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EC number: 242-056-0 | CAS number: 18171-19-2
- 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:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 1995-11-07 to 1995-12-12
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study was conducted according to the appropriate OECD test guideline, and in compliance with GLP. The original study was considered reliability 1. Read-across to the registered substance is considered scientifically justified and is reliability 2.. The data are read across from (3-chloropropyl)diethoxymethylsilane (CAS 13501-76-3).
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 996
- Report date:
- 1996
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- 1992
- Deviations:
- yes
- Remarks:
- 1600 PCE scored instead of 2000 (due to shift towards NCE)
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- (3-chloropropyl)diethoxymethylsilane
- EC Number:
- 236-828-6
- EC Name:
- (3-chloropropyl)diethoxymethylsilane
- Cas Number:
- 13501-76-3
- Molecular formula:
- C8H19ClO2Si
- IUPAC Name:
- 3-chloropropyl(diethoxy)methylsilane
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 Winklemann, Borchen, Germany
- Age at study initiation: young adult
- Weight at study initiation: 35.8 ± 7.2 grams (male) / 31.8 ± 6.4 grams (female)
- Assigned to test groups randomly: yes, under following basis: colour code applied to the back of each animal; cage cards
- Fasting period before study: 16 - 18 hours prior to dosing procedure
- Housing: conventional, 5 animals/sex/Makrolon cage type III
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: ≥ 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 3 ˚c
- Humidity (%): 30 - 70 %
- Air changes (per hr): 15 changes per hour
- Photoperiod (hrs dark / hrs light): 12 hours dark / 12 hours light
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: corn oil
- Details on exposure:
- Route of exposure: intraperitoneal
- Duration of treatment / exposure:
- 24 to 48 hours
- Frequency of treatment:
- Test compound and controls were administered once by intraperitoneal injection 10 ml/kg bw.
- Post exposure period:
- The positive control group was sacrificed 24 hours after administration of the test substance. The vehicle control and test substance groups were sacrificed 24 - 48 hours after administration of the test substance.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
1600 mg/kg bw
Basis:
nominal conc.
- No. of animals per sex per dose:
- Five
- 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: pure erythrocyte suspension was used to prepare flat cells on glass by means of a Shandon Cytospin 3 (2 slides per animal). Slides were air dried and stained with May-Grundwald/Giemsa
METHOD OF ANALYSIS: A MIAMED image analyser equipped with the "Micronucleus Test V 4.00" software was used for fully automated slide scoring. Where possible, a total of approximately 2000 PCE (i.e. 10,000 PCE per treatment group) were analysed for micronuclei. The corresponding NCE were also scored for micronuclei. As an indicator for chemical-induced bone marrow toxicity, for each animal the PCE/NCE ratio was determined on the basis of 2000 PCE scored. - Evaluation criteria:
- A test compound is considered an inducer of micronuclei in PCE, if at least one group of mice treated with the test compound reveals a statistically and biologically relevant increase in micronucleated PCE compared with the negative control.
- Statistics:
- Means and standard deviations of the following parameters were calculated for each treatment group:
-the number of PCE with micronuclei
-the number of NCE with micronuclei
-the PCE/NCE ratio.
"Statgraphics" statistical software was used to analyse data. Test compound groups were compared with negative control groups of the same sampling time. Heterogeneity between animals of the same dose group was tested for by calculating the heterogeneity χ2 for the differences between the proportions of micronuclei for each animal. Pearson's contingency χ2 with one degree of freedom including a Yates correcting factor used to make comparisons in homogenous groups. In the case of inhomogeneity between groups, after transformation of the data, a one-sided two-sample t-test is performed, and can also be used to compare the micronucleus frequencies of the positive control with the negative control groups for comparison of PCE/NCE ratios.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- PCE/NCE ratio reduced
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- See table 3
Any other information on results incl. tables
Table 3: Results of in vivo micronucleus test with Wacker BS 1701
|
Vehicle Control |
Vehicle Control |
Positive Control |
1600 mg/kg bw |
1600 mg/kg bw |
|
Number of cells evaluated |
2000 approx. |
2000 approx. |
2000 approx. |
2000 approx. |
2000 approx. |
|
Sampling time (h) |
24 |
48 |
24 |
24 |
48 |
|
Number of erythro-cytes |
normochromatic |
NR |
NR |
NR |
NR |
NR |
polychromatic |
2000 approx. |
2000 approx. |
2000 approx. |
2000 approx. |
2000 approx. |
|
polychromatic with micronuclei (%) |
Male 0.16 % Female 0.13 % |
Male 0.20 % Female 0.11 % |
Male 4.1 % Female 2.2 % |
Male 0.15 % Female 0.13 % |
Male 0.2 % Female 0.18 % |
|
Ratio of erythrocytes |
polychromatic / normochromatic (ratio) |
Male 0.7 Female 0.81 |
Male 0.48 Female 1.38 |
Male 0.57 Female 0.83 |
Male 0.1 Female 0.14 |
Male 0.07 Female 0.09 |
polychromatic with micronuclei / normochromatic |
NR |
NR |
NR |
NR |
NR |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
(3-chloropropyl)diethoxymethylsilane was tested in an in vivo mouse micronucleus assay to EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test) and under GLP. No evidence for test substance mediated induction of micronuclei was observed. It is noted that the PCE / NCE ratio was reduced in the test substance-treated animals indicating the test substance had reached the target tissue. It is concluded that the test substance is not genotoxic under the conditions of the test. The result is a read across from (3-chloropropyl)diethoxymethylsilane (CAS 13501-76-3).
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