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EC number: 213-926-7 | CAS number: 1067-25-0
- 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
Endpoint summary
Administrative data
Description of key information
Oral (OECD 401): Males LD50 > 5170 mg/kg bw (limit test); Females LD50 = 5170 mg/kg bw (estimated)
Inhalation (OECD 403): LC50 > 22200 mg/m³
Dermal: There are no measured acute dermal toxicity data available (data waiving according to Column 2 of REACH Annex VIII, Section 8.5.3).
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 25 Feb 1987 to 12 March 1987
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Deviations:
- yes
- Remarks:
- Non GLP. No data on purity or stability. The females were tested at 2 doses, whereas at least 3 are recommended to permit an "acceptable determination of the LD50".
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Wistar Bor:WISW (SPFTNO)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Winkelmann Versuchstierzucht GmbH & Co., Borchen, GERMANY
- Age at study initiation: 57 days (males), 71-72 days (females)
- Weight at study initiation: 172-197 g (males), 146-164 g (females)
- Fasting period before study: 16 h
- Housing: Macrolon cages type II
- Diet: standard diet (Ssniff R, special diet for rats), ad libitum
- Water: drinking water, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 2
- Humidity (%): 55 ± 15
- Photoperiod (hrs dark / hrs light): 12 / 12
IN-LIFE DATES: From: 25 February 1988 To: 12 March 1988 - Route of administration:
- oral: gavage
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- MAXIMUM DOSE VOLUME APPLIED: 5.62 ml/kg bw
- Doses:
- 5170 mg/kg bw (males)
2401 or 5170 mg/kg bw (females) - No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: observation for mortality twice daily (once daily on weekends and holidays); clinical observations after treatment continuously for 4-6 h then daily; bodyweights on days 0, 7, 14.
- Necropsy of survivors performed: yes, macroscopic examination included external appearance, body orifices, body cavities (thoracic and abdominal), and their contents. - Statistics:
- None given. LD50 value for males is derived from a limit test (1 dose). The LD50 value for females (based on 2 doses) is described as an estimate.
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- > 5 170 mg/kg bw
- Based on:
- test mat.
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- ca. 5 170 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: Estimate
- Mortality:
- Two females died at 5170 mg/kg bw (3 - 4 hours after exposure). There were no deaths in males at this dose or in females at 2401 mg/kg bw.
- Clinical signs:
- other:
- Body weight:
- other body weight observations
- Remarks:
- See Table 2 (Any other information on results including tables).
- Gross pathology:
- The stomach and intestines of the two females that died were filled with liquid and the mucosa of the proventricular was red.
- Interpretation of results:
- other: CLP/EU GHS criteria are not met, no classification required according to Regulation (EC) No 1272/2008
- Conclusions:
- In an acute oral toxicity study conducted in compliance with the now deleted OECD 401, but not to GLP (reliability score 2), the LD50 values for trimethoxy(propyl)silane were > 5170 mg/kg bw in males and 5170 mg/kg bw (estimated) in females. These values indicate low acute toxicity by the oral route. The most common signs of toxicity were reduced locomotion, impaired co-ordination, loss of muscle tone and loss of righting reflex.
Reference
Table 1: Number of animals dead and with evident toxicity, and time range within which mortality occurred
Dose | Mortality (# dead/total) | Time range of deaths (hours) | Number with evident toxicity (#/total) | |||||
Male | Female | Combined |
| Male | Female | Combined | ||
2401 | - | 0/5 | 0/5 | n/a | Reduced locomotion Impaired co-ordination Loss of muscle tone Loss of righting reflex - lateral Loss of righting reflex - supine Loss of pinna, pain, corneal reflexes Clonic spasms Excitation-like twitching Ptosis (drooping eyelid) Lacrymation Mydriasis (dilated pupils) Hypersialosis (excessive salivation) Fur, ruffled Laboured breathing Reduced body temperature Abnormal gait Sunken flanks Cyanosis | - - - - - - - - - - - - - - - - - - | 4/5 4/5 2/5 1/5 1/5 0/5 1/5 0/5 0/5 1/5 0/5 0/5 1/5 0/5 1/5 1/5 2/5 0/5 | - - - - - - - - - - - - - - - - - - |
5170 | 0/5 | 2/5 | 2/10 | 3-4 h | Reduced locomotion Impaired co-ordination Loss of muscle tone Loss of righting reflex - lateral Loss of righting reflex - supine Loss of pinna reflex Loss of pain reflex Loss of corneal reflex Clonic spasms Excitation-like twitching Ptosis (drooping eyelid) Lacrymation Mydriasis (dilated pupils) Hypersialosis (excessive salivation) Fur, ruffled Laboured breathing Reduced body temperature Abnormal gait Sunken flanks Cyanosis | 5/5 5/5 4/5 2/5 2/5 0/5 0/5 0/5 1/5 0/5 0/5 0/5 0/5 0/5 0/5 4/5 0/5 0/5 1/5 0/5 | 4/5 4/5 3/5 3/5 3/5 2/5 2/5 2/5 0/5 1/5 2/5 0/5 2/5 4/5 1/5 4/5 2/5 1/5 3/5 2/5 | 9/10 9/10 7/10 5/10 5/10 2/10 2/10 2/10 1/10 1/10 2/10 0/10 2/10 4/10 1/10 8/10 2/10 1/10 4/10 2/10 |
Table 2: Body weights (g) – individual values
Dose (mg/bw day) | Animal No. | 0 d | 7 d | 14 d |
Males | ||||
5170 | 1 2 3 4 5 | 188 172 194 197 186 | 226 203 236 231 217 | 258 235 271 265 249 |
Females | ||||
2401 | 11 12 13 14 15 | 156 164 150 164 148 | 171 183 166 186 165 | 185 190 176 191 171 |
5170 | 6 7 8 9 10 | 150 162 154 146 149 | 168 182 - - 170 | 171 186 - - 178 |
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 5 170 mg/kg bw
- Quality of whole database:
- The available key study is considered adequate and reliable (Klimisch score 2), and is thus sufficient to fulfil the standard information requirements set out in Annex VII, 8.5.1, of Regulation (EC) No 1907/2006.
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 7 Feb 1990 to 21 Feb 1990
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Version / remarks:
- adopted 12 May 1981
- Deviations:
- yes
- Remarks:
- Deviations unlikely significantly to affect the outcome of the study: excursions from recommended relative humidity and temperature; limited reporting of clinical observations.
- GLP compliance:
- yes
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rat
- Strain:
- other: Wistar derived Crl:WI(WU)BR
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Sulzfeld, GERMANY
- Age at study initiation: 7 weeks
- Weight at study initiation: mean - 218 g (males), 166 g (females)
- Fasting period before study: none stated
- Housing: (after exposure) 5 males or 5 females per suspended stainless steel cage
- Diet: standard diet, ad libitum
- Water: drinking water, ad libitum
- Acclimation period: 15 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): during exposure: mean 22.6; after exposure: 22 ± 3 (excursion 18.5 for 1 h)
- Humidity (%): during exposure: mean 79 ± 15 (relative humidity was above 70% for about 2 hours, during the rest of the exposure humidity was between 30 and 70%); after exposure: 30 - 70 (excursions 29, 74, 95 for 1 h on each occasion)
- Air changes (per hr): during exposure: 38; after exposure: 10
- Photoperiod (hrs dark / hrs light): 12 h/12 h
IN-LIFE DATES: From: 1990-02-07 To: 1990-02-21 - Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- air
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: horizontal glass chamber; animals separated by perforated stainless steel plates
- Exposure chamber volume: 16 L (total volume)
- Method of holding animals in test chamber: see above
- Source and rate of air: 0.6 m³/h; flow velocity 34 m/h; ventilation frequency 38/h
- System of generating particulates/aerosols: heated air bubbled through heated test material at 35° C, passed through heated Pall filter (30° C) to remove aerosol as far as possible
- Method of particle size determination: to determine aerosol content: 11-stage cascade impactor
- Treatment of exhaust air: no details
- Temperature, humidity, pressure in air chamber: (mean of hourly measurements) 22.6° C; 79 ± 15%; pressure unstated
TEST ATMOSPHERE
- Brief description of analytical method used: hourly GC analysis
- Samples taken from breathing zone: yes
TEST ATMOSPHERE: 22.2 ± 6.9 g/m³ (4 measurements); nominal 59.8 g/m³; particle size tabulated (about 1% of the total test atmosphere consisted of aerosol). - Analytical verification of test atmosphere concentrations:
- yes
- Duration of exposure:
- 4 h
- Concentrations:
- Single exposure concentration:
22.2 ± 6.9 g/m³ (measured)
59.8 g/m³ (nominal) - No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: observations daily; body weights prior to exposure and on observation days 7 and 14.
- Necropsy of survivors performed: yes - Statistics:
- None relating to LC50.
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 22 200 mg/m³ air (analytical)
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Mortality:
- One of each sex died during exposure. One male died on observation Day 4 (see Table 2, Any other information on results incl. tables).
- Clinical signs:
- other: See field "Any other information on results incl. tables"
- Body weight:
- Body weights were generally not affected. Body weights were reduced in two females on Days 14, or 7 and 14 (see Attachment for tabulated data).
- Gross pathology:
- The lungs of the three animal that died during treatment or observation were discoloured red, spotted or swollen. No abnormalities were found in the remaining animals autopsied on Day 14.
- Other findings:
- None reported.
- Interpretation of results:
- other: CLP/EU GHS criteria are not met, no classification required according to Regulations (EC) No 1272/2008
- Conclusions:
- In an acute inhalation study according to OECD 403 and in accordance with GLP (reliability score 1) the LD50 for trimethoxy(propyl)silane was in excess of 22200 mg/m³ in the rat.
Reference
Clinical Signs
During the first 15 minutes of exposure animals were restless. Their eyes were half-closed and breathing was irregular. From 30 minutes and onward, rats seemed to be in narcosis, their breathing became deep and irregular. Directly after exposure, rats were still in narcosis. They showed dyspnoea and moist rales.
The first day of the 14-day observation period revealed wet nose and a dirty fur in several of the surviving rats. Thereafter, no abnormalities were observed. Just before death on Day 4 of the observation period, the male animal demonstrated lethargy, showed flabby muscles, incoordination, piloerection and a visually increased breathing frequency.
Exposure concentration and aerodynamic particle size
The mean actual concentration turned out to be 22.2 ± 6.9 g/m³. The standard deviation resulted from four measurements. The corresponding nominal concentration was 59.8 g/m³.
Particle size analysis is given in Table 1. The 50 percent accumulation point for the distribution was between 2.4 and 2.8 µm. However, the concentration of aerosol measured in this way turned out to be 0.2g/m³, indicating that a negligible amount of about one percent of the total test atmosphere consisted of aerosol.
Table 1: Aerodynamic particle size distribution
Aerodymamic diameter (µm) |
Distribution % of total mass (22.2 g/m³) |
<1 |
1.0 |
1 |
4.5 |
1.4 |
2.5 |
1.8 |
15.1 |
2.4 |
12.2 |
2.8 |
10.8 |
3.1 |
18.3 |
3.4 |
26.5 |
3.8 |
4.4 |
4.2 |
0.7 |
>4.2 |
3.9 |
Table 2: Concentrations, exposure conditions and mortality per animals treated
Nominal Conc. (g/m³) |
Analytical Conc. (g/m³ ± SD ) |
Mortality (dead/total) |
||
Males |
Females |
Combined |
||
59.8 |
22.2 +/- 6.9 |
2/5 |
1/5 |
3/10 |
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LC50
- Value:
- > 22 200 mg/m³ air
- Physical form:
- inhalation: vapour
- Quality of whole database:
- The available key study is considered adequate and reliable (Klimisch score 1), and is thus sufficient to fulfil the standard information requirements set out in Annex VIII, 8.5.1, of Regulation (EC) No 1907/2006.
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Studies were chosen as key when the available study was of relevance and of sufficient quality for classification, labelling and for risk assessment. Other available data are included as supporting studies.
Acute toxicity: oral
The key acute oral toxicity study on trimethoxy(propyl)silane (CAS 1067-25-0) was conducted in accordance to the now deleted OECD 401, but not according to GLP (ASTA Pharma, 1988). Five male and five female Wistar Bor:WISW (SPFTNO) rats per dose were administered the test item by single oral gavage application. Males were dosed at 5170 mg/kg bw and females were dosed at 2401 or 5170 mg/kg bw.
Clinical signs were characterized by reduced locomotion, reduced muscle tone, loss of righting reflexes, sunken flanks and laboured respiration. Further, ptosis, mydriasis, cyanosis, reduced body surface temperature and general lack of reflexes were observed prior to death in female animals. There were also isolated cases of clonic spasms, excitation-like twitching, lacrimation, hypersialosis, stalking gait and ruffled fur.
Initial symptoms of intoxication were observed 7 minutes after administration of the substance and lasted up to 2 days. Deaths occurred 3 and 4 hours, respectively, among the females after administration of 5170 mg/kg bw.
Necropsy of the two female animals that died revealed that the stomach and intestines were filled with liquid and the mucosa of the proventriculus was red.
The mean LD50 values were:
Male > 5170 mg/kg bw (limit test)
Females ca.5170 mg/kg bw (estimate)
An additional acute oral toxicity study on trimethoxy(propyl)silane (CAS 1067-25-0) was conducted similar to the now deleted OECD 401 and not to GLP (INBIFO, 1979). 10 male Sprague-Dawley rats per dose were administered 4.22, 5.62, 7.50, 10.0 or 13.3 g/kg bw via a single oral gavage application. Overt toxicity was evident in all dose groups. Effects included reduced to absent spontaneous activity, reaction to external stimuli, backtwist reflex, muscle tone, reaction to pain or corneal reflex. Five rats had blood in the urine. One rat that died had dark red lungs. General condition and behaviour of most rats had returned to normal after 2 days. Deaths within 14 days in the groups treated with 4.22, 5.62, 7.50, 10.0 or 13.3 g/kg bw were 0, 2, 3, 10 and 10, respectively. The LD50 value in male rats was calculated to be 7420 mg/kg bw.
Acute toxicity: inhalation
The key acute inhalation toxicity study on trimethoxy(propyl)silane (CAS 1067-25-0) was conducted in compliance with GLP and according to OECD 403 (TNO, 1990). Groups of five male and five female Crl:WI(WU)BR rats were exposed to vapours of the test item via whole body exposure at a concentration of 22.2 g/m3 for one single period of 4 hours.
Shortly after the beginning of exposure, restlessness started and irregular breathing was observed, followed by signs of narcosis, and deep and irregular breathing. Three rats died during or after exposure (two males and one female). Wet noses and dirty fur were common findings on the first day of the 14-day observation period.
Except for two females, body weight gain was not affected by exposure.
No abnormalities were observed at necropsy in the animals that survived to scheduled sacrifice at the end of the observation period. In the animals which died during or after exposure, dark-red discoloured, occasionally spotted and swollen, lungs were found.
It was concluded that the 4-hour LC50 value of trimethoxy(propyl)silane (vapour) in rats was > 22.2 g/m3.
An additional acute inhalation toxicity study on trimethoxy(propyl)silane (CAS 1067-25-0) was conducted similar to OECD 403, but not according to GLP (INBIFO, 1979). Groups of 10 male and 10 female Sprague Dawley rats were exposed to an aerosol of the test item via head-only exposure at measured concentrations of 6.6, 15.4, 19.9 ml/m³ for 6 hours.
Dose dependent narcotic effects were seen, characterized as follows: Apathy, slight trembling and spasms over the whole body, slight to severe ataxia, absent backtwist reflex. Reduction in respiration rate with partial intermittent respiration. Reduced to absent reaction to pain, reduced ability to grip as well as reduced ear muscle and corneal reflex. Mortality in the groups exposed to 0, 6.6, 15.4, or 19.9 ml/m³ of the test item was as follows: Males 1, 1, 0 and 8. Females 0, 3, 3 and 7.
It was concluded that the 6-hour LC50 value for trimethoxy(propyl)silane (aerosol) in rats was 15.2 g/m³ (dose given in ml/m3, converted using a relative density of 0.94).
Acute toxicity: dermal
No data available. In accordance with Column 2 of REACH Annex VIII, the acute toxicity study via the dermal route (required in Section 8.5.3 of REACH Annex VIII) does not need to be conducted because inhalation of the substance is likely.
Justification for classification or non-classification
The available data on acute toxicity (lethality) do not meet the criteria for classification according to Regulation (EC) No. 1272/2008, and are therefore conclusive but not sufficient for classification of the registered substance.
Classification as STOT-SE Cat 3, with the hazard statement 'H336: May cause drowsiness and dizziness' according to Regulation (EC) No. 1272/2008 is not warranted for the test substance. Although signs of narcosis were observed in the acute inhalation study, this was rather linked to the systemic effects provoked by the test substance after exposure at a concentration exceeding the limit dose stated in the corresponding OECD guideline. In addition the reported concentration could have been higher due to the whole-body inhalation and possible additional oral uptake of the test substance. Mortality and clinical signs as laboured breathing and lethargy were observed. At necropsy dark red discoloured lungs were reported, thus leading to the conclusion that the narcotic effects were rather a consequence of anoxia provoked by systemic effects.
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