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EC number: 201-029-3 | CAS number: 77-47-4
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian germ cell study: cytogenicity / chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1978
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 978
- Report date:
- 1978
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 478 (Genetic Toxicology: Rodent Dominant Lethal Test)
- Deviations:
- yes
- Remarks:
- Information on bodyweight and toxicity signs not recorded
- GLP compliance:
- no
- Type of assay:
- rodent dominant lethal assay
Test material
- Reference substance name:
- Hexachlorocyclopentadiene
- EC Number:
- 201-029-3
- EC Name:
- Hexachlorocyclopentadiene
- Cas Number:
- 77-47-4
- Molecular formula:
- C5Cl6
- IUPAC Name:
- hexachlorocyclopentadiene
- Test material form:
- liquid
1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Details on species / strain selection:
- Random bred male and female mice
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Inc., Protage, Michigan
- Age at study initiation: at least 8 weeks
- Assigned to test groups randomly: yes
- Housing: Males housed individually and females housed in pairs (except when mating) in shoe box cages on AB-SORB-DRI bedding.
- Diet: Purina Lab Chow ad libitum
- Water: ad libitum
- Acclimation period: 2 weeks
ENVIRONMENTAL CONDITIONS
- Photoperiod: 12 hour light/dark cycle
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: DMSO
- Duration of treatment / exposure:
- Male mice exposed to several dose levels of test compound over 5 days
- Frequency of treatment:
- Daily
- Post exposure period:
- Rested for 2 days following treatment, then mated weekly for 7 weeks.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 1 mg/kg bw/day (nominal)
- Dose / conc.:
- 0.3 mg/kg bw/day (nominal)
- Dose / conc.:
- 0.1 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 10 random bred mice assigned to 1 of 5 groups. Three groups received different dose levels of hexachlorocyclopentadiene; a fourth group received only the solvent; a fifth group received a known mutagen as the positive control. Following treatment, each male was mated with 2 virgin females which were replaced weekly for 7 weeks.
- Control animals:
- yes, concurrent vehicle
- yes, sham-exposed
- yes, historical
- Positive control(s):
- Triethylenemelamine (TEM)
- Justification for choice of positive control(s):
- Route of administration: single intraperitoneal injection
Examinations
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: Range finding studies were conducted to calculate dose information. LD50, LD5 and LD1 concentrations were computer generated based on the preliminary study. The high dose level was selected from these data; 1/3rd and 1/10th of the high dose were used as the intermediate and low dose levels respectively.
TREATMENT AND SAMPLING TIMES: Male mice were exposed to the test compound for 5 days then mated over the entire period of spermatogenesis to unexposed virgin females. At mid-pregnancy the females were killed and scored for number of living and dead implants, as well as fertility level.
METHOD OF ANALYSIS: The number of dead and living fetuses, resorption sites, and total implantation sites were recorded. Data were analysed for statistical significance. Results were compared to data from control animals and used to determine the degree of induced dominant lethality. - Evaluation criteria:
- Dominant lethality is determined from:
a) a mutation index derived from dead to total implants; or
b) the number of dead implants per pregnant female - Statistics:
- See attached background material.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- A preliminary test was performed in order to determine the toxicity of the substance and adapt the final doses selected
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 50 mg/kg to 5000 mg/kg (first trial). 7.6 mg/kg to 76 mg/kg (second trial).
- Clinical signs of toxicity in test animals: Mortality occurred at all the doses investigated. All animals died at 76 mg/kg and above.
Any other information on results incl. tables
See attached background material for full results table.
Applicant's summary and conclusion
- Conclusions:
- Hexachlorocyclopentadiene was not active in this Mouse Dominant Lethal Assay.
- Executive summary:
A mouse dominant lethal assay was performed to determine the potential of the assay to induce structural and numerical chromosome aberrations according to a method similar to the OECD Tetsing Guideline 478 (non-GLP) with deviations.
Hexachlorocyclopentadiene was tested for toxicity over a range of 50 mg/kg to 5,000 mg/kg. Based on this toxicity and acute LD50 level of 76 mg/kg was calculated. The high dose was selected as the LD50 and concentrations of 25.3 mg/kg and 7.6 mg/kg were employed as the two lower doses levels. These concentrations proved to be too toxic for a five-day exposure since all ten animals died before five days. A second LD50 was calculated and identified 1 mg/kg as the high dose and 1/3 and 1/10 of the LD50 levels for the study.
The test material was examined for its ability to induce dominant lethality in mice treated with 0.1, 0.3 and 1.0 mg/kg bw/d for five days.
There was no evidence for significant dominant lethal activity by Hexachlorocyclopentadiene in mice. All data were within the concurrent and historical control levels. The positive control compound produced the expected dominant lethal effects in the first three mating weeks. Hexachlorocyclopentadiene was not active in the Mouse Dominant Lethal Assay conducted as part of this evaluation.
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