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EC number: 431-770-1 | CAS number: 216698-07-6
- 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
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- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Genetic toxicity in vivo
Description of key information
Link to relevant study records
- 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:
- 07.03. - 25.03.2000
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: OECD guideline study, GLP.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- adopted 21st July 1997
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes
- Remarks:
- NOTOX B.V., Hambakenwetering 7, 5231 DD ‘s-Hertogenbosch, The Netherlands
- Type of assay:
- micronucleus assay
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Sulzfeld, Germany
- Age at study initiation: 6 weeks
- Weight at study initiation: between 30 and approx. 33 g
- Housing: Five male animals per group were housed in labeled polycarbonate cages containing purified sawdust as bedding material (SAWI, Jelu Werk, Rosenberg, Germany).
- Diet: standard pelleted laboratory animal diet, ad libitum
- Water: tap water, ad libitum
- Acclimation period: At least 5 days before start of treatment.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 +/- 3 °C
- Humidity (%): 30-70%
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12 - Route of administration:
- intraperitoneal
- Vehicle:
- Vehicle used: Corn oil
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test substance was suspended in corn oil. Test substance concentrations were blended and treated by ultra sonication to obtain a homogeneous suspension. Test substance concentrations were dosed within 4 hours after preparation. - Duration of treatment / exposure:
- A limit study with a repeated dose (with a 24 h interval) of 1000 mg/kg bw with male mice only was performed and sampled (after the second dosing)
- Frequency of treatment:
- Since, the test substance was difficult to suspend in corn oil, the highest dose that could be reached was 1000 mg/kg body weight. Therefore, the mice received a repeated intraperitoneal injection (with a 24 h interval) of 1000 mg/kg body weight to reach the limit dose of 2000 mg/kg body weight.
The route of administration was chosen to maximize the chance of the test substance reaching the target tissue. The dosing volume was 10 mL/kg bw. - Remarks:
- Doses / Concentrations:
approx. 2000 mg/kg bw (2x 1000 mg/kg bw)
Basis:
nominal conc. - No. of animals per sex per dose:
- Two groups of each 5 males.
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- The positive control used was cyclophosphamide dissolved in 0.9% (w/v) NaCl in Milli-RO water dosed at a single intraperitoneal injection of 50 mg salt/kg bw.
- Tissues and cell types examined:
- Bone marrow smears from femur.
- Details of tissue and slide preparation:
- TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields):
The animals dosed with corn oil and the test substance were sacrificed by cervical dislocation 24 or 48 h after the second dosing. The animals treated with cyclophosphamide were sacrificed by cervical dislocation 48 hr after dosing. Both femurs were removed and freed of blood and muscles. Both ends of the bone were shortened until a small opening to the marrow canal became visible. The bone was flushed with approximately 2 ml of foetal calf serum. The cell suspension was collected and centrifuged at 1000 rpm (approximately 100 g) for 5 min. The supernatant was removed with a Pasteur pipette. A drop of serum was left on the pellet. The cells in the sediment were carefully mixed with the serum by aspiration with the remaining serum. A drop of the cell suspension was placed on the end of a slide. The drop was spread by moving a clean slide with roundwhetted sides at an angle of approximately 45° over the slide with the drop of bone marrow suspension. The preparations were air-dried, fixed for 5 min in 100% methanol and air-dried overnight. Two slides were prepared per animal.
DETAILS OF SLIDE PREPARATION:
The slides were automatically stained using the "Wright-stain-procedure" in an "Ames" HEMA-tek slide stainer (Miles, Bayer Nederland B.V.). The dry slides were dipped in xylene before they were embedded in MicroMount and mounted with a coverslip.
METHOD OF ANALYSIS:
All slides were randomly coded before examination. An adhesive label with NOTOX study identification number and code was stuck over the marked slide. At first the slides were screened at a magnification of 100 X for regions of suitable technical quality, i.e. where the cells were well spread, undamaged and well stained. Slides were scored at a magnification of 1000 x. The number of micronucleated polychromatic erythrocytes was counted in 2000 polychromatic erythrocytes. The ratio polychromatic to normochromatic erythrocytes was determined by counting and differentiating the first 1000 erythrocytes at the same time. Micronuclei were only counted in polychromatic erythrocytes. Averages and standard deviations were calculated. - Evaluation criteria:
- A test substance is considered positive in the micronucleus test if:
It induced a biologically as well as a statistically significant (Wilcoxon Rank Sum Test; two-sided test at P < 0.05) increase in the frequency of micronucleated polychromatic erythrocytes (at any dose or at any sampling time).
A test substance is considered negative in the micronucleus test if:
None of the tested concentrations or sampling times showed a statistically significant (P < 0.05) increase in the incidence of micronucleated polychromatic erythrocytes.
The incidence of micronucleated polychromatic erythrocytes in the control animals should reasonably be within the laboratory historical solvent control data range; (mean + three times the standard deviation: 0.69%o ± 0.80 %o indicated are means for n=201). - Statistics:
- The Wilcoxon rank-sum test was used to assess significant differences between the numbers of micronuclei in the treatment and control groups, in which P<0.05 was used as the lowest level of significance.
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RANGE FINDING STUDY
A dose range finding study performed with the test article (NOTOX Project 264397) showed no toxic effect in male or female mice when receiving a repeated (with a 24 h interval) intraperitoneal injection with 1000 mg/kg body weight. Therefore, a limit study with a repeated dose (with a 24 h interval) of 1000 mg/kg body weight with male mice only was performed.
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay):
The mean numbers of micronucleated polychromatic erythrocytes scored in the test substance treated groups were compared with the corresponding control groups. No increase in the frequency of micronucleated polychromatic erythrocytes was observed in the polychromatic erythrocytes of the bone marrow of test substance treated animals. The incidence of micronucleated polychromatic erythrocytes in the slides of the animals treated with test substance were within the laboratory historical solvent control data range. Cyclophosphamide, the positive control substance, induced a statistically significant increase in the number of micronucleated polychromatic erythrocytes. Hence, the acceptability criteria of the test were met.
- Ratio of PCE/NCE (for Micronucleus assay):
The animals of the groups which were treated with the test substance showed no decrease in the ratio of polychromatic to normochromatic erythrocytes compared to the vehicle controls, which reflects a lack of toxic effects of this compound on the erythropoiesis. The group that was treated with cyclophosphamide showed a decrease in the ratio of polychromatic to normochromatic erythrocytes.
- Statistical evaluation: No statistically significant differences in the frequency of erythrocytes containing micronuclei between the solvent control and the dose group (2000 mg/kg bw) was observed. - Conclusions:
- Interpretation of results (migrated information): negative
It is concluded that the test article is not mutagenic in the micronucleus test under the experimental conditions described in this report. - Executive summary:
In order to evaluate the test article’s genotoxic effect on erythrocytes in bone marrow, A GLP-compliant Micronucleus Test in mice following OECD guideline 474 was performed. Two groups each comprising 5 males, received a repeated intraperitoneal injection of 1000 mg of the test article per kg body weight with a 24 hours interval. Corresponding vehicle treated groups served as negative controls, a group treated with a single intraperitoneal injection of cyclophosphamide (CP) at 50 mg/kg body weight served as positive control.
Bone marrow was sampled 24 or 48 hours after the second dosing. Bone marrow from the positive control group was harvested at 48 hours after dosing only. Cyclophosphamide, the positive control substance, induced a statistically significant increase in the number of micronucleated polychromatic erythrocytes. No increase in the frequency of micronucleated polychromatic erythrocytes was observed in the polychromatic erythrocytes of the bone marrow of animals treated with the test substance compared to the vehicle controls. The incidences of micronucleated polychromatic erythrocytes in the slides of the animals treated with the test substance were within the laboratory historical solvent control data range. The groups that were treated with the test article showed no decrease in the ratio of polychromatic to normochromatic erythrocytes compared to the vehicle controls, which reflects a lack of toxic effects of this compound on the erythropoiesis. The group that was treated with cyclophosphamide showed a decrease in the ratio of polychromatic to normochromatic erythrocytes.
Reference
MEAN NUMBER OF MICRONUCLEATED POLYCHROMATIC ERYTHROCYTES PER 2000 POLYCHROMATIC ERYTHROCYTES AND RATIO OF POLYCHROMATIC/NORMOCHROMATIC ERYTHROCYTES
Group | Treatment | Dose (mg/kg bw) | sampling time | Number of micronucleated polychromatic erythrocytes per 2000 polychromatic erythrocytes (mean ± S.D.)1 | Ratio polychromatic/ normochromatic (mean ± S.D.) |
A | corn oil2 | - | 24 | 1.2 ± 0.8 | 1.01 ± 0.05 |
B | corn oil2 | - | 48 | 1.4 ± 1.1 | 1.02 ± 0.06 |
C | test article2 | 1000 | 24 | 0.6 ± 0.5 | 1.00 ± 0.05 |
D | test article2 | 1000 | 48 | 1.4 ± 1.7 | 1.04 ± 0.01 |
E | CP | 50 | 48 | 19.6 ± 5.4 | 0.53 ± 0.21 |
CP = Cyclophosphamide
1 Five animals per treatment group
2 Dosed twice with a 24 h interval
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
Ames Test
The mutagenic potential of the test substance was investigated in a GLP-compliant Ames test (Notox, 1999) according to OECD guideline 471, performed with Salmonella typhimurium TA 98, TA 100, TA 1535, TA 1537 and Escherichia coli strain WP2 uvrA in the presence and absence of a metabolic activation system (S9 mix). Due to precipitation in the range finding test, the maximum tested concentration in the main test was 1000 µg/plate. None of the tested concentrations led to an increase in the incidence of either histidine- or tryptophan-prototrophic mutants by comparison with the negative control either with or without metabolic activation. The bacterial background lawn was not reduced at all concentrations tested and no decrease in the number of revertants was observed. This result was confirmed in a second independent experiment. Therefore, based on the results of these experiments and on standard evaluation criteria, it is concluded that the test article and its metabolites did not induce gene mutations in the strains of S. typhimurium and E. coli used.
Chromosome Aberration Test
In a chromosome aberration test (BSL Bioservice, 2006) according to OECD 473 and in compliance with GLP, the substance was investigated for clastogenic effects on Chinese hamster lung fibroblasts (V79) at various concentrations (20 - 60 µg/ml with, and 7.5 - 250 µg/ml without the metabolic activation system S9). The cells were incubated with the tet substance for 4 hours in the presence and for 4 or 20 hours in the absence of S9-mix. No biologically significant increase in the number of specific chromosome aberrations and no increase in the frequencies of polyploid cells were found after treatment with the test item in any of the experiments. The number of chromosome aberrations was within the historical control range at all doses assessed. No precipitation was observed in any concentration tested. Toxic effects were observed at doses from 15 µg/ml and higher and from 28 µg/ml and higher in experiments with or without S9-mix, respectively. EMS (400 and 900 µg/mL) and CPA (0.83 µg/mL) were used as positive controls and induced distinct and biologically relevant increases in cells with structural chromosomal aberration. Therefore, it is concluded that this experiment is valid and under the given experimental conditions no evidence of clastogenic effects was obtained in C79 cells in vitro.
Mammalian cell gene mutation assay
The test substance was assessed for its potential to induce gene mutations at the hypoxanthine-guanine phosphoribosyl transferase (HPRT) locus in Chinese hamster ovary (CHO) cells in vitro, following GLP principled and OECD guideline 476. Two independent experiments were carried out, both with and without the addition of liver S9 mix from phenobarbital- and β-naphthoflavone induced rats (exogenous metabolic activation). According to the results of this in vitro study, in two experiments performed independently of each other the test substance did not relevantly increase the number of mutant colonies, either without S9 mix or after the addition of a metabolizing system. The mutant frequencies at any concentration were within the range of the concurrent vehicle control values and within the range of our historical negative control data. The mutation frequencies of the (positive and negative) control groups were within the historical control data range. Cytotoxic effects, as indicated by clearly reduced cloning efficiencies of about or below 20% of the respective negative control values were observed in both experiments in the presence of S9 mix, and after 24 hours treatment in the 2nd Experiment at least at the highest applied concentrations. The increase in the frequencies of mutant colonies induced by the positive control substances EMS and DMBA clearly demonstrated the sensitivity of the test method and of the metabolic activity of the S9 mix employed. Thus, in the absence and the presence of metabolic activation, the test article is not a mutagenic substance in the HPRT locus assay using CHO cells under the experimental conditions chosen.
In vivo micronucleus test
In a GLP-compliant Micronucleus Test performed in mice following OECD guideline 474, the test article was investigated for genotoxic effects on erythrocytes in bone marrow. Two groups each comprising 5 males received a repeated intraperitoneal injection of 1000 mg/kg body weight of the test article with a 24 hours interval. Bone marrow was sampled 24 or 48 hours after the second dosing. Cyclophosphamide, the positive control substance, induced a statistically significant increase in the number of micronucleated polychromatic erythrocytes. No increase in the frequency of micronucleated polychromatic erythrocytes was observed in animals treated with the test substance compared to the vehicle controls. The incidences of micronucleated polychromatic erythrocytes in animals treated with the test substance were within the laboratory historical solvent control range. No decrease in the ratio of polychromatic to normochromatic erythrocytes compared to the vehicle controls was noted in treated animals, reflecting a lack of toxic effects of this compound on the erythropoiesis. As a result, it is concluded that the test article is not mutagenic in the micronucleus test under the experimental conditions described in this report.
Justification for selection of genetic toxicity endpoint
The GLP compliant in vivo study was selected to represent the whole set of valid studies required for this endpoint.
Justification for classification or non-classification
Dangerous Substance Directive (67/548/EEC)
The available experimental test data is reliable and suitable for the purpose of classification under Directive 67/548/EEC. Based on the present data, classification for genotoxicity is not warranted under Directive 67/548/EEC.
Classification, Labeling, and Packaging Regulation (EC) No. 1272/2008
The available experimental test data are reliable and suitable for the purpose of classification under Regulation (EC) No.1272/2008. Based on the present data, classification for genotoxicity is not warranted under Regulation (EC) No.1272/2008.
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