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EC number: 246-910-3 | CAS number: 25376-45-8
- 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
Toxicity to reproduction
Administrative data
- Endpoint:
- fertility, other
- Remarks:
- based on test type (migrated information)
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: Not fully equivalent or similar to OECD guideline. Not fully reported.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 985
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- GLP compliance:
- not specified
Test material
- Reference substance name:
- 4-methyl-m-phenylenediamine
- EC Number:
- 202-453-1
- EC Name:
- 4-methyl-m-phenylenediamine
- Cas Number:
- 95-80-7
- Molecular formula:
- C7H10N2
- IUPAC Name:
- 4-methylbenzene-1,3-diamine
- Details on test material:
- 0, 0.01 and 0.03% 2,4-TDA
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Male rats (60-70 day old) were randomly distributed into 4 groups of 8-10 rats each and kept at 24ºC on a light-dark cycle of 12 hour. Rats were fed lab chow mixed with 2,4-TDA at concentrations of 0, 0.01 or 0.03%. The animals were housed one per cage and provided with their respective diets and tap water ad libitum. Body weights were measured weekly.
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- other: Laboratory chow
- Details on exposure:
- The rats were given diet containing 0, 0.01, or 0.03% 2,4–TDA.
- Details on mating procedure:
- After 10 weeks of treatment, each male rat was mated with 2 untreated, virgin females. Insemination was confirmed by vaginal smear, and after insemination the females were separately caged. After 1 week the females not inseminated were replaced by 2 new females, and mating continued for another week. A total of 4 females were mated with each male.
- Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- No data.
- Duration of treatment / exposure:
- 10 weeks, thereafter 4 weeks recovery
- Frequency of treatment:
- Continuous
- Details on study schedule:
- See "Further details on study design" for details.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 0.01, or 0.03% 2,4–TDA.
Basis:
no data
- No. of animals per sex per dose:
- 10 male rats per dosed group, 8 controls
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- After 2 weeks conditioning the (60–70)–day old rats were randomly distributed into 4 groups of 8–10 rats. They were kept 1/cage, at 24°C, and with a 12 hr dark/light cycle. The rats were given a proprietary feed containing 0, 0.01, or 0.03% TDA, and water, ad libitum. The 0.03 and 0.01% doses were approximately equal to 5, and 15 mg 2,4–TDA/kg bw/day, respectively. After 10 weeks of treatment, all the animals were returned to the regular proprietary food ration, and each was mated with 2 untreated, virgin females. Insemination was confirmed by vaginal smear, and after insemination the females were separately caged. After 1 week the females not inseminated were replaced by 2 new females, and mating continued for another week. A total of 4 females were mated with each male.
Body weights were measured weekly. The females were killed 14 days after confirmed insemination, and were examined for the presence and number of implantation sites, viable implants, and resorptions. The males used in breeding were sacrificed 2 weeks after mating, ie, 4 weeks after their return to the regular feed. The testes, and epididymides were fixed, stained and examined by light microscopy. - Positive control:
- Not used.
Examinations
- Parental animals: Observations and examinations:
- Not applicable.
- Oestrous cyclicity (parental animals):
- Not applicable.
- Sperm parameters (parental animals):
- The testes and epididymides were fixed and analysed for sperm analyses.
- Litter observations:
- Not applicable.
- Postmortem examinations (parental animals):
- Not applicable.
- Postmortem examinations (offspring):
- Not applicable.
- Statistics:
- The Chi-square technique was used to detect overall differences in the fertility index and mating index. When significant differences were found, pairwise comparisons between control and treatment groups were made by chi-sequare tests (one degree of freedom) using the Yates correction for continuity. The data for viable implants in pregnant females were analysed by analysis of varience. The level of significance was selected as p<0.05.
- Reproductive indices:
- Not applicable.
- Offspring viability indices:
- Not applicable.
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- not specified
- Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Histopathological findings: non-neoplastic:
- not specified
- Other effects:
- not specified
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- not specified
- Reproductive function: sperm measures:
- not specified
- Reproductive performance:
- not specified
Details on results (P0)
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- not specified
- Mortality / viability:
- not specified
- Body weight and weight changes:
- not specified
- Sexual maturation:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- not specified
- Histopathological findings:
- not specified
Details on results (F1)
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- The rats fed 0 and 0.03% 2,4–TDA in the feed over 10 weeks consumed 25 and 20 g feed/day, respectively. After initial acclimatisation the food consumption did not vary significantly over the 10 weeks.
0.03% (5 mg/kg bw):
Retardation in weight gain during weeks 4 -10 probably due to some reduced food consumption (no further details provided). 5/10 males revealed to be infertile, while the remaining animals in this group exhibited generally unimpaired fertility. Mating index significantly decreased: 0.73 (p<0.01), fertility index significantly decreased: 0.41 (p< 0.05). Light-microscopic examinations of the testes revealed focal or diffuse hypospermatocytogenesis in the seminiferous tubules and in cauda epididymides.
0.01% (15 mg/kg bw):
All animals were fertile; mating index: 0.95, fertility index: 0.74
Control: all animals were fertile; mating index: 1.00, fertility index: 0.72
The pregnancies derived from treated males were not significantly different from those produced from control males in terms of viable implants. Also the mean number of resorptions were similar in all of the groups. - Executive summary:
Effects of 2,4-toluenediamine (TDA) on reproduction in adult male Sprague-Dawley rats were evaluated. Diets containing 0, 0.01 and 0.03% TDA were fed ad libitum to experimental animals for 10 week. No signs of toxicity were found. Exposure to the high dose resulted in decreased mating frequency and an increase in infertile matings. Light-microscopic examination of the testes revealed reduced numbers of sperm in the seminiferous tubules and cauda epididymides. These results indicate that TDA is capable of reducing fertility and of exerting an inhibitory or toxic effect on spermatogenesis in the rat.
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