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EC number: 260-350-7 | CAS number: 56706-10-6
- 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 / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1 September 1998 - 3 October 1998
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 4,4,13,13-tetraethoxy-3,14-dioxa-8,9-dithia-4,13-disilahexadecane
- EC Number:
- 260-350-7
- EC Name:
- 4,4,13,13-tetraethoxy-3,14-dioxa-8,9-dithia-4,13-disilahexadecane
- Cas Number:
- 56706-10-6
- Molecular formula:
- C18H42O6S2Si2
- IUPAC Name:
- 4,4,13,13-tetraethoxy-3,14-dioxa-8,9-dithia-4,13-disilahexadecane
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan-Winkelmann GmbH, D-33176 Borchen
- Age at study initiation: approximately 7 weeks
- Weight at study initiation: males: 27.4-33.8 g; female: 22.0-26.1g
- Assigned to test groups randomly: yes, under following basis: computerised random number generator.
- Fasting period before study:
- Housing: Macrolon cages type II, 1 animal per cage
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: at least 6 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21.0-21.5°C
- Humidity (%): 50-57%
- Air changes (per hr):
- Photoperiod (hrs dark / hrs light): 12 hrs dark/12 hrs light
IN-LIFE DATES: From: To: 3 Sept 1998
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: peanut oil
- Lot/batch no. (if required): 1936301 - Details on exposure:
- Route of exposure: intraperitoneal
- Duration of treatment / exposure:
- 46-48 hours
- Frequency of treatment:
- 2 intraperitoneal administrations of 10 ml/kg bw with an interval of approximately 24 hours (test material and negative control group). Positive control group received a single injection of 10 ml/kg bw
- Post exposure period:
- Animals were sacrificed 22-24h after second (test and negative control) or single (positive control) administration.
Doses / concentrations
- Dose / conc.:
- 2 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 7
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- - cyclophosphamide
- Justification for choice of positive control(s): standard guideline positive control
- Route of administration: intraperitoneal
- Doses / concentrations: 10 ml/kg bw of 0.9% solution in physiological saline
Examinations
- Tissues and cell types examined:
- See table 2
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: limit dose
TREATMENT AND SAMPLING TIMES (in addition to information in specific fields): no further information
DETAILS OF SLIDE PREPARATION: centrifuged cells were suspended in a thin layer of serum, and a small drop was smeared on a slide and air-dried overnight. The dried slides were stained using the panoptic stain method of Pappenheim (Queisser W (1978) Das Knochenmark, Georg Thieme Verlag, Stuttgart)
METHOD OF ANALYSIS: microscopic examination. 2000 PCE scored for incidence of polychromatic erythrocytes with micronuclei. Ratio of PCE/NCE was scored based on 1000 erythrocytes (PCE+NCE) - Statistics:
- Frequencies of PCE with micronuclei of test material and of positive control group were compared with those of the negative control group. A Poisson test was applied. Data from each treatment group for each sex and for the sexes combined were compared with appropriate negative control using software from ASTA medica AG and an Alpha computer (Digital Equipment Corp)
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- See table 3
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay): negative
- Ratio of PCE/NCE (for Micronucleus assay): see table 3. The PCE/NCE ratio was unchanged in treated animals, so there is no evidence that the test substance reached the target tissue.
- Appropriateness of dose levels and route: appropriate dose and route
- Statistical evaluation: no statistically significant induction of micronuclei occurred
Any other information on results incl. tables
Table 3: Results of in vivo micronucleus test with Silane Si 266
|
Vehicle Control |
Positive control |
2000 mg/kg bw |
|
Number of cells evaluated |
2000 |
2000 |
2000 |
|
Sampling time (h) |
24 |
24 |
24 |
|
Number of erythrocytes per animal |
normochromatic |
NR |
NR |
NR |
polychromatic |
2000 |
2000 |
2000 |
|
polychromatic with micronuclei |
3.4 |
38.1 |
3.4 |
|
Ratio of erythrocytes |
polychromatic / normochromatic |
1.9* |
1.5* |
1.8* |
polychromatic with micronuclei / normochromatic |
NR |
NR |
NR |
* Mean calculated from data for individual animals
PCE polychromatic erythrocyte
NR not recorded
Applicant's summary and conclusion
- Conclusions:
- S2 was tested in an in vivo mouse micronucleus assay conducted to OECD 474 and in compliance with GLP. No evidence of genotoxicity was observed under the conditions of the test. It should be noted that the PCE/NCE ratio was unchanged in treated animals, so there is no evidence that the test substance reached the target tissue. It is concluded that the test substance is negative for the induction of micronuclei in vivo.
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