyama, Tomoya Yamada, Akira Yoshitake, Hirohiko Yamada, and Junshi Miyamoto. “The Affinity of Procymidone to Androgen Receptor in Rats and Mice.” The Journal of Toxicological Sciences 18, no. 2 (1993): 83–93. https://doi.org/10.2131/jts.18.83.
Hughes, Ieuan A, John D Davies, Trevor I Bunch, Vickie Pasterski, Kiki Mastroyannopolou, and Jane MacDougall. “Androgen Insensitivity Syndrome.” Lancet 2012 OCT, no. 20;380(9851) (June 13, 2012): 1419–28. https://doi.org/doi: 10.1016/S0140-6736(12)60071-3.
Inawaka, Kunifumi, Noriyuki Kishimoto, Hashihiro Higuchi, and Satoshi Kawamura. “Maternal Exposure to Procymidone Has No Effects on Fetal External Genitalia Development in Male Rabbit Fetuses in a Modified Developmental Toxicity Study.” The Journal of Toxicological Sciences 35, no. 3 (2010): 299–307. https://doi.org/10.2131/jts.35.299.
Ipulan LA, Raga D, Suzuki K, Murashima A, Matsumaru D, Cunha G, and Yamada G. “Investigation of Sexual Dimorphisms through Mouse Models and Hormone/Hormone-Disruptor Treatments.” Differentiation; Research in Biological Diversity 91, no. 4 (2016): 78–89. https://doi.org/10.1016/j.diff.2015.11.001.
Jarfelt, K, M Dalgaard, U Hass, J Borch, H Jacobsen, and O Ladefoged. “Antiandrogenic Effects in Male Rats Perinatally Exposed to a Mixture of Di(2-Ethylhexyl) Phthalate and Di(2-Ethylhexyl) Adipate.” Reproductive Toxicology 19, no. 4 (April 2005): 505–15. https://doi.org/10.1016/j.reprotox.2004.11.005.
Jensen TK, Frederiksen H, Kyhl HB, Lassen TH, Swan SH, Bornehag CG, Skakkebaek NE, et al. “Prenatal Exposure to Phthalates and Anogenital Distance in Male Infants from a Low-Exposed Danish Cohort (2010-2012).” Environmental Health Perspectives 124, no. 7 (2016): 1107–13. https://doi.org/10.1289/ehp.1509870.
Kang, Hong-Yo, Ko-En Huang, Shiuh Young Chang, Wen-Lung Ma, Wen-Jye Lin, and Chawnshang Chang. “Differential Modulation of Androgen Receptor-Mediated Transactivation by Smad3 and Tumor Suppressor Smad4.” Journal of Biological Chemistry 277, no. 46 (November 2002): 43749–56. https://doi.org/10.1074/jbc.M205603200.
Kelce, William R., Christy R. Lambright, L.Earl Gray, and Kenneth P. Roberts. “Vinclozolin Andp,P′-DDE Alter Androgen-Dependent Gene Expression:In VivoConfirmation of an Androgen Receptor-Mediated Mechanism.” Toxicology and Applied Pharmacology 142, no. 1 (January 1997): 192–200. https://doi.org/10.1006/taap.1996.7966.
Kita, Diogo H., Katlyn B. Meyer, Amanda C. Venturelli, Rafaella Adams, Daria L.B. Machado, Rosana N. Morais, Shanna H. Swan, Chris Gennings, and Anderson J. Martino-Andrade. “Manipulation of Pre and Postnatal Androgen Environments and Anogenital Distance in Rats.” Toxicology 368–369 (August 2016): 152–61. https://doi.org/10.1016/j.tox.2016.08.021.
Klinefelter, Gary R, John W Laskey, Witold M Winnik, Juan D Suarez, Naomi L Roberts, Lillian F Strader, Brandy W Riffle, and D N Rao Veeramachaneni. “Novel Molecular Targets Associated with Testicular Dysgenesis Induced by Gestational Exposure to Diethylhexyl Phthalate in the Rat: A Role for Estradiol.” REPRODUCTION 144, no. 6 (December 2012): 747–61. https://doi.org/10.1530/REP-12-0266.
Kojima, Hiroyuki, Eiji Katsura, Shinji Takeuchi, Kazuhito Niiyama, and Kunihiko Kobayashi. “Screening for Estrogen and Androgen Receptor Activities in 200 Pesticides by in Vitro Reporter Gene Assays Using Chinese Hamster Ovary Cells.” Environmental Health Perspectives 112, no. 5 (April 2004): 524–31. https://doi.org/10.1289/ehp.6649.
Labrie, F. “Mechanism of Action and Pure Antiandrogenic Properties of Flutamide.” Cancer 72, no. S12 (December 15, 1993): 3816–27. https://doi.org/10.1002/1097-0142(19931215)72:12+<3816::AID-CNCR2820721711>3.0.CO;2-3.
Lanzoni, Anna, Anna F Castoldi, George EN Kass, Andrea Terron, Guilhem De Seze, Anna Bal‐Price, Frédéric Y Bois, et al. “Advancing Human Health Risk Assessment.” EFSA Journal 17, no. Suppl 1 (July 8, 2019): e170712. https://doi.org/10.2903/j.efsa.2019.e170712.
Lin, Han, Qing-Quan Lian, Guo-Xin Hu, Yuan Jin, Yunhui Zhang, Dianne O. Hardy, Guo-Rong Chen, et al. “In Utero and Lactational Exposures to Diethylhexyl-Phthalate Affect Two Populations of Leydig Cells in Male Long-Evans Rats1.” Biology of Reproduction 80, no. 5 (May 1, 2009): 882–88. https://doi.org/10.1095/biolreprod.108.072975.
Martínez, Ariadne Gutiérrez, Balia Pardo, Rafael Gámez, Rosa Mas, Miriam Noa, Gisela Marrero, Maikel Valle, et al. “Effects of In Utero Exposure to D-004, a Lipid Extract from Roystonea Regia Fruits, in the Male Rat: A Comparison with Finasteride.” Journal of Medicinal Food 14, no. 12 (December 2011): 1663–69. https://doi.org/10.1089/jmf.2010.0279.
Martino-Andrade AJ, Liu F, Sathyanarayana S, Barrett ES, Redmon JB, Nguyen RH, Levine H, and Swan SH. “Timing of Prenatal Phthalate Exposure in Relation to Genital Endpoints in Male Newborns.” Andrology 4, no. 4 (2016): 585–93. https://doi.org/10.1111/andr.12180.
Martino‐Andrade, Anderson J., Rosana N. Morais, Giuliana G. K. Botelho, Graziela Muller, Simone W. Grande, Giovanna B. Carpentieri, Gabriel M. C. Leão, and Paulo R. Dalsenter. “Coadministration of Active Phthalates Results in Disruption of Foetal Testicular Function in Rats.” International Journal of Andrology 32, no. 6 (December 2009): 704–12. https://doi.org/10.1111/j.1365-2605.2008.00939.x.
Matsuura, Ikuo, Tetsuji Saitoh, Michiko Ashina, Yumi Wako, Hiroshi Iwata, Naoto Toyota, Yoshihito Ishizuka, Masato Namiki, Nobuhito Hoshino, and Minoru Tsuchitani. “EVALUATION OF A TWO-GENERATION REPRODUCTION TOXICITY STUDY ADDING ENDOPOINTS TO DETECT ENDOCRINE DISRUPTING ACTIVITY USING VINCLOZOLIN.” The Journal of Toxicological Sciences 30, no. Special (2005): S163-188. https://doi.org/10.2131/jts.30.S163.
McIntyre, B. S. “Androgen-Mediated Development in Male Rat Offspring Exposed to Flutamide in Utero: Permanence and Correlation of Early Postnatal Changes in Anogenital Distance and Nipple Retention with Malformations in Androgen-Dependent Tissues.” Toxicological Sciences 62, no. 2 (August 1, 2001): 236–49. https://doi.org/10.1093/toxsci/62.2.236.
Molina-Molina, J, A Hillenweck, I Jouanin, D Zalko, J Cravedi, M Fernandez, A Pillon, J Nicolas, N Olea, and P Balaguer. “Steroid Receptor Profiling of Vinclozolin and Its Primary Metabolites.” Toxicology and Applied Pharmacology 216, no. 1 (October 1, 2006): 44–54. https://doi.org/10.1016/j.taap.2006.04.005.
Moore, R W, T A Rudy, T M Lin, K Ko, and R E Peterson. “Abnormalities of Sexual Development in Male Rats with in Utero and Lactational Exposure to the Antiandrogenic Plasticizer Di(2-Ethylhexyl) Phthalate.” Environmental Health Perspectives 109, no. 3 (March 2001): 229–37. https://doi.org/10.1289/ehp.01109229.
Murashima, Aki, Satoshi Kishigami, Axel Thomson, and Gen Yamada. “Androgens and Mammalian Male Reproductive Tract Development.” Biochimica et Biophysica Acta (BBA) - Gene Regulatory Mechanisms 1849, no. 2 (February 2015): 163–70. https://doi.org/10.1016/j.bbagrm.2014.05.020.
Nightingale, Joanna, Khurram S. Chaudhary, Paul D. Abel, Andrew P. Stubbs, Hanna M. Romanska, Stephen E. Mitchell, Gordon W.H. Stamp, and El-Nasir Lalani. “Ligand Activation of the Androgen Receptor Downregulates E-Cadherin-Mediated Cell Adhesion and Promotes Apoptosis of Prostatic Cancer Cells.” Neoplasia 5, no. 4 (July 2003): 347–61. https://doi.org/10.1016/S1476-5586(03)80028-3.
OECD. 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, 2023. https://doi.org/10.1787/9789264264366-en.
Olier, Ivan, Yiqiang Zhan, Xiaoyu Liang, and Victor Volovici. “Causal Inference and Observational Data.” BMC Medical Research Methodology 23, no. 1 (October 11, 2023): 227. https://doi.org/10.1186/s12874-023-02058-5.
Orton, Frances, Erika Rosivatz, Martin Scholze, and Andreas Kortenkamp. “Widely Used Pesticides with Previously Unknown Endocrine Activity Revealed as in Vitro Antiandrogens.” Environmental Health Perspectives 119, no. 6 (June 2011): 794–800. https://doi.org/10.1289/ehp.1002895.
Ostby J, Kelce WR, Lambright C, Wolf CJ, Mann P, and Gray LE Jr. “The Fungicide Procymidone Alters Sexual Differentiation in the Male Rat by Acting as an Androgen-Receptor Antagonist in Vivo and in Vitro.” Toxicology and Industrial Health 15, no. 1 (1999): 80–93. https://doi.org/10.1177/074823379901500108.
Parks LG, Ostby JS, Lambright CR, Abbott BD, Klinefelter GR, Barlow NJ, and Gray LE Jr. “The Plasticizer Diethylhexyl Phthalate Induces Malformations by Decreasing Fetal Testosterone Synthesis during Sexual Differentiation in the Male Rat.” Toxicological Sciences : An Official Journal of the Society of Toxicology 58, no. 2 (2000): 339–49. https://doi.org/10.1093/toxsci/58.2.339.
Rittmaster, Roger S., and Alastair J.J. Wood. “Finasteride.” New England Journal of Medicine 330, no. 2 (January 13, 1994): 120–25. https://doi.org/10.1056/NEJM199401133300208.
Saillenfait, Anne-Marie, Jean-Philippe Sabaté, and Frédéric Gallissot. “Diisobutyl Phthalate Impairs the Androgen-Dependent Reproductive Development of the Male Rat.” Reproductive Toxicology 26, no. 2 (October 2008): 107–15. https://doi.org/10.1016/j.reprotox.2008.07.006.
Sato, Takashi, Takahiro Matsumoto, Hirotaka Kawano, Tomoyuki Watanabe, Yoshikatsu Uematsu, Keisuke Sekine, Toru Fukuda, et al. “Brain Masculinization Requires Androgen Receptor Function.” Proceedings of the National Academy of Sciences 101, no. 6 (February 10, 2004): 1673–78. https://doi.org/10.1073/pnas.0305303101.
Schaufele, Fred, Xavier Carbonell, Martin Guerbadot, Sabine Borngraeber, Mark S. Chapman, Aye Aye K. Ma, Jeffrey N. Miner, and Marc I. Diamond. “The Structural Basis of Androgen Receptor Activation: Intramolecular and Intermolecular Amino–Carboxy Interactions.” Proceedings of the National Academy of Sciences 102, no. 28 (July 12, 2005): 9802–7. https://doi.org/10.1073/pnas.0408819102.
Schneider, Steffen, Wolfgang Kaufmann, Volker Strauss, and Bennard Van Ravenzwaay. “Vinclozolin: A Feasibility and Sensitivity Study of the ILSI-HESI F1-Extended One-Generation Rat Reproduction Protocol.” Regulatory Toxicology and Pharmacology 59, no. 1 (February 2011): 91–100. https://doi.org/10.1016/j.yrtph.2010.09.010.
Scholze M, Taxvig C, Kortenkamp A, Boberg J, Christiansen S, Svingen T, Lauschke K, et al. “Quantitative in Vitro to in Vivo Extrapolation (QIVIVE) for Predicting Reduced Anogenital Distance Produced by Anti-Androgenic Pesticides in a Rodent Model for Male Reproductive Disorders.” Environmental Health Perspectives 128, no. 11 (2020): 117005. https://doi.org/10.1289/EHP6774.
Schwartz CL, Christiansen S, Vinggaard AM, Axelstad M, Hass U, and Svingen T. “Anogenital Distance as a Toxicological or Clinical Marker for Fetal Androgen Action and Risk for Reproductive Disorders.” Archives of Toxicology 93, no. 2 (2019): 253–72. https://doi.org/10.1007/s00204-018-2350-5.
Sharpe, Richard M. “Androgens and the Masculinization Programming Window: Human–Rodent Differences.” Biochemical Society Transactions 48, no. 4 (August 28, 2020): 1725–35. https://doi.org/10.1042/BST20200200.
Shimamura M, Kodaira K, Kenichi H, Ishimoto Y, Tamura H, and Iguchi T. “Comparison of Antiandrogenic Activities of Vinclozolin and D,L-Camphorquinone in Androgen Receptor Gene Transcription Assay in Vitro and Mouse in Utero Exposure Assay in Vivo.” Toxicology 174, no. 2 (2002): 97–107. https://doi.org/10.1016/s0300-483x(02)00044-6.
Simard, J., I. Luthy, J. Guay, A. Bélanger, and F. Labrie. “Characteristics of Interaction of the Antiandrogen Flutamide with the Androgen Receptor in Various Target Tissues.” Molecular and Cellular Endocrinology 44, no. 3 (March 1986): 261–70. https://doi.org/10.1016/0303-7207(86)90132-2.
Song, Jae W., and Kevin C. Chung. “Observational Studies: Cohort and Case-Control Studies.” Plastic and Reconstructive Surgery 126, no. 6 (December 2010): 2234–42. https://doi.org/10.1097/PRS.0b013e3181f44abc.
Stoner, Elizabeth. “The Clinical Development of a 5α-Reductase Inhibitor, Finasteride.” The Journal of Steroid Biochemistry and Molecular Biology 37, no. 3 (November 1990): 375–78. https://doi.org/10.1016/0960-0760(90)90487-6.
Sunman, Birce, Kadriye Yurdakok, Belma Kocer-Gumusel, Ozgur Ozyuncu, Filiz Akbiyik, Aylin Balci, Gizem Ozkemahli, Pinar Erkekoglu, and Murat Yurdakok. “Prenatal Bisphenol a and Phthalate Exposure Are Risk Factors for Male Reproductive System Development and Cord Blood Sex Hormone Levels.” REPRODUCTIVE TOXICOLOGY 87 (2019): 146–55. https://doi.org/10.1016/j.reprotox.2019.05.065.
Swan, Shanna H. “Environmental Phthalate Exposure in Relation to Reproductive Outcomes and Other Health Endpoints in Humans.” ENVIRONMENTAL RESEARCH 108, no. 2 (2008): 177–84. https://doi.org/10.1016/j.envres.2008.08.007.
Swan, Shanna H., Katharina M. Main, Fan Liu, Sara L. Stewart, Robin L. Kruse, Antonia M. Calafat, Catherine S. Mao, et al. “Decrease in Anogenital Distance among Male Infants with Prenatal Phthalate Exposure.” Environmental Health Perspectives 113, no. 8 (August 2005): 1056–61. https://doi.org/10.1289/ehp.8100.
Thankamony, A., V. Pasterski, K. K. Ong, C. L. Acerini, and I. A. Hughes. “Anogenital Distance as a Marker of Androgen Exposure in Humans.” Andrology 4, no. 4 (July 2016): 616–25. https://doi.org/10.1111/andr.12156.
Tut, Thein G., Farid J. Ghadessy, M. A. Trifiro, L. Pinsky, and E. L. Yong. “Long Polyglutamine Tracts in the Androgen Receptor Are Associated with Reduced Trans -Activation, Impaired Sperm Production, and Male Infertility 1.” The Journal of Clinical Endocrinology & Metabolism 82, no. 11 (November 1997): 3777–82. https://doi.org/10.1210/jcem.82.11.4385.
Ungewitter, Erica, Emmi Rotgers, Tanika Bantukul, Yasuhiko Kawakami, Grace E. Kissling, and Humphrey Hung-Chang Yao. “Teratogenic Effects of in Utero Exposure to Di-(2-Ethylhexyl)-Phthalate (DEHP) in B6:129S4 Mice.” Toxicological Sciences, January 25, 2017, kfx019. https://doi.org/10.1093/toxsci/kfx019.
Venturelli, Amanda Caroline, Katlyn Barp Meyer, Stefani Valéria Fischer, Diogo Henrique Kita, Rafaela Adams Philipsen, Rosana Nogueira Morais, and Anderson Joel Martino Andrade. “Effects of in Utero and Lactational Exposure to Phthalates on Reproductive Development and Glycemic Homeostasis in Rats.” Toxicology 421 (June 2019): 30–40. https://doi.org/10.1016/j.tox.2019.03.008.
Vo TT, Jung EM, Dang VH, Jung K, Baek J, Choi KC, and Jeung EB. “Differential Effects of Flutamide and Di-(2-Ethylhexyl) Phthalate on Male Reproductive Organs in a Rat Model.” The Journal of Reproduction and Development 55, no. 4 (2009): 400–411. https://doi.org/10.1262/jrd.20220.
Welsh, Michelle, Philippa T.K. Saunders, Mark Fisken, Hayley M. Scott, Gary R. Hutchison, Lee B. Smith, and Richard M. Sharpe. “Identification in Rats of a Programming Window for Reproductive Tract Masculinization, Disruption of Which Leads to Hypospadias and Cryptorchidism.” Journal of Clinical Investigation 118, no. 4 (April 1, 2008): 1479–90. https://doi.org/10.1172/JCI34241.
Welsh, Michelle, Hiroko Suzuki, and Gen Yamada. “The Masculinization Programming Window.” In UNDERSTANDING DIFFERENCES AND DISORDERS OF SEX DEVELOPMENT (DSD), 27:17–27, 2014. https://doi.org/10.1159/000363609.
Wenzel AG, Bloom MS, Butts CD, Wineland RJ, Brock JW, Cruze L, Unal ER, Kucklick JR, Somerville SE, and Newman RB. “Influence of Race on Prenatal Phthalate Exposure and Anogenital Measurements among Boys and Girls.” Environment International 110 (2018): 61–70. https://doi.org/10.1016/j.envint.2017.10.007.
Wilson, Vickie S., Kembra L. Howdeshell, Christy S. Lambright, Johnathan Furr, and L. Earl Gray. “Differential Expression of the Phthalate Syndrome in Male Sprague–Dawley and Wistar Rats after in Utero DEHP Exposure.” Toxicology Letters 170, no. 3 (May 2007): 177–84. https://doi.org/10.1016/j.toxlet.2007.03.004.
Wilson, Vickie S., Christy Lambright, Johnathan Furr, Joseph Ostby, Carmen Wood, Gary Held, and L.Earl Gray. “Phthalate Ester-Induced Gubernacular Lesions Are Associated with Reduced Insl3 Gene Expression in the Fetal Rat Testis.” Toxicology Letters 146, no. 3 (February 2004): 207–15. https://doi.org/10.1016/j.toxlet.2003.09.012.
Wolf, C. J., LeBlanc, G.A., and Gray LE Jr. “Interactive Effects of Vinclozolin and Testosterone Propionate on Pregnancy and Sexual Differentiation of the Male and Female SD Rat.” Toxicological Sciences 78, no. 1 (January 21, 2004): 135–43. https://doi.org/10.1093/toxsci/kfh018.
Wolf, C. J., LeBlanc, G.A., J.S. Ostby, and Gray LE Jr. “Characterization of the Period of Sensitivity of Fetal Male Sexual Development to Vinclozolin.” Toxicological Sciences 55, no. 1 (May 1, 2000): 152–61. https://doi.org/10.1093/toxsci/55.1.152.
Wolf, Cynthia, Christy Lambright, Peter Mann, Matthew Price, Ralph L. Cooper, Joseph Ostby, and L. Earl Gray. “Administration of Potentially Antiandrogenic Pesticides (Procymidone, Linuron, Iprodione, Chlozolinate, p,P′-DDE, and Ketoconazole) and Toxic Substances (Dibutyl- and Diethylhexyl Phthalate, PCB 169, and Ethane Dimethane Sulphonate) during Sexual Differentiation Produces Diverse Profiles of Reproductive Malformations in the Male Rat.” Toxicology and Industrial Health 15, no. 1–2 (February 1999): 94–118. https://doi.org/10.1177/074823379901500109.
Wong, Choi-iok, William R. Kelce, Madhabananda Sar, and Elizabeth M. Wilson. “Androgen Receptor Antagonist versus Agonist Activities of the Fungicide Vinclozolin Relative to Hydroxyflutamide.” Journal of Biological Chemistry 270, no. 34 (August 1995): 19998–3. https://doi.org/10.1074/jbc.270.34.19998.
Yamasaki Kanji, Noda Shuji, Muroi Takako, Mitoma Hideo, Takakura Saori, and Sakamoto Satoko. “Effects of in Utero and Lactational Exposure to Flutamide in SD Rats: Comparison of the Effects of Administration Periods.” Toxicology 209, no. 1 (April 2005): 47–54. https://doi.org/10.1016/j.tox.2004.12.004.
Yeh, Shuyuan, Meng-Yin Tsai, Qingquan Xu, Xiao-Min Mu, Henry Lardy, Ko-En Huang, Hank Lin, et al. “Generation and Characterization of Androgen Receptor Knockout (ARKO) Mice: An in Vivo Model for the Study of Androgen Functions in Selective Tissues.” Proceedings of the National Academy of Sciences 99, no. 21 (October 15, 2002): 13498–503. https://doi.org/10.1073/pnas.212474399.
Zhang, Jie, Yuanyuan Yao, Junlin Pan, Xiuxiu Guo, Xiaoying Han, Jun Zhou, and Xiaoqian Meng. “Maternal Exposure to Di-(2-Ethylhexyl) Phthalate (DEHP) Activates the PI3K/Akt/MTOR Signaling Pathway in F1 and F2 Generation Adult Mouse Testis.” Experimental Cell Research 394, no. 2 (September 2020): 112151. https://doi.org/10.1016/j.yexcr.2020.112151.
Zhang, Lian-Dong, Qian Deng, Zi-Ming Wang, Ming Gao, Lei Wang, Tie Chong, and He-Cheng Li. “Disruption of Reproductive Development in Male Rat Offspring Following Gestational and Lactational Exposure to Di-(2-Ethylhexyl) Phthalate and Genistein.” Biological Research 46, no. 2 (2013): 139–46. https://doi.org/10.4067/S0716-97602013000200004.
Relationship: 2127: Altered, Transcription of genes by the AR leads to AGD, decreased
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| 5α-reductase inhibition leading to short anogenital distance (AGD) in male (mammalian) offspring | non-adjacent | Moderate | |
| Androgen receptor (AR) antagonism leading to short anogenital distance (AGD) in male (mammalian) offspring | non-adjacent | Moderate | |
| Decreased testosterone synthesis leading to short anogenital distance (AGD) in male (mammalian) offspring | non-adjacent | Moderate | Low |
Evidence Supporting Applicability of this Relationship
| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| human, mouse, rat | human, mouse, rat | High | NCBI |
| Life Stage | Evidence |
|---|---|
| Fetal to Parturition | High |
| Sex | Evidence |
|---|---|
| Male | High |
Species
This KER applies to humans, mice, and rats based on biological plausibility. Current empirical evidence is from rat studies only.
Fetal masculinization including the AGD is regulated by androgens interacting with the AR in all mammals, including humans (Murashima et al., 2015; Thankamony et al., 2016), although, the size of the AGD and difference between the sexes vary between species. A large number of studies exist showing that fetal exposure to anti-androgens causes shortened AGD in male rats and mice (Schwartz et al., 2019a). Some epidemiological studies find associations between exposure to anti-androgenic compounds and shorter AGD in boys (Thankamony et al., 2016). However, the associations are not very clear and confidence in the data is limited by conflicting results, possibly due to differences in study design and methods for exposure measurements and analyses. Nevertheless, the KER is considered applicable to humans, based on current understanding of the role of AR activation in fetal masculinization.
Life stage
The length of the AGD is programmed during fetal life during the masculinization programming window. This takes place in rats around embryonic days 15.5-19.5 (GD16-20) and likely gestation weeks 8-14 in humans (Welsh et al., 2008). It should be mentioned that though AGD is believed to be relatively stable throughout life, it can be responsive to postnatal changes in androgen levels (Schwartz et al., 2019a).
Sex
A decrease in the male AGD is a consequence of disrupted androgen action (Welsh et al 2008). While exposure to chemicals during fetal life can also shorten female AGD, the biological significance and the mechanism driving the effect is unknown (Schwartz et al 2019a).
Key Event Relationship Description
During male reproductive development, the androgen receptor (AR) regulates gene transcription in target tissues to induce masculinization. Target tissues include the perineum, the tissue located between the anus and the genitals. This tissue is sexually dimorphic, with males developing the levator ani-bulbocavernosus (LABC) muscle complex in response to androgen signaling. The anogenital distance (AGD) is about twice as long in newborn males than in females in many mammals such mice, rats and humans.
A consequence of reduced androgen action during the masculinization programming window in utero, the male AGD will end up being shorter, approaching female AGD when AR signaling is almost blocked. Measuring of the AGD thus serves as a morphometric biomarker for compromised androgen action during fetal life and is used in OECD test guidelines for assessing endocrine disruption.
This KER refers to a tissue-specific, in this case the perineum, alteration in AR-mediated gene transcription during fetal development leading to a decreased AGD in male offspring.
Evidence Supporting this KER
Biological PlausibilitySexual differentiation initiates during fetal life when a surge in testosterone induces masculinization of a range of tissues and organs (Welsh et al). Testosterone and the more potent metabolite DHT mediate masculinization via activation of the AR; a nuclear transcription factor. Androgens thus induce masculinization via altered AR gene transcription in target tissues. This includes the perineum (Niel et al 2008; Ipulan et al 2014) which can be measured as the AGD and is approximately twice as long in newborn male rodents and humans compared to female (Schwartz et al 2019a). This is also evident in male AR knockout mice which present with an AGD that is indistinguishable from wildtype female littermates (MacLean et al 2008; Notini et al 2005).
Empirical EvidenceCurrent evidence for direct transcriptional changes mediated by AR disruption in the perineum leading to shorter male AGD is limited. Two studies were identified investigating the transcriptional footprint in the perineum after anti-androgen exposure:
Gestational exposure of rats to the 5α-reductase inhibitor finasteride (leading to decreased DHT levels) decreased fetal male AGD with 37% at gestational day (GD) 21. Microarray was used to compare transcriptional profiles between control males, finasteride-exposed males, and control females, revealing a sexually dimorphic transcriptional profile of the perineum, with the profile of finasteride-exposed males being intermediary to the male and female control groups (Schwartz et al 2019b).
Gestational exposure of rats to the AR antagonist triticonazole induced decreased fetal male AGD at GD21 and a differentially expressed set of genes investigated by whole transcriptome sequencing in the perineum at both GD17 and GD21 (Draskau et al 2022).
References
Draskau MK, Schwartz CL, Evrard B, Lardenois A, Pask A, Chalmel F and Svingen T (2022). The anti-androgenic fungicide triticonazole induces region-specific transcriptional changes in the developing rat perineum and phallus. Chemosphere 308(Pt 2):136346. doi: 10.1016/j.chemosphere.2022.136346
Ipulan LA, Suzuki K, Sakamoto Y, Murashima A, Imai Y, Omori A, Nakagata N, Nishinakamura R, Valasek P and Yamada G (2014). Nonmyocytic androgen receptor regulates the sexually dimorphic development of the embryonic bulbocavernosus muscle. Endocrinology 155(7):2467-79. doi: 10.1210/en.2014-1008
MacLean HE, Chiu WS, Notini AJ, Axell AM, Davey RA, McManus JF, Ma C, Plant DR, Lynch GS and Zajac JD (2008). Impaired skeletal muscle development and function in male, but not female, genomic androgen receptor knockout mice. FASEB J 22(8):2676-89. doi: 10.1096/fj.08-105726
Murashima, Aki, Satoshi Kishigami, Axel Thomson, and Gen Yamada. “Androgens and Mammalian Male Reproductive Tract Development.” Biochimica et Biophysica Acta (BBA) - Gene Regulatory Mechanisms 1849, no. 2 (February 2015): 163–70. https://doi.org/10.1016/j.bbagrm.2014.05.020.
Niel L, Willemsen KR, Volante SN and Monks DA (2008). Sexual dimorphism and androgen regulation of satellite cell population in differentiating rat levator ani muscle. Dev Neurobiol 68(1):115-22. doi: 10.1002/dneu.20580
Notini AJ, Davey RA, McManus JF, Bate KL and Zajac JD (2005). Genomic actions of the androgen receptor are required for normal male sexual differentiation in a mouse model. J Mol Endocrinol 35(3):547-55. doi: 10.1677/jme.1.0188
Schwartz CL, Christiansen S, Vinggaard AM, Axelstad M, Hass U and Svingen T (2019a). Anogenital distance as a toxicological or clinical marker for fetal androgen action and risk for reproductive disorders. Arch Toxicol 93(2):253-272. doi: 10.1007/s00204-018-2350-5
Schwartz CL, Vinggaard AM, Christiansen S, Darde TA, Chalmel F and Svingen T (2019b). Distinct Transcriptional Profiles of the Female, Male, and Finasteride-Induced Feminized Male Anogenital Region in Rat Fetuses. Toxicol Sci 169(1):303-311. doi: 10.1093/toxsci/kfz046
Thankamony, A., V. Pasterski, K. K. Ong, C. L. Acerini, and I. A. Hughes. “Anogenital Distance as a Marker of Androgen Exposure in Humans.” Andrology 4, no. 4 (July 2016): 616–25. https://doi.org/10.1111/andr.12156.
Welsh M, Saunders PT, Fisken M, Scott HM, Hutchison GR, Smith LB, Sharpe RM. 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. doi: 10.1172/JCI34241