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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 219-969-8 | CAS number: 2587-76-0
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Acute Toxicity: inhalation
Administrative data
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Not reported
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 974
- Report date:
- 1974
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Male and female rats were exposed to the test material as an aerosol mist for 4 hours.
- GLP compliance:
- no
- Remarks:
- Study conducted in 1974, prior to inception of GLP
- Test type:
- standard acute method
- Limit test:
- no
Test material
- Reference substance name:
- Chlorotrioctylstannane
- EC Number:
- 219-969-8
- EC Name:
- Chlorotrioctylstannane
- Cas Number:
- 2587-76-0
- Molecular formula:
- C24H51ClSn
- IUPAC Name:
- chlorotrioctylstannane
- Test material form:
- liquid
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: 54 Tif. RAI (SPF)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Bred in-house at the testing facility
- Age at study initiation: 7 to 8 weeks old
- Weight at study initiation: 175 to 185 g (male and female)
- Housing: The male and female rats were segregated (9 animals to a cage) during observation period
ENVIRONMENTAL CONDITIONS
- Temperature: 22 ± 1 °C
- Humidity: Approximately 50 % (relative)
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- nose only
- Vehicle:
- air
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: The exposure system used in the test was that described by Sachsse et al., 1974 (Sachsse K, Ullmann L, Voss G & Hess R: Measurement of inhalation toxicity of aerosols in small laboratory animals. Proceedings of the European Society for the study of Drug Toxicity Volume XV, 239, 1974). The animals were not exposed until the aerosol was evenly dispersed throughout the chamber (15 minutes).
- Method of holding animals in test chamber: The test animals were kept in separate PVC tubes positioned radially around the exposure chamber.
- Source and rate of air: The test material was sprayed into the exposure chamber by means of a pressure nozzle. The liquid was injected by a motor-driven syringe at a rate of 0.9, 3 and 12 mL/hr into a stream of compressed air (2 atm.) flowing through a spray nozzle at a rate of 10 L/min. The aerosol mist thus produced was discharged into the exposure chamber.
- Method of particle size determination: Gravimetrically
TEST ATMOSPHERE
- Brief description of analytical method used: The particle-size distribution in the aerosol was determined gravimetrically on Selectron-Filters, pore size 0.2 µm every hour with the aid of a Cascade Impactor (C.T. Casella and Co., Ltd).
- Samples taken from breathing zone: Yes. The aerosol in the immediate vicinity of the animals was sampled on membrane filters, pore size 0.2 µm (Satorius) hourly after the beginning of the test.
VEHICLE
- Concentration of test material in vehicle: 92, 224 and 718 mg/m³
TEST ATMOSPHERE
- At 92 mg/m³ the mean particle size distribution was 44, 19, 21 and 16 % of the particles >7, 3 to 7, 1 to 3 and <1 µm, respectively.
- At 224 mg/m³ the mean particle size distribution was 59, 16, 20 and 5 % of the particles >7, 3 to 7, 1 to 3 and <1 µm, respectively.
- At 718 mg/m³ the mean particle size distribution was 55, 14, 24 and 7 % of the particles >7, 3 to 7, 1 to 3 and <1 µm, respectively. - Analytical verification of test atmosphere concentrations:
- yes
- Duration of exposure:
- 4 h
- Concentrations:
- 92, 224 and 718 mg/m²
- No. of animals per sex per dose:
- 9 animals per sex per dose
- Control animals:
- not specified
- Details on study design:
- - Duration of observation period following administration: 7 days
- Frequency of observations and weighing: Clinical signs were recorded throughout the 7 day observation period.
- Necropsy of survivors performed: Yes
Results and discussion
Effect levels
- Key result
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- ca. 250 mg/m³ air
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Mortality:
- All of the 18 rats (9 male and 9 female) that were exposed to the lowest concentration of test material, 92 mg/m³, survived.
Three male and three female rats died between 24 and 48 hours after being exposed to the median test material concentration of 224 mg/m³. A further male rat died prior to the end of the 7 day observation period.
At the highest concentration of test material, 718 mg/m³, all 9 male and all 9 female rats had died within 24 hours of exposure. - Clinical signs:
- other: After the 4-hour exposure the rats in concentrations where mortalities occurred (224 mg/m³ and 718 mg/m³) showed signs of dyspnoea, lateral position, cyanosis, apathy and ruffled fur. These symptoms became more accentuated as test material concentration i
- Gross pathology:
- Haemorrhages in the lungs and congested organs were observed in the animals that died during the study. In those that were sacrificed after the 7 day observation period, no test material related gross organ changes were seen.
Any other information on results incl. tables
Table 1: Mortality Results
Concentration (mg/m³) |
Exposure time (hours) |
No. of Animals |
Died within |
||||||||
0 - 4 hours |
24 hours |
48 hours |
7 days |
||||||||
|
|
M |
F |
M |
F |
M |
F |
M |
F |
M |
F |
92 |
4 |
9 |
9 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
224 |
4 |
9 |
9 |
0 |
0 |
0 |
0 |
3 |
3 |
4 |
3 |
718 |
4 |
9 |
9 |
0 |
0 |
9 |
9 |
9 |
9 |
9 |
9 |
Applicant's summary and conclusion
- Interpretation of results:
- other: Category 2 in accordance with EU criteria
- Conclusions:
- Under the conditions of the study, the LC50 of the test material was found to be 250 mg/m³ (0.25 mg/L) in male and female rats.
- Executive summary:
The acute inhalation toxicity of the test material was investigated in a study which was conducted in accordance with generally accepted scientific principles.
During the study, the test material was administered to three separate groups of albino rats, each group comprised of 9 males and 9 females. The rats were exposed to the test material for a period of 4 hours, via nose-only exposure, as an aerosol mist at concentrations of 92, 224 and 718 mg/m³. The individual concentrations of the test material were gravimetrically determined.
The exposure system used in the study was that described by Sachsse et al. (1974); the test material was sprayed into the exposure chamber by means of a pressure nozzle. The liquid was injected by a motor-driven syringe at a rate of 0.9, 3 and 12 mL/hr into a stream of compressed air (2 atm.) flowing through a spray nozzle at a rate of 10 L/min. The aerosol mist thus produced was discharged into the exposure chamber.
All of the 18 rats (9 male and 9 female) that were exposed to the lowest concentration of test material, 92 mg/m³, survived. Three male and three female rats died between 24 and 48 hours after being exposed to the median test material concentration of 224 mg/m³. A further male rat died prior to the end of the 7 day observation period. At the highest concentration of test material, 718 mg/m³, all 9 male and all 9 female rats had died within 24 hours of exposure.
The rats in concentrations where mortalities occurred (224 mg/m³ and 718 mg/m³) showed signs of dyspnoea, lateral position, cyanosis, apathy and ruffled fur. These symptoms became more accentuated as test material concentration increased. The surviving animals had recovered within 4 to 5 days.
Haemorrhages in the lungs and congested organs were observed in the animals that died during the study. In those that were sacrificed after the 7 day observation period, no test material related gross organ changes were seen.
Under the conditions of the study, the LC50 of the test material was found to be 250 mg/m³ (0.25 mg/L) in male and female rats.
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.
![ECHA](/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/echa_logo.png)