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EC number: 201-898-9 | CAS number: 89-32-7
- 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
Respiratory sensitisation
Administrative data
- Endpoint:
- respiratory sensitisation: in vivo
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- July-August 1988
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 988
- Report date:
- 1989
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- GLP compliance:
- no
Test material
- Reference substance name:
- Benzene-1,2:4,5-tetracarboxylic dianhydride
- EC Number:
- 201-898-9
- EC Name:
- Benzene-1,2:4,5-tetracarboxylic dianhydride
- Cas Number:
- 89-32-7
- Molecular formula:
- C10H2O6
- IUPAC Name:
- 5,11-dioxatricyclo[7.3.0.0³,⁷]dodeca-1,3(7),8-triene-4,6,10,12-tetrone
- Test material form:
- solid: crystalline
- Details on test material:
- - Colour: colourless
- Odour: odourless
- CAS-Number: 89-32-7
- Molecular formula: C10 H2 O6
- Molecular weight: 218.12
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Lot/batch No.of test material: identification no. 10820-33-D
- Expiration date of the lot/batch: no data
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: room temperature (approximately 20°C)
- Stability under test conditions: stable
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories. Inc., Portage. MI, USA
- Age at study initiation: 6 weeks
- Weight at study initiation: ca. 270-430 g
- Housing: gang housing
- Diet (e.g. ad libitum): Purina Rodent Chow 5001, Ralston Purina Co., St. Louis. MO, USA
- Water (e.g. ad libitum): supplied from a reverse-osmosis (RO) purifier by an automatic watering system
- Acclimation period: 2-week quarantine period
- Fasting period: 18 hours
- Indication of any skin lesions: no
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22°C
- Humidity (%): 40%
- Photoperiod (hrs dark / hrs light): 12 hours fluorescent lighting, 12 hours darkness
Test system
- Route of induction exposure:
- inhalation
- Route of challenge exposure:
- inhalation
- Vehicle:
- unchanged (no vehicle)
- Concentration:
- Induction and challenege exposure: 50 microgr/m3 of test article aerosol in air
- No. of animals per dose:
- 10 rats/sex/group
- Details on study design:
- Following a 2-week quarantine period. three groups of rats (10 rats/sex/group = 60 total rats) were randomly selected from a pool of rats whose body weigllts did not deviate more than three standard deviation units from the population mean. One group was exposed to 50 ug/m3 of the test article aerosol in air and two groups were exposed in a cbamber to clean filtered air only. The duration of the exposures was 6 hours per day for 5 days.
Following a 3-week rest, the test article-exposed rats along with one filtered air control (F AC) group were cbal1eDged with 50 ug/m3 of test item for 6 hours. The third group of rats was designated as nonchallenged filtered air controL All rats were euthanized and necropsied approximately 18 hours after the final exposure. - Challenge controls:
- None
- Positive control substance(s):
- none
- Negative control substance(s):
- none
Results and discussion
- Results:
- The time-weighted average concentrations of the test item for the five exposures and one challenge were 56.5 and 48.6 ug/m3, respectively. No significant clinical signs were observed in any rat during the study. There were no statistically significant effects of treatment on body weight. lung foci or absolute and relative lung weight and volume. Serum IgG antibody levels_were significantly elevated in the PMDA-exposed male rats only. When antibody values for the males and females were combined, these values were also statistically significant from controls. The three test item exposed males which had the highest number of lung foci (i.e. 14, 20 and 24) also had the highest levels of serum IgG antibody. However, this observation did not hold true for other animals (Le. rats exhibiting low numbers of foci, or no foci at all. had higher levels of antibody than rats exhibiting more lung foci).
In conclusion, and based on the results of this study, it is believed that the test item could cause respiratory sensitization if the exposure concentration was higher and/or of a longer duration. - Positive control results:
- Not tested
- Negative control results:
- Not tested
Applicant's summary and conclusion
- Interpretation of results:
- Category 1 (respiratory sensitising) based on GHS criteria
- Conclusions:
- Based on the results of this study, it is believed that PMDA could cause respiratory sensitization if the exposure concentration was higher and/or of a longer duration.
- Executive summary:
The purpose of this study was to determine the pulmonary sensitization potential of of the test item in male and female rats following multiple inhalation exposures. The time-weighted average concentrations of the test item for the five exposures and one challenge were 56.5 and 48.6 ug/m3, respectively. No significant clinical signs were observed in any rat during the study. There were no statistically significant effects of treatment on body weight. lung foci or absolute and relative lung weight and volume. Serum IgG antibody levels_were significantly elevated in the PMDA-exposed male rats only. When antibody values for the males and females were combined, these values were also statistically significant from controls. The three test item exposed males which had the highest number of lung foci (i.e. 14, 20 and 24) also had the highest levels of serum IgG antibody. However, this observation did not hold true for other animals (Le. rats exhibiting low numbers of foci, or no foci at all. had higher levels of antibody than rats exhibiting more lung foci).
In conclusion, and based on the results of this study, it is believed that the test item could cause respiratory sensitization if the exposure concentration was higher and/or of a longer duration.
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