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EC number: 269-682-7 | CAS number: 68309-95-5
- 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 / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 30 March 2010 to 27 April 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP compliant study conducted in accordance with a relevant guideline with no or minor deviations.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5395 (In Vivo Mammalian Cytogenetics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Diammonium bis[carbonato-O]dihydroxyzirconate
- EC Number:
- 269-682-7
- EC Name:
- Diammonium bis[carbonato-O]dihydroxyzirconate
- Cas Number:
- 68309-95-5
- Molecular formula:
- C2H2O8Zr.2H4N
- IUPAC Name:
- Diammonium bis[carbonato-O]dihydroxyzirconate
- Details on test material:
- Description : clear colourless liquid
Batch number : 09/092
Date received : 26 February 2010
Expiry date : 26 August 2010
Storage conditions :room temperature in the dark
CoA included in the report
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- ICR
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Sufficient albino Hsd: ICR (CD-1®) strain mice were obtained from Harlan UK. At the start of the main test the mice weighed 22 to 28 g and were approximately five to eight weeks old. After a minimum acclimatisation period of five days the animals were selected at random and given a number unique within the study by tail marking and a number written on a colour coded cage card.
The animals were housed in groups of up to seven, by sex, in solid-floor polypropylene cages with wood-flake bedding. Free access to mains drinking water and food (Harlan Teklad 2014 Rodent Pelleted Diet) was allowed throughout the study.
The temperature and relative humidity were set to achieve limits of 19 to 25ºC and 30 to 70% respectively. Any occasional deviations from these targets were considered not to have affected the purpose or integrity of the study. The rate of air exchange was approximately fifteen changes per hour and the lighting was controlled by a time switch to give twelve hours light and twelve hours darkness.
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- The vehicle was supplied by Gibco, as follows:
Supplier's identification: Phosphate buffered saline
Supplier's lot number: 722040A
Description: Clear colourless liquid
Date received: 03 March 2010
Expiry date: January 2012
Storage conditions: Room temperature - Details on exposure:
- Groups, each of seven male mice, were dosed once only via the intraperitoneal route with the test material at 1000, 500 or 250 mg/kg.
- Duration of treatment / exposure:
- Groups, each of seven male mice, were dosed once only via the intraperitoneal route.
- Frequency of treatment:
- Animals were dosed only once.
- Post exposure period:
- One group of mice from each dose level was killed by cervical dislocation 24 hours following treatment and a second group dosed with test material at 1000 mg/kg was killed after 48 hours. In addition, three further groups of male mice were included in the study; two groups (each of seven mice) were dosed via the intraperitoneal route with the vehicle alone (phosphate buffered saline) and a third group (five mice) was dosed orally with cyclophosphamide. Cyclophosphamide is a positive control material known to produce micronuclei under the conditions of the test. The vehicle controls were killed 24 or 48 hours following dosing and positive control group animals were killed 24 hours following dosing.
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
1000 mg/kg
Basis:
other: intraperitoneal injection
- Remarks:
- Doses / Concentrations:
500 mg/kg
Basis:
other: intraperitoneal injection
- Remarks:
- Doses / Concentrations:
250 mg/kg
Basis:
other: intraperitoneal injection
- Remarks:
- Doses / Concentrations:
Vehicle control
Basis:
other: intraperitoneal injection
- Remarks:
- Doses / Concentrations:
Positive control (5 mg/kg)
Basis:
actual ingested
oral dose
- No. of animals per sex per dose:
- 7 (test and control animals)
5 animals only were dosed with positive control. - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- The positive control material was supplied by Acros Organics, as follows:
Supplier's identification: Cyclophosphamide
Supplier's lot number: A0164185
In-house serial number: R-4447
Date received: 27 October 2008
Expiry date: 27 October 2010
Storage conditions: Approximately 4ºC in the dark
For the purpose of this study the positive control material was freshly prepared as required as a solution at the appropriate concentration in distilled water (Aguettant batch no. 300522801).
The concentration, homogeneity and stability of the positive control material and its preparation were not determined by analysis.
Examinations
- Tissues and cell types examined:
- Bone marrow
Polychromatic and normochromatic erythrocytes - Details of tissue and slide preparation:
- Slide Preparation
Immediately following termination (i.e. 24 or 48 hours following dosing), both femurs were dissected from each animal, aspirated with foetal calf serum and bone marrow smears prepared following centrifugation and re-suspension. The smears were air-dried, fixed in absolute methanol, stained in May-Grünwald/Giemsa, allowed to air-dry and a cover slip applied using mounting medium.
Slide Evaluation
Stained bone marrow smears were coded and examined blind using light microscopy at x1000 magnification. The incidence of micronucleated cells
per 2000 polychromatic erythrocytes (PCE-blue stained immature cells) per animal was scored. Micronuclei are normally circular in shape, although occasionally they may be oval or half-moon shaped, and have a sharp contour with even staining. In addition, the number of normochromatic erythrocytes (NCE-pink stained mature cells) associated with 1000 erythrocytes was counted; these cells were also scored for incidence of micronuclei.
The ratio of polychromatic to normochromatic erythrocytes was calculated together with appropriate group mean values and standard deviations. - Evaluation criteria:
- Interpretation of Results
A comparison was made between the number of micronucleated polychromatic erythrocytes occurring in each of the test material groups and the number occurring in the corresponding vehicle control group.
A positive mutagenic response would be demonstrated when a statistically significant, dose-responsive, toxicologically relevant increase in the number of micronucleated polychromatic erythrocytes was observed for either the 24 or 48-hour kill times when compared to their corresponding control group. If these criteria were not fulfilled, then the test material was considered to be non genotoxic under the conditions of the test.
A positive response for bone marrow toxicity would be demonstrated when the dose group mean polychromatic to normochromatic ratio was shown to be statistically significantly lower than the concurrent vehicle control group. - Statistics:
- All data were statistically analysed using appropriate statistical methods as recommended by the UKEMS Sub-committee on Guidelines for Mutagenicity Testing Report, Part III (1989). The data was analysed following a transformation using Student's t-test (two tailed) and any significant results were confirmed using the one way analysis of variance.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- Range-finding Toxicity Test
As available data in rats indicated no toxicity by the oral route at the limit dose of 2000 mg/kg, it was considered necessary to only investigate the intraperitoneal route of exposure. A single male and female mouse were treated at 1000 mg/kg by i.p. injection. No difference in sensitivity was observed and therefore two additional male mice were treated at the same dose level and by the same route of exposure. Clear evidence of toxicity was observed in animals dosed with test material via the intraperitoneal route with clinical signs observed as follows: Hunched posture, splayed gait, ptosis, and ataxia. These observations were taken as adequate evidence of systemic absorption. Because of no difference in sensitivity was observed, the main study was performed using male mice only. As adequate evidence of test material toxicity was demonstrated via the intraperitoneal route of administration; therefore, this was selected for use in the main test. The maximum tolerated dose (MTD) of the test material, 1000 mg/kg, was selected for use in the main test, with 500 and 250 mg/kg as the lower dose levels.
Micronucleus Test
Mortality Data and Clinical Observations
There were no premature deaths seen in any of the dose groups. Clinical signs were observed in animals dosed with the test material at and above 250 mg/kg in both the 24 and 48 hour groups where appropriate, these were as follows: Hunched posture, ptosis and ataxia.
Evaluation of Bone Marrow Slides
Modest statistically significant decreases in the PCE/NCE ratio were observed in all three 24 hour test material dose groups and, whilst not statistically significant, a modest decrease was also observed in the 48 hour test 1000 mg/kg dose group when compared to the concurrent vehicle control group. Therefore, the decreases in PCE/NCE ratio, together with the observation of clinical signs at and above 250 mg/kg, were taken to indicate that systemic absorption had occurred and exposure to the target tissue had been achieved.
There were no statistically significant increases in the frequency of micronucleated PCE in any of the test material dose groups when compared to their concurrent vehicle control groups.
The positive control group showed a marked increase in the incidence of micronucleated polychromatic erythrocytes hence confirming the sensitivity of the system to the known mutagenic activity of cyclophosphamide under the conditions of the test.
The test material was found not to produce a significant increase in the frequency of micronuclei in polychromatic erythrocytes of mice under the conditions of the test.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
The test material was considered to be non-genotoxic under the conditions of the test. - Executive summary:
A GLP compliant study has been conducted in accordance with OECD Guideline 474. The test material administered by intraperitoneal injections at dosages of 1000, 500 and 250 mg/kg caused clinical signs of toxicity and reductions in the PCE/NCE ratio, thus confirming exposure of the target organ. The test substance was considered to be non-genotoxic under the conditions of the test.
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