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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
Repeated dose toxicity: inhalation
Administrative data
- Endpoint:
- short-term repeated dose toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 14.08.1989 to 08.09.1989
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- The restrictions were that only one dose and males were tested, and limited examinations were performed, i.e. no haematology, biochemistry or urinalysis. However, this study was performed primarily to investigate effects on the larynx.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 412 (Subacute Inhalation Toxicity: 28-Day Study)
- Deviations:
- yes
- Remarks:
- only one concentration used, only males, limited examinations, i.e. no haematology, biochemistry or urinalysis.
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 3-Glycidoxypropyltrimethoxysilane hydrolysate
- IUPAC Name:
- 3-Glycidoxypropyltrimethoxysilane hydrolysate
- Reference substance name:
- not yet allocated
- IUPAC Name:
- not yet allocated
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, NY.
- Age at study initiation: 41 days
- Weight at study initiation: 131.2 + 9.0 grams
- Fasting period before study: No data
- Housing: 1/2 per cage in stainless steel, wire-mesh cages.
- Diet (e.g. ad libitum): Ad libitum (except during exposure period)
- Water (e.g. ad libitum): Ad libitum (except during exposure period)
- Acclimation period: Two days
ENVIRONMENTAL CONDITIONS
- Temperature (°F): 62-70 (17-21°C)
- Humidity (%): 45-77
- Air flow: 300l/min (13.5 changes/min)
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 14.08.1989 to 08.09.1989
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- whole body
- Vehicle:
- other: unchanged (no vehicle)
- Remarks on MMAD:
- MMAD / GSD: MMAD was 2.93 (±1.71) microns
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: The inhalation chambers used in the study were constructed of stainless steel with glass windows for animal observations, with a volume of approximately 1300 litres.
- Method of holding animals in test chamber: Free
- Source: No data
- Method of conditioning air: No data
- System of generating particulates/aerosols: A 2% TMSPGE-hydrolysate solution was prepared daily and was metered from a piston pump into an atomizer fitted with a liquid nozzle and an air nozzle. The atomizer was inserted into the top of the inhalation chamber turret where the liquid aerosol was dispersed throughout the chamber by filtered chamber supply air. The operating pressure of the atomizer used to generate the TMSPGE-hydrolysate was 20 psig.
- Temperature, humidity, pressure in air chamber: 18.5-19.9oC, 84.9-93.8%
- Air flow rate: 300 L/min
- Air change rate: 13.5/min
- Method of particle size determination: The particle size distribution was measured using a TSI Aerodynamic Particle Sizer and a 20:1 diluter. These determinations were made once a day for the duration of the study. The data collected were analysed by probit analysis to obtain the mass median aerodynamic diameter (MMAD) and the geometric standard deviation (sg).
- Treatment of exhaust air: No data
TEST ATMOSPHERE
- Brief description of analytical method used: Chamber concentrations of TMSPGE-hydrolysate were determined by gravimetric methods. Four samples were obtained from the TMSPGE-hydrolysate aerosol exposure chamber each day. The nominal concentration was calculated daily by dividing the total amount of material delivered to the chamber by the total airflow rate.
- Samples taken from breathing zone: No data
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Chamber concentrations of TMSPGE-hydrolysate were determined by gravimetric methods. Four samples were obtained from the TMSPGE-hydrolysate aerosol exposure chamber each day. The nominal concentration was calculated daily by dividing the total amount of material delivered to the chamber by the total airflow rate.
- Duration of treatment / exposure:
- 6 hours/day
- Frequency of treatment:
- Five days per week for three weeks followed by four days of exposure during the fourth week for a total of 19 exposures over a 4-week period
Doses / concentrationsopen allclose all
- Dose / conc.:
- 119 mg/m³ air (analytical)
- Dose / conc.:
- 150 mg/m³ air (nominal)
- No. of animals per sex per dose:
- 15 males
- Control animals:
- yes
- Details on study design:
- - Dose selection rationale: No data
- Rationale for selecting satellite groups: Five of the 15 test and control animals were assigned to a satellite group for ultrastructural evaluation of the larynges. However, this was not performed.
- Post-exposure recovery period in satellite groups: None - Positive control:
- None
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
The rats were observed daily during exposure and observations were recorded on a group basis. Preceding and following each exposure, observations were recorded for animals exhibiting overt clinical signs. At the time of body weight collection and just preceding necropsy, detailed observations were performed on all animals. On non-exposure days, animals were observed once a day for overt clinical signs and mortality.
DETAILED CLINICAL OBSERVATIONS: No
BODY WEIGHT: Yes
- Time schedule for examinations: Individual body weights were measured prior to initiation of the first exposure, weekly and immediately prior to sacrifice.
FOOD CONSUMPTION:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: 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: No
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: Males: days -4 and 11; females: days -5 and 10
- Dose groups that were examined: Control and test.
HAEMATOLOGY: No
CLINICAL CHEMISTRY: No
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- Ten animals of the test material hydrolysate treated and control groups were sacrificed on the day following the 19th exposure. A complete necropsy was performed on these animals and the following tissues were fixed in 10% neutral buffered formalin for histologic evaluation: gross lesions, larynx, lungs, trachea, nasal turbinates and kidneys. The remaining two rats from the control group were subjected to a complete necropsy and perfusion-fixed with 5% methanol-free EM grade formaldehyde. The perfusion-fixation was performed to allow comparison of these control rats with rats from another silane group that was also perfusion-fixed. The larynges from these two rats were then further immersion-fixed in 2% glutaraldehyde. Other organs, including brain, spinal cord, and peripheral nerves, were taken from these control animals and processed for light microscopic evaluation.
- Other examinations:
- The satellite group (5 test material hydrolysate treated and 5 control animals) was sacrificed on the day following the 18th exposure. The larynges of three control animals and five test material hydrolysate treated animals were taken and immersion-fixed in 2% glutaraldehyde for possible electron microscopic examination.
- Statistics:
- The data for continuous, parametric variables were intercompared for the exposure and control groups by use of Levene's test for homogeneity of variances and by t-tests. If Levene's test indicated homogeneous variances, the groups were compared by pooled variance t-tests. If Levene's test indicated heterogeneous variances, the groups were compared by separate variance t-test. Frequency data were compared using Fisher's exact tests. All statistical tests, except the frequency comparisons, were performed using BDMP Statistical Software (Dixon, 1985). The frequency data tests are described in Biometry (Sokal and Rohlf, 1969). The probability value of p < 0.05 (two-tailed) was used as the critical level of significance for all tests.
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- No mortality or exposure-related clinical signs were observed during the study.
- Mortality:
- no mortality observed
- Description (incidence):
- No mortality or exposure-related clinical signs were observed during the study.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Decreases in absolute body weight and/or body weight gain were observed for the test material hydrolysate treated animals during each week of the study. At the end of the study the percent decrease in mean body weight of the test material hydrolysate exposed group compared to the control group was 11%. At the end of the study the percent decrease in mean body weight gain of the test material hydrolysate exposed group compared to the control group was 29%.
- 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:
- no effects observed
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- No adverse findings.
- Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- No abnormal findings.
- Histopathological findings: neoplastic:
- not examined
Effect levels
- Dose descriptor:
- NOAEC
- Basis for effect level:
- other: No NOAEC was identified.
- Remarks on result:
- not determinable
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
No NOAEC identified
Table 1 - Individual body weight (grams), males group for 0 mg/m3
Week 0 | Week 1 | Week 2 | Week 3 | Week 4 | |
Animal 1 | 114.4 | 123.2 | 151.8 | 178.2 | 199.5 |
Animal 2 | 123.7 | 134.7 | 165.3 | 193.4 | 213.2 |
Animal 3 | 119.5 | 130.3 | 158.6 | 186.8 | 208.3 |
Animal 4 | 123.7 | 136.9 | 167.0 | 194.3 | - |
Animal 5 | 125.8 | 136.0 | 160.0 | 184.3 | 200.2 |
Animal 6 | 121.7 | 129.8 | 151.7 | 169.7 | 188.9 |
Animal 7 | 127.5 | 136.5 | 163.2 | 183.7 | - |
Animal 8 | 130.1 | 140.8 | 164.9 | 188.6 | 200.8 |
Animal 9 | 137.3 | 148.6 | 179.8 | 207.3 | - |
Animal 10 | 132.7 | 141.1 | 165.1 | 106.3 | - |
Animal 11 | 138.7 | 145.0 | 179.2 | 208.1 | 228.4 |
Animal 12 | 132.8 | 140.9 | 163.9 | 186.4 | 211.5 |
Animal 13 | 141.4 | 154.2 | 190.5 | 219.5 | - |
Animal 14 | 143.9 | 158.0 | 195.8 | 225.9 | 247.4 |
Animal 15 | 153.9 | 104.8 | 200.1 | 231.0 | 253.4 |
Mean | 131.1 | 141.4 | 170.5 | 196.2 | 215.1 |
St. dev. | 10.5 | 11.2 | 15.1 | 18.1 | 21.4 |
M | 15.0 | 15.0 | 15.0 | 15.0 | 10.0 |
Table 2 - Individual body weight (grams), males with 150 mg/m3
Week 0 | Week 1 | Week 2 | Week 3 | Week 4 | |
Animal 1 | 117.4 | 123.2 | 143.1 | 154.7 | 176.9 |
Animal 2 | 132.6 | 120.2 | 142.7 | 160.1 | 177.6 |
Animal 3 | 121.8 | 126.2 | 139.4 | 153 | 166.8 |
Animal 4 | 127.7 | 132.1 | 150.2 | 168.1 | - |
Animal 5 | 123.9 | 128.7 | 149.7 | 173.8 | - |
Animal 6 | 131.1 | 137.6 | 163.3 | 186.3 | 202.1 |
Animal 7 | 131.8 | 135.7 | 160.4 | 180.5 | - |
Animal 8 | 131.9 | 138.2 | 157.8 | 178.5 | 192.3 |
Animal 9 | 133.7 | 139.8 | 163.4 | 180 | 193.6 |
Animal 10 | 134.4 | 140.4 | 152..9 | 165.7 | 182.4 |
Animal 11 | 132.3 | 138.3 | 154.3 | 175.1 | 193.2 |
Animal 12 | 138.5 | 146.6 | 188.4 | 187.9 | - |
Animal 13 | 138.8 | 145.1 | 171.6 | 195.9 | 212.3 |
Animal 14 | 145 | 152.5 | 173.9 | 196 | 213.7 |
Animal 15 | 138.3 | 145.5 | 163.9 | 186.5 | - |
Mean | 131.4 | 137.3 | 156.9 | 178.8 | 191.3 |
St. dev. | 7.52 | 0.32 | 10.54 | 12.73 | 15.47 |
M | 15 | 15 | 15 | 15 | 10 |
Please see attached documents for all gained result tables.
Applicant's summary and conclusion
- Conclusions:
- In a four-week repeated inhalation study (reliability score 2) conducted using a protocol similar to OECD 412 (with restrictions) and GLP, rats were exposed to an aerosol of 3-glycidoxypropyltrimethoxysilane hydrolysate at a concentration of 119 mg/m3. Significant reductions in body weight gain were observed and therefore the NOAEC was <119 mg/m3. There was no evidence of laryngeal granuloma formation.
- Executive summary:
In a four-week repeated inhalation study (reliability score 2) conducted using a protocol similar to OECD 412 (with restrictions) and GLP, rats were exposed to an aerosol of 3-glycidoxypropyltrimethoxysilane hydrolysate at a concentration of 119 mg/m3. Significant reductions in body weight gain were observed and therefore the NOAEC was <119 mg/m3. There was no evidence of laryngeal granuloma formation.
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