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EC number: 939-179-3 | CAS number: -
- 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: other: chromosome mutation
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Justification of read-across: Both chemicals are of comparable structures with minor deviations and can be characterized as an ester of sorbitan and a fatty acid. Justification of reliability of 2: scientifically well-performed study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Sorbitan stearate
- EC Number:
- 215-664-9
- EC Name:
- Sorbitan stearate
- Cas Number:
- 1338-41-6
- IUPAC Name:
- 1,4-anhydro-6-O-stearoyl-D-glucitol
- Reference substance name:
- Sorbitan monooctadecanoate
- IUPAC Name:
- Sorbitan monooctadecanoate
- Test material form:
- solid: crystalline
- Details on test material:
- - Name of test material (as cited in study report): Sorbitan monooctadecanoate
- Molecular weight (if other than submission substance): 430.62
- Physical state: white to slightly yellow waxy solid
- Analytical purity: >99.5%
- Storage condition of test material: room temperature
Constituent 1
Constituent 2
Test animals
- Species:
- mouse
- Strain:
- Crj: CD(SD)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Japan
- Age at study initiation: 9 weeks
- Weight at study initiation:23.1-34.5
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21.0-25.0
- Humidity (%): 40.0-75.0
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: water
- Duration of treatment / exposure:
- gavage, once per day, two days
- Frequency of treatment:
- once per day, two days
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
500, 1000 and 2000 mg/kg
Basis:
actual ingested
micronucleus test
- Remarks:
- Doses / Concentrations:
250, 500, 1000, 2000 mg/kg
Basis:
actual ingested
preliminary toxicity test
- No. of animals per sex per dose:
- Preliminary toxicity test: 3 males and 3 females per dose
main test: 5 males per dose - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamidemonohydrat
- Route of administration: gavage
- Doses / concentrations: 50 mg/kg
Examinations
- Tissues and cell types examined:
- bone marrow
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
Any other information on results incl. tables
The analogue approach using sorbitan stearate as source chemical is justified:
Both chemicals are of comparable structures with minor deviations and can be characterized as an ester of sorbitan and a fatty acid. Compared to the source chemical, the target chemical has a shorter alkyl chains that affect its physicochemical properties. But based on the kinetic / metabolic investigations on both chemicals, the length of the alkyl chain is not considered to have significant impact on the metabolic pathway or toxicological mode of action. Oral gavage studies in rats administered C14 labeled sorbitan stearate in oil solutions have demonstrated that about 90% of the substance was absorbed and hydrolyzed to stearic acid and sorbitan. The metabolic fate of sorbitan caprylate was investigated using a lipase assay. The hydrolysis mediated by porcine pancreas lipase was quantitatively determined. The target chemical sorbitan caprylate is proved to be hydrolyzed and caprylic acid was formed . These findings suggest that metabolism of the sorbitan occur initially via enzymatic hydrolysis, leading to sorbitan and the corresponding natural acids.
Based on the above mentioned information, it is reasonable to consider that these two substances are comparable in their metabolic fate and thereby toxicological profiles. Hence, the source chemical is considered as “suitable with interpretation” analog.
According to the available toxicity studies, the findings are also comparable for target and source chemicals:
· The findings in acute toxicity studies are comparable. Both chemicals are of no acute toxicity.
· The findings in subacute dose toxicity studies are comparable. No treatment effects were observed in 28-day repeated toxicity studies in Wistar rats. The same NOEL of 1000 mg/kg bw/d was derived for both chemicals.
· The findings in genetic toxicity are comparable. Both chemicals did not induce gene mutations in Ames tests, but induced structural chromosomal aberrations in cell lines of Chinese Hamster.
· The findings in reproduction / developmental toxicity studies are comparable.
General condition and mortality in mice after double oral administrations of sorbitan stearate in the preliminary toxicity test
sex | Dose mg/kg/day | Number of mice | General condition | Mortality |
male | 250 | 3 | no abnormality | 0/3 |
500 | 3 | no abnormality | 0/3 | |
1000 | 3 | no abnormality | 0/3 | |
2000 | 3 | no abnormality | 0/3 | |
female | 250 | 3 | no abnormality | 0/3 |
500 | 3 | no abnormality | 0/3 | |
1000 | 3 | no abnormality | 0/3 | |
2000 | 3 | no abnormality | 0/3 |
General conditin and mortality in male mice after double administration of sorbitan stearate in the micronucleus test
Dose mg/kg/day | Number of mice | General condition | Mortality |
Negative control | 5 | no abnormality | 0/5 |
500 | 5 | no abnormality | 0/5 |
1000 | 5 | no abnormality | 0/5 |
2000 | 5 | no abnormality | 0/5 |
positive coontral 50 | 5 | no abnormality | 0/5 |
Results of micronucleus test in male mice after double oral administrations of sorbitan stearate
Group | Animal No. | % of MNPCEs | % of PCEs in ERY |
Negative control | 1 | 0.10 | 56.7 |
2 | 0.05 | 47.8 | |
3 | 0.15 | 53.5 | |
4 | 0.10 | 62.6 | |
5 | 0.15 | 40.0 | |
mean | 0.11 | 52.1 | |
500 mg/kg/day | 6 | 0.00 | 59.4 |
7 | 0.10 | 62.2 | |
8 | 0.20 | 57.8 | |
9 | 0.10 | 52.3 | |
10 | 0.05 | 55.0 | |
mean | 0.09 | 57.3 | |
1000 mg/kg/day | 11 | 0.20 | 57.4 |
12 | 0.10 | 50.8 | |
13 | 0.15 | 50.4 | |
14 | 0.05 | 58.6 | |
15 | 0.10 | 43.9 | |
mean | 0.12 | 52.2 | |
2000 mg/kg/day | 16 | 0.05 | 63.8 |
17 | 0.15 | 56.4 | |
18 | 0.30 | 65.1 | |
19 | 0.05 | 52.9 | |
20 | 0.10 | 52.4 | |
mean | 0.13 | 58.1 | |
Positive control 50 mg/kg/day | 21 | 2.75 | 59.4 |
22 | 2.45 | 57.7 | |
23 | 2.75 | 60.5 | |
24 | 2.65 | 59.1 | |
25 | 3.00 | 66.5 | |
mean | 2.72 | 60.6 |
% of MNPCEs: % of micronucleated polychromatic erythrocytes in polychromatic ery血rocytesobserved
% of PCEs in ERY: % of polychromatic erythrocytes in erythrocytes observed
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
In conclusion, the test item did not induce clastogen effect in the bone marrow cells of the mouse under the test condition. - Executive summary:
The test item was asssessed in the micronucleus assay for its potential to induce micronuclei in the bone marrow of mice. Water was used as a vehicle. Preliminary toxicity test was carried out in order to test the dose used, with doses of 250, 500, 1000, 2000 mg/kg/day in male and female mice by gavage. No mortality or abnormality was observed. Therefore the micronucleus test was performed with doses of 500, 1000, 2000 mg/kg/day. The test item was administered by gavage once per day for 2 days. Water was used as negative control and CP was used as positive control. No effect was observed in the groups of the test substance. Significant effects were observed in the postive control group. In conclusion, the test item did not induce clastogen effect in the bone marrow cells of mice under the test condition.
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