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EC number: 203-860-7 | CAS number: 111-34-2
- 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
Studies on acute toxicity of BVE are available:
The oral LD50 in male Wistar rats was 10300 mg/kg bw.
The LC50 (4h) in rats is >33.3 mg/L.
The dermal LD50 in rabbits is 3300 mg/kg bw.
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
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline study with acceptable restrictions. Restriction: purity of TS not reported; non-fasted animals; no data about vehicle; no data about clinical signs, necropsy or body weight.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Deviations:
- no
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Male Carworth-Wistar rats were used, 90 to 120 g in weight. Animals were kept on complete diet.
- Route of administration:
- oral: gavage
- Vehicle:
- not specified
- Details on oral exposure:
- Rats not fasted before dosing; application volume 1-10 mL
- Doses:
- Dose levels were arranged in a logarithmic series differing by a factor of 2 (no further details).
- No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- Post exposure observation period 14 days
- Statistics:
- LD50-values were estimated by the method of Thompson using the tables of Weil, based on mortalities.
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 10 300 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: limits of +-1.96 standard deviations (calculated according to Thompson): 8400-12630 mg/kg bw
- Mortality:
- no further details
- Clinical signs:
- other: no data
- Gross pathology:
- no data
- Other findings:
- no data
- Conclusions:
- The LD50 in male Wistar rats was 10300 mg/kg bw; the post exposure observation period was 14 days. The Limit dose according to OECD TG401 is 5000 mg/kg bw.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 10 300 mg/kg bw
- Quality of whole database:
- Comparable to guideline study with acceptable restrictions.
Restriction: purity of TS not reported; non-fasted animals; no data about vehicle; no data about clinical signs, necropsy or body weight
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to the Limit test described in OECD TG403. Restriction: purity of TS not reported; concentration analytically not verified, no data on clinical signs or necropsy.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Deviations:
- no
- Principles of method if other than guideline:
- Toxic effects in rats after inhalation exposure for 4 h
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Male and female Carworth-Wistar rats were used, 90 to 120 g in weight. Animals were kept on complete diet.
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- other: air
- Details on inhalation exposure:
- Metered atmospheres were generated by using pumps which delivered known amounts of TS to a stream of air. Concentrations are nominal, but not analytically verified; no further details
- Analytical verification of test atmosphere concentrations:
- no
- Duration of exposure:
- 4 h
- Concentrations:
- 8000 or 16000 ppm corresponding to 33.3 or 66.6 mg/L
- No. of animals per sex per dose:
- 6 rats
- Details on study design:
- Groups of 6 male or female rats were used. Mortalities noted during the 14-day observation period. Effect levels related to male and female rats combined.
- Sex:
- male/female
- Dose descriptor:
- LC0
- Effect level:
- 8 000 ppm
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- other: (33.3 mg/L) 0 out of 6 rats died
- Sex:
- male/female
- Dose descriptor:
- LC100
- Effect level:
- 16 000 ppm
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- other: (66.6 mg/L) 6 out of 6 rats died
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 33.3 mg/L air
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- other: Recommended limit concentration according to OECD TG403 is 5 mg/L
- Mortality:
- no further details
- Clinical signs:
- other: no data
- Body weight:
- no data
- Gross pathology:
- no data
- Conclusions:
- No mortality was noted (0/6 animals died) in male and female Wistar rats following exposure to 8000 ppm (=33.3 mg/L) for 4 hours and a post exposure observation period of 14 days. However, a dose level of 16000 ppm (66.6 mg/L) for 4 h killed all 6 rats.
The LC50 (4) in rats is >33.3 mg/L (Limit dose according to OECD TG403 ist 5 mg/L).
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LC50
- Value:
- 33.3
- Quality of whole database:
- Comparable to the Limit test described in OECD TG403. Restriction: purity of TS not reported; concentration analytically not verified, no data on clinical signs or necropsy.
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline study with acceptable restrictions. Restriction: purity of test substance not stated; no data on clinical signs; no necropsy; only males.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- Deviations:
- no
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rabbit
- Strain:
- New Zealand White
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Male albino New Zealand rabbits weighing 2.5 to 3.5 kg were used.
No further details. - Type of coverage:
- occlusive
- Vehicle:
- unchanged (no vehicle)
- Details on dermal exposure:
- Groups of 4 animals were used. Dosages were placed on the shaved rabbit skin under occlusive dressing (contact ca. 1/10 of body surface).
- Duration of exposure:
- 24 h
- Doses:
- no details given
- No. of animals per sex per dose:
- 4
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: no data
- Necropsy of survivors performed: no
- no data about clinical signs & body weight - Statistics:
- LD50-values were estimated by the method of Thompson using the tables of Weil, based on mortalities noted during the 14-day observation period.
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 3 300 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: original value 4.24 mL/kg bw and limits of +-1.96 standard deviations (calculated according to Thompson): 3.02-5.95 mL/kg bw (2350-4630 mg/kg bw)
- Mortality:
- No further data available.
- Clinical signs:
- other: no data
- Gross pathology:
- no data
- Conclusions:
- In male New Zealand White rabbits the acute dermal toxicity was determined after an exposure period of 24 h (occlusive) and a post exposure period of 14 days. The LD50 is 4.24 mL/kg bw, i.e. 3300 mg/kg bw. The limit dose recommended in OECD TG402 is 2000 mg/kg bw.
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 3 300 mg/kg bw
- Quality of whole database:
- Comparable to guideline study with acceptable restrictions.
Restriction: purity of test substance not stated; no data on clinical signs; no necropsy; only males.
Additional information
Oral
The LD50 of BVE in male Wistar rats was 10300 mg/kg bw; the post exposure observation period was 14 days (Smyth et al., 1954). The limit dose according to OECD TG401 is 5000 mg/kg bw.
Inhalation
No mortality was noted (0/6 animals died) in male and female Wistar rats following exposure to 8000 ppm BVE (=33.3 mg/L) for 4 hours and a post exposure observation period of 14 days. However, a dose level of 16000 ppm (66.6 mg/L) for 4 h killed all 6 rats (Smyth et al., 1954). The LC50 (4) in rats is >33.3 mg/L (Limit dose according to OECD TG403 ist 5 mg/L).
In the inhalation hazard test (same publication) no mortality occurred in 6 male rats within 14 days after exposure for 5 min to saturated vapour.
Dermal
In male New Zealand White rabbits the acute dermal toxicity of BVE was determined after an exposure period of 24 h (occlusive) and a post exposure period of 14 days. The LD50 is 4.24 mL/kg bw, i.e. 3300 mg/kg bw (Smith et al., 1954). The limit dose recommended in OECD TG402 is 2000 mg/kg bw.
Justification for selection of acute toxicity – oral endpoint
Comparable to guideline study with acceptable restrictions.
Justification for selection of acute toxicity – inhalation endpoint
Comparable to guideline study with acceptable restrictions.
Justification for selection of acute toxicity – dermal endpoint
Comparable to guideline study with acceptable restrictions.
Justification for classification or non-classification
Dangerous Substance Directive (67/548/EEC): the available studies are considered reliable and suitable for classification purposes under 67/548/EEC. As a result the substance is not considered to be classified under Directive 67/548/EEC, as amended for the 31st time in Directive 2009/2/EG.
Classification, Labelling, and Packaging Regulation (EC) No 1272/2008: the available experimental test data are reliable and suitable for classification purposes under Regulation (EC) No 1272/2008. As a result the substance is not considered to be classified under Regulation (EC) No 1272/2008, as amended for the sixth time in Regulation No 605/2014.
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.
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