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Relationship: 3448

Title

A descriptive phrase which clearly defines the two KEs being considered and the sequential relationship between them (i.e., which is upstream, and which is downstream). More help

Decrease, intratesticular testosterone leads to Decrease, circulating testosterone levels

Upstream event

The causing Key Event (KE) in a Key Event Relationship (KER). More help

Decrease, intratesticular testosterone

Downstream event

The responding Key Event (KE) in a Key Event Relationship (KER). More help

Decrease, circulating testosterone levels

Key Event Relationship Overview

The utility of AOPs for regulatory application is defined, to a large extent, by the confidence and precision with which they facilitate extrapolation of data measured at low levels of biological organisation to predicted outcomes at higher levels of organisation and the extent to which they can link biological effect measurements to their specific causes.Within the AOP framework, the predictive relationships that facilitate extrapolation are represented by the KERs. Consequently, the overall WoE for an AOP is a reflection in part, of the level of confidence in the underlying series of KERs it encompasses. Therefore, describing the KERs in an AOP involves assembling and organising the types of information and evidence that defines the scientific basis for inferring the probable change in, or state of, a downstream KE from the known or measured state of an upstream KE. More help

AOPs Referencing Relationship

AOP Name	Adjacency	Weight of Evidence	Quantitative Understanding	Point of Contact	Author Status	OECD Status
Decreased testosterone synthesis leading to short anogenital distance (AGD) in male (mammalian) offspring	adjacent	High	Moderate	Terje Svingen (send email)	Under development: Not open for comment. Do not cite	Under Development
Decreased testosterone synthesis leading to hypospadias in male (mammalian) offspring	adjacent			Terje Svingen (send email)	Under development: Not open for comment. Do not cite

Taxonomic Applicability

Latin or common names of a species or broader taxonomic grouping (e.g., class, order, family) that help to define the biological applicability domain of the KER.In general, this will be dictated by the more restrictive of the two KEs being linked together by the KER. More help

Term	Scientific Term	Evidence	Link
mammals	mammals		NCBI
rat	Rattus norvegicus	High	NCBI
mouse	Mus musculus	High	NCBI

Sex Applicability

An indication of the the relevant sex for this KER. More help

Sex	Evidence
Male	High

Life Stage Applicability

An indication of the the relevant life stage(s) for this KER. More help

Term	Evidence
All life stages	High

Key Event Relationship Description

Provides a concise overview of the information given below as well as addressing details that aren’t inherent in the description of the KEs themselves. More help

This KE describes a decrease in intratesticular testosterone production leading to a decrease in circulating levels of testosterone. Intratesticular testosterone can be measured in whole testicular tissue samples by testing ex vivo testicular testosterone production, and circulating testosterone is measured in plasma or serum. In males, the testes produce and secrete the majority of the circulating testosterone, with only a small contribution from the adrenal gland (Naamneh Elzenaty et al., 2022). In mammals, intratesticular testosterone levels are 30- to 100-fold higher than serum testosterone levels (Coviello et al., 2004; McLachlan et al., 2002; Turner et al., 1984). Reducing testicular testosterone will consequently lead to a reduction in circulating levels as well.

Evidence Collection Strategy

Include a description of the approach for identification and assembly of the evidence base for the KER. For evidence identification, include, for example, a description of the sources and dates of information consulted including expert knowledge, databases searched and associated search terms/strings. Include also a description of study screening criteria and methodology, study quality assessment considerations, the data extraction strategy and links to any repositories/databases of relevant references.Tabular summaries and links to relevant supporting documentation are encouraged, wherever possible. More help

This KER is in general considered canonical knowledge, and the evidence is therefore based on selected primary sources as well as review papers.

Evidence Supporting this KER

Addresses the scientific evidence supporting KERs in an AOP setting the stage for overall assessment of the AOP. More help

Biological Plausibility

Addresses the biological rationale for a connection between KEupstream and KEdownstream. This field can also incorporate additional mechanistic details that help inform the relationship between KEs, this is useful when it is not practical/pragmatic to represent these details as separate KEs due to the difficulty or relative infrequency with which it is likely to be measured. More help

The biological plausibility for this KER is considered high. The testes are the primary testosterone-producing organs in male mammals and the main contributors to the circulating testosterone levels in males (Naamneh Elzenaty et al., 2022). A decrease in intratesticular testosterone will therefore lead to a decrease in secretion of testosterone and consequently lower circulating levels of testosterone.

Empirical Evidence

Provides specific (citable) evidence that supports the idea of a change in the upstream KE (KEupstream) leading to, or being associated with, a subsequent change in the downstream KE (KEdownstream), assuming the perturbation of KEupstream is sufficient. More help

The empirical evidence for this KER is overall judged as high.

In vivo toxicity studies in rats and mice have shown that exposure to substances that lowers intratesticular testosterone also lowers circulating testosterone levels. This includes in utero exposure and measurements in fetal males (Borch J et al., 2004; Vinggaard AM et al., 2005) as well as exposure and measurements postnatally in male rodents (Hou X et al., 2020; Ji et al., 2010; Jiang XP et al., 2017)

Supporting this evidence are castration studies in male rats and monkeys, showing a marked reduction in circulating testosterone levels when removing the testes (Gomes & Jain, 1976; Perachio et al., 1977).

Lastly, in humans, males with hypogonadism or gonadal dysgenesis present with lower circulating testosterone levels (Hirose Y et al., 2007; Jones LW et al., 1970).

Dose concordance

In vivo toxicity studies support dose concordance for this KER, as exemplified below.

In pre-pubertal/pubertal male rats, chlorocholine chloride exposure (postnatal day (PND) 23-60) in three doses reduced both intratesticular and serum testosterone levels at PND60 at all doses tested (Hou X et al., 2020).

Perinatal exposure (gestational day (GD) 10-birth) of male mice to diethylhexyl phthalate (DEHP) in three doses (100, 500, and 1000 mg/kg bw/day) reduced intratesticular testosterone at 500 and 1000 mg/kg bw/day at PND1, while only 1000 mg/kg bw/day reduced serum levels of testosterone, although this was measured later, at PND56 (Xie Q et al., 2024)

In utero exposure (GD7-21) of male rats to DEHP in doses of 300 or 750 mg/kg bw/day reduced intratesticular testosterone levels at GD21, while only the high dose also reduced plasma testosterone levels (Borch J et al., 2004).

Temporal concordance

In vivo toxicity studies moderately support temporal concordance for this KER, as exemplified below.

Several studies show that a decrease in intratesticular and circulating testosterone can be measured at the same time point (Borch J et al., 2004; Hou X et al., 2020; Jiang XP et al., 2017; Vinggaard AM et al., 2005).

In utero exposure of male mice to DEHP from GD10 to birth reduced intratesticular testosterone levels at PND1 with LOAEL 500 mg/kg bw/day, and when measured at PND56, circulating testosterone levels were decreased, but with LOAEL 1000 mg/kg bw/day (Xie Q et al., 2024).

In Fisher JS et al., 2003, exposure of male rats from GD13-21 to 500 mg/kg bw/day dibutyl phthalate reduced intratesticular testosterone by ~90% (measured at GD19). When analyzing circulating testosterone levels at PND4, 10, 15, 25, and 90, only the testosterone levels on PND25 were decreased.

One study report conflicting results on the temporal concordance of this KER (Caceres et al., 2023). Here, male rats were exposed for 20 weeks from PND60 to a mixture of the phytoestrogens genistein and daidzein (combined dose of either 29 or 290 mg/kg bw/day). Intratesticular testosterone was measured every 4 weeks, while serum levels of testosterone were measured every second week. While the mixture caused a reduction of serum testosterone after 2 weeks of exposure, a reduction in intratesticular testosterone was not measured until after 8 weeks. The discrepancy might be explained by the multiple mechanisms of action of the phytoestrogens, as they, besides affecting testicular testosterone synthesis, may also influence peripheral aromatization of testosterone to estrogens (van Duursen et al., 2011).

Incidence concordance

Incidence concordance can not be evaluated for this KER.

Uncertainties and Inconsistencies

Addresses inconsistencies or uncertainties in the relationship including the identification of experimental details that may explain apparent deviations from the expected patterns of concordance. More help

There are examples of in vivo studies, in which stressors exposure have caused a reduction in intratesticular testosterone levels without a reduction in circulating testosterone levels.

Known modulating factors

This table captures specific information on the MF, its properties, how it affects the KER and respective references.1.) What is the modulating factor? Name the factor for which solid evidence exists that it influences this KER. Examples: age, sex, genotype, diet 2.) Details of this modulating factor. Specify which features of this MF are relevant for this KER. Examples: a specific age range or a specific biological age (defined by...); a specific gene mutation or variant, a specific nutrient (deficit or surplus); a sex-specific homone; a certain threshold value (e.g. serum levels of a chemical above...) 3.) Description of how this modulating factor affects this KER. Describe the provable modification of the KER (also quantitatively, if known). Examples: increase or decrease of the magnitude of effect (by a factor of...); change of the time-course of the effect (onset delay by...); alteration of the probability of the effect; increase or decrease of the sensitivity of the downstream effect (by a factor of...) 4.) Provision of supporting scientific evidence for an effect of this MF on this KER. Give a list of references. More help

Quantitative Understanding of the Linkage

Captures information that helps to define how much change in the upstream KE, and/or for how long, is needed to elicit a detectable and defined change in the downstream KE. More help

Response-response Relationship

Provides sources of data that define the response-response relationships between the KEs. More help

Time-scale

Information regarding the approximate time-scale of the changes in KEdownstream relative to changes in KEupstream (i.e., do effects on KEdownstream lag those on KEupstream by seconds, minutes, hours, or days?). More help

The time-scale for this KER is likely minutes or hours, as testosterone is secreted into the blood from the testes after synthesis. In vivo, a decrease in intratesticular and circulating testosterone can be measured at the same time, both in fetal and postnatal studies (Borch J et al., 2004; Hou X et al., 2020; Jiang XP et al., 2017; Vinggaard AM et al., 2005). Ex vivo, chemically-induced reduction in testicular production of testosterone can be measured in culture media after 3 hours incubation (earlier time points were not measured) (Wilson et al., 2009).

Known Feedforward/Feedback loops influencing this KER

Define whether there are known positive or negative feedback mechanisms involved and what is understood about their time-course and homeostatic limits. More help

Testosterone is a part of the hypothalamic-pituitary-gonadal (HPG) axis, which controls testosterone synthesis in puberty and adulthood. In this axis, gonatropin-releasing hormone (GnRH) is released from the hypothalamus and stimulates release of luteinizing hormone (LH) from the pituitary. LH acts on the testes to produce and secrete testosterone. Elevated circulating testosterone levels exerts negative feedback on the HPG axis (decreasing GnRH secretion) to keep testosterone levels in balance (Tilbrook & Clarke, 2001).

Importantly, there are species-specific differences in when the HPG axis is functional during development. In the mouse, fetal testosterone synthesis is independent of pituitary LH (O’Shaughnessy et al., 1998), whereas in humans, human chorionic gonadotropin (hCG) act similarly to LH and appear to be critical in stimulating testosterone synthesis in the fetal testis (Huhtaniemi, 2025).

Domain of Applicability

A free-text section of the KER description that the developers can use to explain their rationale for the taxonomic, life stage, or sex applicability structured terms. More help

Taxonomic applicability

The KER is assessed applicable to mammals, as testicular testosterone synthesis is common for all mammals. It is, however, acknowledged that this KER most likely has a much broader domain of applicability extending to non-mammalian vertebrates.

Sex applicability

This KER is only applicable to males, as testes are only found in males.

Life stage applicability

This KER is applicable to all life stages. Once formed, the testes produce and secrete testosterone during fetal development and throughout postnatal life, although testosterone levels do vary between life stages (Vesper et al., 2015).

References

List of the literature that was cited for this KER description. More help

Borch J, Ladefoged O, Hass U, & Vinggaard AM. (2004). 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(1), 53–61. https://doi.org/10.1016/j.reprotox.2003.10.011

Caceres, S., Crespo, B., Alonso-Diez, A., De Andrés, P. J., Millan, P., Silván, G., Illera, M. J., & Illera, J. C. (2023). Long-Term Exposure to Isoflavones Alters the Hormonal Steroid Homeostasis-Impairing Reproductive Function in Adult Male Wistar Rats. Nutrients, 15(5), 1261. https://doi.org/10.3390/nu15051261

Coviello, A. D., Bremner, W. J., Matsumoto, A. M., Herbst, K. L., Amory, J. K., Anawalt, B. D., Yan, X., Brown, T. R., Wright, W. W., Zirkin, B. R., & Jarow, J. P. (2004). Intratesticular Testosterone Concentrations Comparable With Serum Levels Are Not Sufficient to Maintain Normal Sperm Production in Men Receiving a Hormonal Contraceptive Regimen. Journal of Andrology, 25(6), 931–938. https://doi.org/10.1002/j.1939-4640.2004.tb03164.x

Fisher JS, Macpherson S, Marchetti N, & Sharpe RM. (2003). Human “testicular dysgenesis syndrome”: A possible model using in-utero exposure of the rat to dibutyl phthalate. Human Reproduction (Oxford, England), 18(7), 1383–1394. https://doi.org/10.1093/humrep/deg273

Gomes, W. R., & Jain, S. K. (1976). Effect of unilateral and bilateral castration and cryptorchidism on serum gonadotrophins in the rat. The Journal of Endocrinology, 68(02), 191–196. https://doi.org/10.1677/joe.0.0680191

Hirose Y, Sasa M, Bando Y, Hirose T, Morimoto T, Kurokawa Y, Nagao T, & Tangoku A. (2007). Bilateral male breast cancer with male potential hypogonadism. World Journal of Surgical Oncology, 5, 60. https://doi.org/10.1186/1477-7819-5-60

Hou X, Hu H, Xiagedeer B, Wang P, Kang C, Zhang Q, Meng Q, & Hao W. (2020). Effects of chlorocholine chloride on pubertal development and reproductive functions in male rats. Toxicology Letters, 319, 1–10. https://doi.org/10.1016/j.toxlet.2019.10.024

Huhtaniemi, I. T. (2025). Luteinizing hormone receptor knockout mouse: What has it taught us? Andrology, andr.70000. https://doi.org/10.1111/andr.70000

Ji, Y.-L., Wang, H., Liu, P., Wang, Q., Zhao, X.-F., Meng, X.-H., Yu, T., Zhang, H., Zhang, C., Zhang, Y., & Xu, D.-X. (2010). Pubertal cadmium exposure impairs testicular development and spermatogenesis via disrupting testicular testosterone synthesis in adult mice. Reproductive Toxicology, 29(2), 176–183. https://doi.org/10.1016/j.reprotox.2009.10.014

Jiang XP, Tang JY, Xu Z, Han P, Qin ZQ, Yang CD, Wang SQ, Tang M, Wang W, Qin C, Xu Y, Shen BX, Zhou WM, & Zhang W. (2017). Sulforaphane attenuates di-N-butylphthalate-induced reproductive damage in pubertal mice: Involvement of the Nrf2-antioxidant system. Environmental Toxicology, 32(7), 1908–1917. https://doi.org/10.1002/tox.22413

Jones LW, Isaacs H Jr, Edelbrock H, & Donnell GN. (1970). Reifenstein’s syndrome: Hereditary familial hypogonadism with hypospadias and gynecomastia. The Journal of Urology, 104(4), 608–611. https://doi.org/10.1016/s0022-5347(17)61793-2

McLachlan, R. I., O’Donnell, L., Stanton, P. G., Balourdos, G., Frydenberg, M., de Kretser, D. M., & Robertson, D. M. (2002). Effects of Testosterone Plus Medroxyprogesterone Acetate on Semen Quality, Reproductive Hormones, and Germ Cell Populations in Normal Young Men. The Journal of Clinical Endocrinology & Metabolism, 87(2), 546–556. https://doi.org/10.1210/jcem.87.2.8231

Naamneh Elzenaty, R., Du Toit, T., & Flück, C. E. (2022). Basics of androgen synthesis and action. Best Practice & Research Clinical Endocrinology & Metabolism, 36(4), 101665. https://doi.org/10.1016/j.beem.2022.101665

O’Shaughnessy, P. J., Baker, P., Sohnius, U., Haavisto, A.-M., Charlton, H. M., & Huhtaniemi, I. (1998). Fetal Development of Leydig Cell Activity in the Mouse Is Independent of Pituitary Gonadotroph Function*. Endocrinology, 139(3), 1141–1146. https://doi.org/10.1210/endo.139.3.5788

Perachio, A. A., Alexander, M., Marr, L. D., & Collins, D. C. (1977). Diurnal variations of serum testosterone levels in intact and gonadectomized male and female rhesus monkeys. Steroids, 29(1), 21–33. https://doi.org/10.1016/0039-128X(77)90106-4

Tilbrook, A. J., & Clarke, I. J. (2001). Negative Feedback Regulation of the Secretion and Actions of Gonadotropin-Releasing Hormone in Males. Biology of Reproduction, 64(3), 735–742. https://doi.org/10.1095/biolreprod64.3.735

Turner, T. T., Jones, C. E., Howards, S. S., Ewing, L. L., Zegeye, B., & Gunsalus, G. L. (1984). On the androgen microenvironment of maturing spermatozoa. Endocrinology, 115(5), 1925–1932. https://doi.org/10.1210/endo-115-5-1925

van Duursen, M. B. M., Nijmeijer, S. M., de Morree, E. S., de Jong, P. Chr., & van den Berg, M. (2011). Genistein induces breast cancer-associated aromatase and stimulates estrogen-dependent tumor cell growth in in vitro breast cancer model. Toxicology, 289(2), 67–73. https://doi.org/10.1016/j.tox.2011.07.005

Vesper, H. W., Wang, Y., Vidal, M., Botelho, J. C., & Caudill, S. P. (2015). Serum Total Testosterone Concentrations in the US Household Population from the NHANES 2011-2012 Study Population. Clinical Chemisty, 61(12), 1495–1504. https://doi.org/10.1373/clinchem.2015.245969

Vinggaard AM, Christiansen S, Laier P, Poulsen ME, Breinholt V, Jarfelt K, Jacobsen H, Dalgaard M, Nellemann C, & Hass U. (2005). Perinatal exposure to the fungicide prochloraz feminizes the male rat offspring. Toxicological Sciences : An Official Journal of the Society of Toxicology, 85(2), 886–897. https://doi.org/doi.org/10.1093/toxsci/kfi150

Wilson, V. S., Lambright, C. R., Furr, J. R., Howdeshell, K. L., & Gray, L. E., Jr. (2009). The herbicide linuron reduces testosterone production from the fetal rat testis during both in utero and in vitro exposures. TOXICOLOGY LETTERS, 186(2), 73–77. https://doi.org/10.1016/j.toxlet.2008.12.017

Xie Q, Cao H, Liu H, Xia K, Gao Y, & Deng C. (2024). Prenatal DEHP exposure induces lifelong testicular toxicity by continuously interfering with steroidogenic gene expression. Translational Andrology and Urology, 13(3), 369–382. https://doi.org/10.21037/tau-23-503