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EC number: 202-425-9 | CAS number: 95-50-1
- 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:
- reproductive toxicity, other
- Remarks:
- repeated dose toxicity studies
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 1985
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Histopathology of reproductive organs in repeated dose toxicity studies
Data source
Reference
- Reference Type:
- publication
- Title:
- Toxicology and carcinogenesis studies of 1,2-dichlorobenzene (o-dichlorobenzene) (CAS no. 95-50-1) in F344/N rats and B6C3F1 mice (gavage studies)
- Author:
- National Toxicology Program (NTP)
- Year:
- 1 985
- Bibliographic source:
- Techn. Rep. No. 255, US Dept. of Health and Human Services, Research Triangle Park, N.C. 27709, USA, 1985
Materials and methods
- Principles of method if other than guideline:
- Several repeated dose toxicity studies were conducted which cover the evaluation of potential toxic effects on the reproductive organs. The National Toxicology Program (1985) administered 1,2-dichlorobenzene by gavage for 13 weeks (0, 30, 60, 125, 250 or 500 mg/kg bw) and two years (0, 60 or 120 mg/kg bw) in male and female rats (F344) and mice (B6C3F1). All studies included the macroscopical and histopathological examination of prostate/testes or ovaries/uterus for all animals or control and high dose group respectively.
Test material
- Reference substance name:
- 1,2-dichlorobenzene
- EC Number:
- 202-425-9
- EC Name:
- 1,2-dichlorobenzene
- Cas Number:
- 95-50-1
- Molecular formula:
- C6H4Cl2
- IUPAC Name:
- 1,2-dichlorobenzene
- Details on test material:
- - Name of test material (as cited in study report): 1,2-dichlorobenzene
- Analytical purity: >99%
- Impurities (identity and concentrations): 10.8 ppm acidic components (assumed to be hydrochloric acid); GC system: seven further impurities totalling less than 0.07%; two other GC-MS system: 0.7-0.84% 1,4-dichlorobenzene
- Lot/batch No.: SC61377 (ICC Solvent Chemical Company, New York, NY)
- Stability under test conditions: no notable change in the test material; storage conditions were satisfactory over the course of the study
- Storage condition of test material: 22°C in the dark
Constituent 1
Test animals
- Species:
- other: rats and mice
- Strain:
- other: rats (F344) and mice (B6C3F1)
- Sex:
- male/female
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Duration of treatment / exposure:
- 13 weeks to 2 years
- Frequency of treatment:
- daily
- Details on study schedule:
- Several repeated dose toxicity studies were conducted which cover the evaluation of potential toxic effects on the reproductive organs. The National Toxicology Program (1985) administered 1,2-dichlorobenzene by gavage for 13 weeks (0, 30, 60, 125, 250 or 500 mg/kg bw) and two years (0, 60 or 120 mg/kg bw) in male and female rats (F344) and mice (B6C3F1). All studies included the macroscopical and histopathological examination of prostate/testes or ovaries/uterus for all animals or control and high dose group respectively.
- No. of animals per sex per dose:
- see chapter repeated dose toxicity
- Control animals:
- yes
Results and discussion
Results: P0 (first parental generation)
Effect levels (P0)
- Dose descriptor:
- NOAEL
- Remarks:
- reproductive organs
- Effect level:
- 500 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: None of the repeated dose toxicity/carcinogenicity studies showed any adverse effect on the reproductive organs.
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
Several repeated dose toxicity studies were conducted which cover the evaluation of potential toxic effects on the reproductive organs. The National Toxicology Program (1985) administered 1,2-dichlorobenzene by gavage for 13 weeks (0, 30, 60, 125, 250 or 500 mg/kg bw) and two years (0, 60 or 120 mg/kg bw) in male and female rats (F344) and mice (B6C3F1). All studies included the macroscopical and histopathological examination of prostate/testes or ovaries/uterus for all animals or control and high dose group respectively.
None of the studies showed any adverse effect on the reproductive organs. The only effects seen were interstitial-cell tumours of the testis in male rats with a significant positive trend when analyzed by the life-table test, but with a significant negative trend when analyzed by the Cochran-Armitage test. Since this tumour was not considered to be life threatening, the increase detected by the life-table test was discounted.
As confirmed by literature (Mangelsdorf et al. 2003, Ulbrich and Palmer 1995, Janer et al. 2007, Dent 2007, Sanbuissho et al. 2009) histopathological examinations of reproductive tissues in repeated dose toxicity studies on rodents are of high value and high sensitivity for evaluation of reproductive toxicity in males and females.
Applicant's summary and conclusion
- Executive summary:
Several repeated dose toxicity studies were conducted which cover the evaluation of potential toxic effects on the reproductive organs. The National Toxicology Program (1985) administered 1,2-dichlorobenzene by gavage for 13 weeks (0, 30, 60, 125, 250 or 500 mg/kg bw) and two years (0, 60 or 120 mg/kg bw) in male and female rats (F344) and mice (B6C3F1). All studies included the macroscopical and histopathological examination of prostate/testes or ovaries/uterus for all animals or control and high dose group respectively.
None of the studies showed any adverse effect on the reproductive organs. The only effects seen were interstitial-cell tumours of the testis in male rats with a significant positive trend when analyzed by the life-table test, but with a significant negative trend when analyzed by the Cochran-Armitage test. Since this tumour was not considered to be life threatening, the increase detected by the life-table test was discounted.
As confirmed by literature (Mangelsdorf et al. 2003, Ulbrich and Palmer 1995, Janer et al. 2007, Dent 2007, Sanbuissho et al. 2009) histopathological examinations of reproductive tissues in repeated dose toxicity studies on rodents are of high value and high sensitivity for evaluation of reproductive toxicity in males and females.
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