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EC number: 200-782-5 | CAS number: 72-48-0
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian cell study: DNA damage and/or repair
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 1991
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Evaluation of DNA-binding activity of hydroxyanthraquinones occuring in Rubia tinctorum L
- Author:
- B. Poginsky et al.
- Year:
- 1 991
- Bibliographic source:
- Carcinogenesis vol. 12 no. 7, pp. 1265 - 1271
- Report date:
- 1991
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Principle of test: In the present study they have investigated by 32P-postlabelling the possible binding to DNA of test substance in vivo, following oral administration of the test substance in mice.
- GLP compliance:
- no
- Type of assay:
- other: DNA-binding activity: 32P-postlabelling assay (detection of covalent binding of chemical carcinogens to DNA in animals and humans)
Test material
- Reference substance name:
- 1,2-dihydroxyanthraquinone
- EC Number:
- 200-782-5
- EC Name:
- 1,2-dihydroxyanthraquinone
- Cas Number:
- 72-48-0
- Molecular formula:
- C14H8O4
- IUPAC Name:
- 1,2-dihydroxy-9,10-dihydroanthracene-9,10-dione
- Test material form:
- solid: particulate/powder
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- other: Parkers
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: National Institute for Medical Research, Mill Hill, London
- Age at study initiation: 4-6 weeks
- Weight at study initiation: n.a.
- Fasting period before study: deprived of food each evening, the compounds was administered the following morning
- Housing: n.a.
- Diet (e.g. ad libitum): ad libitum for the rest of the day
- Water (e.g. ad libitum): ad libitum
- Acclimation period: n.a.
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- - Concentration of test material : 10mg
- Details on exposure:
- DIET PREPARATION
- Rate of preparation of diet (frequency):1/day
- Mixing appropriate amounts with (Type of food): cheese spread (1g)
- Storage temperature of food: n.a. - Duration of treatment / exposure:
- 4 days
- Frequency of treatment:
- 1/day
- Post exposure period:
- 4 hours after the last administration the mice were killed
Doses / concentrations
- Dose / conc.:
- 10 other: mg/day
- No. of animals per sex per dose:
- 2 animals per group, one dose
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- none
Examinations
- Tissues and cell types examined:
- Liver, kidney, duodenum and colon were removed and stored at -70°C until DNA isolation
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Vehicle controls validity:
- valid
- Additional information on results:
- The 32P-postlabelling analysis of hepatic DNA from mice treated with the test item does not show evidence of radioactive spot other than those seen in control DNA.
The kidney DNA from mice treated with the test substance showed a similar pattern to that of the control group.
Applicant's summary and conclusion
- Conclusions:
- The test substance does not form DNA adducts in mice liver, kidney, duodenum and colon.
- Executive summary:
In the present study, they have investigated by32P-postlabelling the possible binding to DNA of 1,2 -dihydroantraquinone in vivo, following the treatment of males Parkes mice, 4 -6 weeks old. The32P-postlabelling assay is a method to detect covalent binding of chemical carcinogens to DNA in animals and humans.
Duplicate group of two animals/group were deprived of food each evening and the compounds (10mg/d) were administered mixed with cheese spread (1g) the following morning. Thereafter, the mice received standard lab diet ad libitum for the rest of the day. The mice were treated for 4 days; the controls received cheese spread only. Four hours after the last administration, the mice were killed. Liver, kidney, duodenum and colon were removed and store at -70°C until DNA isolation.
The thawed tissues sample were homogenized and the DNA were isolated and labelled by32-P-postlabelling. The DNA adducts were measured by chromatography. The presence of radiolabelled adducts on the chromatograms was detected by autoradiography. The levels of adducts in DNA samples were determined from the amount of radioactivity present in the adduct spot, measured by Cerenkov counting32P-ATP used in the labelling reaction.
In conclusion, the32P-postlabelling of DNA from mice treated with the test substance did not give rise of DNA adducts in mice liver, kidney, duodenum and colon.
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