Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 219-784-2 | CAS number: 2530-83-8
- 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
Carcinogenicity
Administrative data
Description of key information
In a dermal carcinogenicity study (BRRC, 1982) conducted to GLP, 25 µl of 25% [3-(2,3-epoxypropoxy)propyl]trimethoxysilane in acetone was not carcinogenic in male C3H mice when administered three times per week.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Link to relevant study records
- Endpoint:
- carcinogenicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- This study was designed to determine the dermal carcinogenic potential of the test material by applying it to the skin of male C3H/HeJ mice over the period of their lifetime and determining the gross and microscopic appearance of the resulting lesions.
- GLP compliance:
- yes
- Species:
- mouse
- Strain:
- C3H
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Jackson Laboratories, ME
- Age at study initiation: 51 to 76 days.
- Weight at study initiation: No data
- Fasting period before study: No data
- Housing: Five per cage in stainless steel suspended cages.
- Diet (e.g. ad libitum): Ad libitum
- Water (e.g. ad libitum): Ad libitum
- Acclimation period: No data
ENVIRONMENTAL CONDITIONS
- Temperature (°C): No data
- Humidity (%): No data
- Air changes (per hr): No data
- Photoperiod (hrs dark / hrs light): No data
IN-LIFE DATES: From: 12.03.1979 until death of animal. - Route of administration:
- dermal
- Vehicle:
- acetone
- Details on exposure:
- TEST SITE
- Area of exposure: No data
- % coverage: No data
- Type of wrap if used: No data
- Time intervals for shavings or clippings: Fur clipped once per week.
REMOVAL OF TEST SUBSTANCE
- Washing (if done): No data
- Time after start of exposure: No data
TEST MATERIAL
- Amount(s) applied (volume or weight with unit): 25 µl
- Concentration (if solution): 25%
- Constant volume or concentration used: yes
VEHICLE
- Justification for use and choice of vehicle (if other than water): No data
- Amount(s) applied (volume or weight with unit): No data
- Concentration (if solution): 25%
- Lot/batch no. (if required): No data
- Purity: 100%
USE OF RESTRAINERS FOR PREVENTING INGESTION: No data - Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- Lifetime
- Frequency of treatment:
- 3 applications/week (Monday, Wednesday and Friday)
- Post exposure period:
- None
- Dose / conc.:
- 5 mg/kg bw/day
- Dose / conc.:
- 25 other: µl of 25% of the test material in acetone/application
- No. of animals per sex per dose:
- 40
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Post-exposure period: Not applicable
- Positive control:
- 0.1% methylcholanthrene in acetone
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Daily for mortality
DETAILED CLINICAL OBSERVATIONS: No
DERMAL IRRITATION (if dermal study): Yes
- Time schedule for examinations: Carefully examined for skin lesions once per month.
BODY WEIGHT: No
FOOD CONSUMPTION:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: No
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: No
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: No
CLINICAL CHEMISTRY: No
URINALYSIS: No - Sacrifice and pathology:
- A necropsy was performed on all dead mice and on moribund mice, which were sacrificed. A necropsy consisted of a careful examination of the skin and body cavities. All observations were recorded. The dorsal skin and any suspect internal tumours from all non-autolyzed mice were fixed in 10% neutral buffered formalin. Tissues fixed in formalin were carefully trimmed, embedded, sectioned and stained with haematoxylin and eosin for examination by a pathologist. All neoplastic and non-neoplastic lesions discovered during the histopathologic examination were recorded and tabulated.
- Statistics:
- Mortality rates and skin tumour incidence were compared by the product-limit method. The Mantel-Cox and Breslow statistics were used to test the equality of the survival and time-to-tumour curves.
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- The mean survival time of the test material group was 482 days versus 502 days for the acetone controls. The difference was not statistically significant. The mean survival time in the methylcholanthrene (MC) group was 204 days reflecting the early mortality associated with the high incidence of skin tumours.
- Mortality:
- no mortality observed
- Body weight and weight changes:
- not examined
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- See Table 1. No epidermal or subcutaneous tumours were observed in the test material group. Eight animals had hyperkeratosis (compared to the acetone controls) suggesting a possible irritating effect on the epidermis. No epidermal tumours were observed in the group treated with acetone though two mice had subcutaneous sarcomas outside the treatment area (one subcutaneous fibrosarcoma of the left foreleg and one subcutaneous lymphosarcoma over the left hip). One mouse had epidermal hyperplasia. The positive control (MC) group had 39 animals with skin tumours including 33 with confirmed squamous cell carcinomas, two mice with papillomas four mice had gross carcinomas that were not confirmed histologically because of cannibalism. These results confirm the sensitivity of the animals to a known skin carcinogen.
- Histopathological findings: neoplastic:
- no effects observed
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- >= 5 other: mg/kg bw/day for 3 applications per week
- Sex:
- male
- Basis for effect level:
- other: No effects observed.
- Critical effects observed:
- not specified
- Conclusions:
- In a dermal carcinogenicity study (reliability score 2) conducted to GLP, 25 µl of 25% of the test material in acetone was not carcinogenic in male C3H mice when administered three times per week.
- Executive summary:
In a dermal carcinogenicity study (reliability score 2) conducted to GLP, 25 µl of 25% of the test material in acetone was not carcinogenic in male C3H mice when administered three times per week.
Reference
Table 1 Summary of tumour data
Test material | MC | Acetone | |
Concentration | 25% | 0.1% | 100% |
Volume (µ l) | 25 | 25 | 25 |
Mean survival time (d) | 482 | 204 | 502 |
Animals with papillomas | 0 | 2 | 0 |
Animals with carcinomas | 0 | 37 | 0 |
Animals with subcutaneous sarcomas | 0 | 0 | 2 |
Time to first skin tumour (d) | - | 31 | - |
Time to median skin tumour (d) | - | 92 | - |
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 5 mg/kg bw/day
- Study duration:
- chronic
- Species:
- mouse
Justification for classification or non-classification
Based on the available evidence, [3-(2,3-epoxypropoxy)propyl]trimethoxysilane does not require classification for carcinogenicity according to Regulation (EC) 1272/2008.
Additional information
Two dermal carcinogenicity studies are available. These studies are of limited value in addressing the carcinogenicity endpoint, but together provide good negative evidence for dermal carcinogenicity.
A dermal carcinogenicity study which meets generally accepted scientific principles but was not conducted in compliance with GLP found [3-(2,3-epoxypropoxy)propyl]trimethoxysilane (CAS 2530-83-8) not carcinogenic in male C3H mice when administered three times per week for the duration of a lifespan (BRRC, 1982). The NOAEL for carcinogenicity is reported to be >= 5 mg/kg bw/day for 3 applications per week. The test material was administered at 25% in acetone per application to 40 animals per sex per dose. A necropsy was performed on all dead mice and on moribund mice which were sacrificed. The necropsy consisted of a careful examination of the skin and body cavities, with all observations recorded as suspect internal tumours subjected to histopathological analysis. No epidermal or subcutaneous tumours were observed in the test group, with appropriate positive and negative control groups and expected results (BRRC, 1982).
A second dermal carcinogenicity study was also available for the registered substance, which found [3-(2,3-epoxypropoxy)propyl]trimethoxysilane (CAS 2530-83-8) not carcinogenic in C3H mice when administered three times per week for the duration of a lifespan (Oak Ridge National Laboratory, 1987). The NOAEL for carcinogenicity is reported to be >11.1 mg/kg bw/day (male/female) for 3 applications per week. The test material was administered at 46.8, 62.4 and 78 mg/week in 50 µl cyclohexane to 40 animals per sex per dose. A necropsy was performed on all dead mice and on moribund mice which were sacrificed. The necropsy consisted of a careful examination of the skin and body cavities, with all observations recorded as suspect internal tumours subjected to histopathological analysis. None of the materials caused a significant increase in skin tumours. The only tumours (benign papillomas) were in the cyclohexane solvent control groups. There was a dose-dependent and marked increase in skin cancer with benzo(a)pyrene. The 24-month survival rates were 52.6, 32.5 and 48.7 % for females and 47.5, 51.3 and 51.3 % for males of the 46.8, 62.4 and 78 mg/week groups, respectively. The mid-dose females were significantly reduced compared with the solvent controls. In addition, there were no apparent treatment-related effect on body weight and organ weight (Oak Ridge National Laboratory, 1987).
The study was conducted
according to a scientifically acceptable protocol.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.