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EC number: 231-717-9 | CAS number: 7699-43-6
- 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 somatic cell study: cytogenicity / bone marrow chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- disregarded due to major methodological deficiencies
- Study period:
- no data
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- significant methodological deficiencies
- Remarks:
- Bone marrow was only collected once at 24 hours rather than at 12-18 hours and 24 h thereafter, colchicine was given 2 hours before sampling rather than 3-5 hours before sampling; a positive control was not used; results were not presented per animal and no listing of the different types of structural chromosome aberrations was presented. Oral administration was unspecified.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 990
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 475 (Mammalian Bone Marrow Chromosome Aberration Test)
- Deviations:
- yes
- Remarks:
- See rationale for reliability scoring.
- GLP compliance:
- not specified
- Type of assay:
- chromosome aberration assay
Test material
- Reference substance name:
- Zirconium dichloride oxide
- EC Number:
- 231-717-9
- EC Name:
- Zirconium dichloride oxide
- Cas Number:
- 7699-43-6
- Molecular formula:
- Cl2OZr
- IUPAC Name:
- Dichloro(oxo)zirconium
- Test material form:
- solid: crystalline
- Details on test material:
- - Name of test material (as cited in study report): zirconium oxychloride
- Physical state: crystals
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- Swiss
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 8-9 weeks of age
- Weight at study initiation: 28-30 g
- Diet (e.g. ad libitum): ad libitum Gold Mohur mice feed; manufactured by Lipton India Limited
- Water (e.g. ad libitum): ad libitum
- Houding: Temperature controlled chambers
Administration / exposure
- Route of administration:
- oral: unspecified
- Vehicle:
- - Vehicle(s)/solvent(s) used: distilled water
- Details on exposure:
- no data
- Duration of treatment / exposure:
- single oral administration
- Frequency of treatment:
- single dose
- Post exposure period:
- not applicable
Doses / concentrationsopen allclose all
- Dose / conc.:
- 225 other: mg/kg actual ingested - males
- Dose / conc.:
- 750 other: mg/kg actual ingested - males
- Dose / conc.:
- 2 250 other: mg/kg actual ingested - males
- Dose / conc.:
- 220 other: mg/kg actual ingested - females
- Dose / conc.:
- 734 other: mg/kg actual ingested - females
- Dose / conc.:
- 2 200 other: mg/kg actual ingested - females
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- no data
Examinations
- Tissues and cell types examined:
- Bone marrow was flushed out and prepared for analysis of chromosomal aberration.
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: Doses were calculated as fractions of the LD50 dose determined for the test substance.
TREATMENT AND SAMPLING TIMES (in addition to information in specific fields): A single oral administration of the test substance and animals were sacrificed 24 hours after adminstration.
DETAILS OF SLIDE PREPARATION: 2 h before sacrifice, all mice were intraperitoneally injected with colchicine, 4 mg/kg. Bone marrow was flushed out and prepared for analysis of chromosomal aberrations, following the usual hypotonic acetic acid-ethanol fixation and Giemsa staining schedule. Slides were coded and scored blind for total chromosomal abnormalities. - Evaluation criteria:
- 50 well-scattered metaphase plates per animal and a total of 250 metaphase plates per sex per treatment group were observed for chromosomal aberrations. 5000 cells per sex per treatment were scored to estimate divisional frequency.
- Statistics:
- The results obtained for total chromosomal abnormalities were statistically analysed for dose response following trend test according to Margolin et al., 1986. The level of significance was established at p = 0.001.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- positive
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- not specified
- Additional information on results:
- Observations made 24 h after the administration of zirconium oxychloride in concentrations of 2250 and 750 mg/kg body weight in males and 2200 and 734 mg/kg body weight in females increased the divisional frequency in comparison to control. However, mitotic divisional frequency was not enhanced appreciably by the lowest dose used (225 mg/kg for males and 220 mg/kg for females).
Control: 2.74% mitotic cells in males and 2.90% in females
Low dose: 3.10% mitotic cells in males and 3.96% in females
Mid dose: 5.50% mitotic cells in males and 5.60% in females
High dose: 4.90% mitotic cells in males and 5.80% in females
Animals exposed to the test substance reported significant enhancement of the frequency of aberrant metaphases as compared with the control. The percentages of total abnormalities were increased considerably in both sexes with all concentrations used. The degree of increase was directly proportional to the concentration and was significant between the control and the next dose used and also between the consecutive doses.
In general, the abnormalities were relatively higher in the female mice than in the male ones, but the difference was not statistically significant. Induced abnormalities included both chromosomal aberrations and spindle disturbances. The former were mainly chromatid and chromosome breaks with a few cases of centric fusion. The action of zirconium appears to be on different phases of the cell cycle.
Total aberrant metaphases (mean):
control: 5.6% in males and 5.2% in females
Low dose: 10.8% in males and females
Mid dose: 18.0% in males and 19.0% in females
High dose: 22.5% in males and 24.8% in females
Applicant's summary and conclusion
- Conclusions:
- Under the test conditions the frequencies of aberrations were directly proportionate to the concentration used. Female mice were found to be more susceptible than male mice, though not to a significantly higher level. The results of this study should be treated with great care for the following reasons:
1) Only total chromosomal abnormalities are presented, which include structural chromosome aberrations and spindle disturbances, the latter being
polyploidy. Polyploidy is a disturbance in mitotic processes and cell cycle progression. An increase in polypoloidy may indicate that a chemical has the potential to induce numerical aberrations. However, polyploidy is not related to clastogenicity, and should therefore be included separately from the structural chromosome aberrations. As this study does not distinguish between the two, a conclusion on clastogenicity cannot be drawn.
2) An aqueous solution of zirconium oxychloride is given to the mice. It is known from water solubility/hydrolysis experiments that the substance in water will cause a drop in pH by the release of H+ ions. Apart from the fact that the mice have probably been dosed corrosive solutions, there is some evidence that H+ ions can cause chromosomal damage (refer to IARC monograph 54-8 (1992; p. 203) on hydrochloric acid). It can thus not be ruled out that the observed effects in the bone marrow have been caused by the low pH after dissolving the test substance in water.
3) No data was presented on whether the substance can actually reach the bone marrow and whether this test is thus biologically relevant. Some evidence exists that zirconium oxychloride is poorly absorbed by mice after oral administration of an aqueous solution of 1500 mg/kg (Delongeas et al., 1983, J. Pharmacol. 14(4) 437-447). It reaches the blood and after 6 h a maximal blood concentration of 2.9 mg Zr/L (i.e. about 10 mg zirconium oxychloride per liter) was reached. In a similar but more extensive study in rats given aqueous solutions of 3000 mg zirconium oxychloride/kg, the maximal blood concentration was reached after 6 hours being about 0.3 mg Zr/L (i.e. about 1 mg zirconium oxychloride per liter). Using metabolic cages it was shown that within 24 hours 90-98% of the given dose was excreted via feces and minimal amounts via urine. This shows that the substance is hardly absorbed as it is excreted via feces.
In the same study of Delongeas et al. (1983), tissue distribution reveals that the small absorbed fraction is distributed and fixed in the ovaries, liver and lung, and to a lesser degree in bone and CNS. All together this raises the question whether the substance in the current study has reached the bone marrow to a sufficient extent in order to induce effects.
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