Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 200-370-5 | CAS number: 58-22-0
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Carcinogenicity
Administrative data
Description of key information
All data presented are based in the result of a literature search (references are stated in the tables). For testosterone, only limited data on toxicity was available. Further data was found for testosterone propionate and other esters and used for classification.
Testosterone and its esters were tested in mice, rat and hamsters by subcutaneous injection or implantation, and in rabbits and baboons by intramuscular injection. It induced cervical-uterine tumors in mice and prostatic adenocarcinoma was induced in male rats.
The incidences of leukemia and of liver-cell and breast tumors in untreated mice of some strains were decreased by testosterone treatment, but the incidence of mammary tumors was increased by neonatal treatment of females of a mammary-tumor-virus-bearing strain. Neoplasm was induced in hamsters by a combination of estrogen and testosterone. Hyperplasia in the bladder, uteri and vaginal epithelium of rats were detected.
Key value for chemical safety assessment
Justification for classification or non-classification
Due to the study results a carcinogenic effect of testosterone cannot be excluded. Additionally, it has to be taken into account that sex steroids in general can promote the growth of specific hormone dependent tissues and tumors.
Testosterone is classified as :
Category 3 (Xn, R40) according to Directive 67/548/EEC.
Category 2 according to Regulation (EC) 1272/2008 (CLP).
Additional information
All data presented are based in the result of a literature search (references are stated in the tables). For testosterone, only limited data on toxicity was available. Further data was found for testosterone propionate and other esters and used for classification. Although cancer test data are not required to fulfil the Annex VII obligations for a 1 -10 tpa registration dossier, summary data from the open literature are included here to provide support for classification conclusion. Read-across justification summary is attached to this endpoint summary.
Carcinogenicity-Animal Data
Test system |
Test Substance |
Application |
Dose/Duration |
Effect |
Literature |
C3H Mouse, male |
Testosterone propionate (in sesame oil) |
Subcutaneous |
Once weekly for 25 (or more) weeks 0.25 – 1.25 mg/week |
No hepatoma occurrence |
Schenken & Burns, 1943 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
C3H Mouse, female |
Testosterone propionate (in olive oil) |
Subcutaneous |
Once weekly for 12 months 1.00 - 1.25 mg/week |
Reduced incidence of mammary tumors (3/12) compared to controls (18/38). |
Jones, 1941 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
Rabbit, female |
Testosterone oenanthate (in sesam oil) |
Intramuscular |
15 mg on alternate weeks |
2 Adenomatous polyps in 1/21 animals; no other findings |
sark & Sommers, 1966 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
Nb Rat, male |
Testosterone propionate, |
Subcutaneous implant |
91 weeks 10, 20, 30 mg |
Increased incidence for prostatic carcinoma at middle and high dose after about 40 weeks |
Noble, 1977 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
Wistar Rat, female |
Testosterone together with nitrosamine in drinking water |
Subcutaneous implant |
50 mg (1:1 with cholesterol) |
Enhanced incidence of bladder tumors |
Okajima et al., 1975 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
A x C Rat, male, castrated |
Testosterone propionate/cholesterol (1:3) together with N-2-fluoreenyldacetamide, 4 weeks, |
Subcutaneous implant |
48 weeks
200 mg/kg bw |
Increased incidence of liver carcinomas |
Reuber, 1976 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
Hamster |
Testosterone propionate and diethylstilboestrol |
Subcutaneous implant |
5 month interval testosterone propionate 100 diethylstilboestrol 25 mg |
Induction of leiomyomas and leiomysarcomas |
Rivière et al., 1961, Kirkman&Algard, 1965 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
BALB/cCrgl Mouse |
Testosterone in water |
Subcutaneous injection |
First 5 days after birth 25 µg/d |
Hyperplasic epithelial lesions, resembling epidermoid carcinomas (vaginal squamous-cell tumors) |
Kimura&Nandi, 1967 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
BALB/cCrgl Mouse (MTV+), female |
Testosterone |
Subcutaneous injection |
First 5 days after birth 5 - 20 µg/d |
Increased mammary tumor incidence after 8.5 months (mean) |
Mori et al., 1976 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
SHN Mouse (MTV+), female |
5β-dihydrotestosterone in olive oil for the first 5 days after birth |
Subcutaneous injection |
200 µg/d |
Increased mammary tumor incidence after 6.2 months (mean) |
Yanai et al., 1977 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
Albino Rat, female |
Testosterone propionate in arachis oil |
Subcutaneous injection |
Weekly 0.5 mg , increased to 1 mg at the age of 21 days and to 2.5 mg at the age of 6 months |
Theca-cell ovarian tumors, epithelial hyperplasia in the uteri |
Horning 1958 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
Sprague-Dawley Rat, female |
Testosterone propionate in olive oil |
Subcutaneous injection |
Single dose on the day of birth 1.25 mg |
Mammary tumors (fibroadenomas and adenocarcinomas) |
Christacos et al., 1976 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
Sprague-Dawley Rat, female |
Testosterone propionate and DMBA |
Subcutaneous injection |
At day 2 after birth 1.25 mg
DMBA (20 mg, gavage) at day 50 |
Mammary dysplasia, no mammary tumors at day 300 |
Yoshida & Fukunishi, 1978 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
Sprague-Dawley Rat, female |
Testosterone propionate in sesame oil and DMBA |
Subcutaneous injection |
At day 2: 1.0 mg DMBA (20 mg, gavage) at day 50 |
Increased auditory sebaceous gland tumors |
Yoshida & Fukunishi, 1977 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
Sprague-Dawley Rat, female |
Testosterone and testosterone propionate in sesame oil and DMBA |
Subcutaneous injection |
Single dose at day 1 and 5 1.25 mg DMBA (20 mg, gavage) at day 50 |
Little effect of 5 d treatment, reduces mammary adenocarcinoma but increased fibroadenoma at 1 d treatment. No tumors with testosterone alone. |
Shellabarger & Soo, 1973 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
C57BL/Tw Mouse |
1)Testosterone 2)Testosterone propionate 3) 5α-dihydrotestosterone 4) 5α-dihydrotestosterone propionate |
Subcutaneous injection |
Daily for the first 10 days after birth 1: 100 µg 2: 50 µg 3: 100 µg 4: 50 µg |
Ovariectomized after 60 d. Vagina with stratified epithelium partly with superficial squamous metaplasia or cornification |
Iguchi & Takasugi, 1976 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
C57BL/Tw Mouse |
1) Testosterone 2) 5α-dihydrotestosterone |
Subcutaneous injection |
5 times (daily) from the day of birth 100 µg of either compound |
Ovariectomized after 10 d. Proliferation of the vaginal epithelium |
Otha & Inoguchi, 1976 as cited by IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work), V21 (1979) |
Baboon Male |
Testosterone Enenthate |
Intramuscular injection, |
200mg, once per week for 6 months. |
Significant gravimetric and volumetric increases in the prostate; a definite glandular and marked stromal hyperplasia with fibrosis developed in the caudal lobe |
Karr, JP et. al. Induction of benign prostatic hypertrophy in baboons., 1984. Urology: 23(3). |
Rat |
Estradiol plus testosterone |
Implants killed at 8, 16 and 24 weeks after initiation. |
Sampling of accessory sex glands for DNA adducts. Selective adduct formation in the dorsolateral prostate of rats treated with estradiol plus testosterone for 16 or 24 weeks. |
Appearance coinciding with putative preneoplastic lesions and preceding carcinoma development |
Han et al. 1995. Carcinogenesis 16(4), 951-954. |
Mice; rabbits |
Testosterone and its esters |
Subcutaneous injection, or implantation or intramuscular injection |
no data |
Testosterone propionate implanted subcutaneously in mice induced cervical-uterine tumours, which metastasized in some cases; in rats, metastasizing prostatic adenocarcinomas were induced in males.
Neonatal treatment of female mice by subcutaneous injection of testosterone induced lesions of the genital tract and increased the mammary tumour incidence when the animals were adult. 5b-Dihydrotestosterone, which is considered to be hormonally inactive in adults, also increased the incidence of mammary tumours in mice when given neonatally by subcutaneous injections.
|
WHO. 1998. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans, v21 Sex Hormones (II) |
In vitro |
testosterone and other steroids |
2 mmol/L to DNA obtained from human surgical resections, rat liver, HepG2 cells, and calf thymus |
|
no adducts were observed in DNA isolated from HepG2 cells incubated with 10-100 μmol/L testosterone for 24 h. The presence of a carbonyl group at C17 (which testosterone lacks) was predictive of DNA reactivity |
Seraj, M.J., Umemoto, A., Tanaka, M., Kajikawa, A., Hamada, K. & Monden, Y. (1996) DNA adduct formation by hormonal steroids in vitro. Mutat. Res., 370, 49-59.In Food Who Food Additives Series: 43 Prepared by the Fifty-second meeting of the Joint FAO/WHO Expert Committee on Food Additives (JECFA) World Health Organization, Geneva, 2000 IPCS - International Programme on Chemical Safety |
Nobel Rats |
Testosterone. Testosterone and estradiol |
no data |
no data |
DNA strand breaks were observed in the dorsolateral prostate of Nobel rats treated with a combination of testosterone and estradiol but not in those treated with testosterone alone |
Ho, S.M. & Roy, D. (1994) Sex hormone-induced nuclear DNA damage and lipid peroxidation in the dorsolateral prostates of Noble rats. Cancer Lett., 84, 155-162.. In Food Who Food Additives Series: 43 Prepared by the Fifty-second meeting of the Joint FAO/WHO Expert Committee on Food Additives (JECFA) World Health Organization, Geneva, 2000 IPCS - International Programme on Chemical Safety |
Carcinogencicity-Human
Description of Data |
Literature |
Increased testosterone levels may increase the risk for prostatic cancer. Limited evidence that anabolic steroids can cause both benign and malignant liver tumours |
IARC Monographs, Suppl 7, 1987. |
Epidemiological studies of the relationship between serum concentrations of androgens and estrogens and prostate cancer have yielded inconsistent but largely negative results (for references, see Dorgan et al., 1998; Ross et al., 1998). Since a possible association with markers of androgen metabolism (androstanediol glucuronide and DHT) has been observed in some studies, a complex, androgen-dependent, multi-gene model involving both androgen biosynthesis and metabolic pathways has been suggested to be critical for susceptibility to prostatic cancer |
Ross, R.K., Pike, M.C., Coetzee, G.A., Reichardt, J.K.V., Yu, M.C., Feigelson, H., Stanczyk, F.Z., Kolonel, L.N. & Henderson, B.E. (1998) Androgen metabolism and prostate cancer: Establishing a model of genetic susceptibility. Cancer Res., 58, 4497-4505. And Dorgan, J.F., Albanes, D., Virtamo, J., Heinonen, O.P., Chandler, D.W., Galmarini, M., McShane, L.M., Barrett, M.J., Tangrea, J. & Taylor, P.R. (1998) Relationship of serum androgens and estrogens to prostate cancer risk: Results from a prospective study in Finland. Cancer Epidemiol. Biomarkers Prev., 7, 1069-1074. IN Food Who Food Additives Series: 43 Prepared by the Fifty-second meeting of the Joint FAO/WHO Expert Committee on Food Additives (JECFA) World Health Organization, Geneva, 2000 IPCS - International Programme on Chemical Safety |
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.