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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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 04.12.1990 to 22.11.1993
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 993
- Report date:
- 1993
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- Dosing during organogenesis only.
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- [3-(2,3-epoxypropoxy)propyl]trimethoxysilane
- EC Number:
- 219-784-2
- EC Name:
- [3-(2,3-epoxypropoxy)propyl]trimethoxysilane
- Cas Number:
- 2530-83-8
- Molecular formula:
- C9H20O5Si
- IUPAC Name:
- trimethoxy[3-(oxiran-2-ylmethoxy)propyl]silane
Constituent 1
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Hazleton Dutchland Laboratories, Inc
- Age at study initiation: 5.5 months old
- Weight at study initiation: 3.0 to 4.0 kg
- Fasting period before study: No data, but probably not
- Housing: Individually in stainless steel, wire mesh cages
- Diet (e.g. ad libitum): Ad libitum
- Water (e.g. ad libitum): Ad libitum
- Acclimation period: 16 days
ENVIRONMENTAL CONDITIONS
- Temperature (°F): 61-70 (16-21°C)
- Humidity (%): 40-60
- Air changes (per hr): No data
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 04.12.1990 To: 22.11.1993
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: The appropriate amount of A-187 was dissolved with Mazola corn oil. Solutions were mixed manually by repeated inversions and then transferred to a glass Erlenmeyer flask and mixed for at least 10 minutes. Dosing solutions were prepared based on the selected dose and administration of a constant dose volume of 2ml/kg/day. Target concentrations of solutions for the 50, 200 and 400 mg/kg/day dose levels were 25, 100 and 200 mg/ml, respectively. Dosing solutions were prepared three times during the study and were stored at room temperature. Dosing solutions were stirred using a magnetic stirrer for at least 10 minutes prior to each daily dosing period.
VEHICLE
-No details on vehicle. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Concentrations of the dosing solutions were verified prior to use in the study using gas chromatography. Homogeneity of A-187 in each solution was established. Homogeneity and stability of the dosing solutions were initiated prior to the onset of actual dosing.
- Details on mating procedure:
- - Impregnation procedure: No data. Report states that "females were mated to proven males from the BRRC breeding colony. Following successful copulation, the animals were returned to their respective cages"
- If cohoused:
- M/F ratio per cage: No data
- Length of cohabitation: No data
- Further matings after two unsuccessful attempts: No data
- Verification of same strain and source of both sexes: No data
- Proof of pregnancy: Date of copulation referred to as day 0 of pregnancy - Duration of treatment / exposure:
- Test substance exposure occurred during the primary period of organogenesis, i.e., gestation days 6-18.
- Frequency of treatment:
- Once per day on gestation days 6-18
- Duration of test:
- 25 days (animals sacrificed on gestational day 29)
Doses / concentrationsopen allclose all
- Dose / conc.:
- 50 mg/kg bw/day
- Dose / conc.:
- 200 mg/kg bw/day
- Dose / conc.:
- 400 mg/kg bw/day
- No. of animals per sex per dose:
- 22 females
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Based on the results from three developmental toxicity range-finding studies of Union Carbide Organofunctional Silane A-187 in pregnant New Zealand white rabbits.
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Observations for mortality and clinical condition were performed daily (twice daily during the dosing period).
DETAILED CLINICAL OBSERVATIONS: No data
BODY WEIGHT: Yes
- Time schedule for examinations: Maternal body weights were measured on gestational days 0, 6, 12, 15, 18 and 29.
FOOD CONSUMPTION: Yes, food consumption was measured daily throughout gestation (gestation days 0-29).
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
WATER CONSUMPTION: No
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 29
- Organs examined: Uterus, ovaries (including corpora lutea), cervix, vagina and abdominal and thoracic cavities. Liver was weighed. - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes, each uterus was externally examined for signs of haemorrhage, removed from the peritoneal cavity, weighed and dissected longitudinally to expose the contents.
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes - Fetal examinations:
- - External examinations: Yes: [all per litter]
- Soft tissue examinations: Yes: [half per litter]
- Skeletal examinations: Yes: [half per litter]
- Head examinations: Yes: [half per litter] - Statistics:
- The unit of comparison was the pregnant female or the litter. Data collected for non-pregnant females were not included in the statistical analyses. Results of the quantitative continuous variables (e.g., maternal body weights, organ weights, etc.) were intercompared for the three exposed groups and the vehicle control group by use of Levene's test for equal variances (Levene, 1960), analysis of variance (ANOVA), and t-tests with Bonferroni probabilities for pairwise comparisons. The t-tests were used when the F value from the ANOVA was significant. When Levene's test indicated homogeneous variances and the ANOVA was significant, the pooled t-test was used. When Levene's test indicated heterogeneous variances, all groups were compared by an ANOVA for unequal variances (Brown and Forsythe, 1974) followed, when necessary, by the separate variance t-test. Nonparametric data obtained following laparohysterectomy were statistically treated using the Kruskal-Wallis test (Sokal and Rohlf, 1969) followed by the Mann-Whitney U test (Sokal and Rohlf, 1969) when appropriate. Incidence data were compared using Fisher's Exact Test (Sokal and Rohlf, 1969). For all statistical tests, the fiducial limit of 0.05 (two-tailed) was used as the criterion for significance.
- Indices:
- No data
- Historical control data:
- No data
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- effects observed, non-treatment-related
- Description (incidence and severity):
- One dam from the 400 mg/kg bw/day group was found dead on gestation day 29. This animal exhibited gasping, and laboured and audible breathing. No significant clinical signs were observed in any other treatment group.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- One dam from the 400 mg/kg bw/day group was found dead on gestation day 29. This animal exhibited gasping, and laboured and audible breathing. No significant clinical signs were observed in any other treatment group.
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- no effects observed
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not specified
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- no effects observed
- Immunological findings:
- not specified
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- no effects observed
Maternal developmental toxicity
- Details on maternal toxic effects:
- One dam from the 400 mg/kg bw/day group was found dead on gestation day 29. This animal exhibited gasping, and laboured and audible breathing. No significant clinical signs were observed in any other treatment group. No statistically significant, treatment-related differences in body weight/body weight gain or food consumption were observed. There were no significant findings in the necropsy of the dam that died. There were no treatment-related findings from the necropsy of the surviving animals.
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Remarks:
- maternal toxicity
- Effect level:
- 200 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- mortality
- Dose descriptor:
- NOAEL
- Remarks:
- maternal developmental toxicity
- Effect level:
- >= 400 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: no maternal developmental toxicity was observed.
Maternal abnormalities
- Abnormalities:
- no effects observed
Results (fetuses)
- Fetal body weight changes:
- no effects observed
- Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Changes in litter size and weights:
- no effects observed
- Changes in postnatal survival:
- no effects observed
- External malformations:
- no effects observed
- Skeletal malformations:
- no effects observed
- Visceral malformations:
- no effects observed
- Other effects:
- no effects observed
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
There were no effects of the treatment on the number of ovarian corpora lutea, on the number of total, viable or non-viable (early and late resorptions and dead fetuses) implantations per litter or on sex ratio (% males). Percent pre-implantation and post-implantation losses were equivalent across groups. Fetal examination indicated no evidence of embryotoxicity or malformations in any of the treatment groups. There were no effects on mean fetal body weight and no treatment-related differences in the incidences of external, visceral or skeletal variations.
Effect levels (fetuses)
- Dose descriptor:
- NOAEL
- Effect level:
- >= 400 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: teratogenicity
Fetal abnormalities
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Developmental effects observed:
- no
Any other information on results incl. tables
Please see attached tables in attachments.
Applicant's summary and conclusion
- Conclusions:
- In a well conducted study (reliability score 1), conducted using a protocol similar to OECD Test Guideline 414 and GLP, the NOAEL for maternal toxicity and developmental toxicity were 200 and =400 mg/kg bw/day, respectively, in rabbits.
- Executive summary:
In a well conducted study (reliability score 1), conducted using a protocol similar to OECD Test Guideline 414 and GLP, the NOAELs for maternal toxicity and developmental toxicity were 200 and =400 mg/kg bw/day, respectively, in rabbits.
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