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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 205-575-3 | CAS number: 142-96-1
- 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
There are no studies according to current guidelines available. But there are non-guideline studies on hand, which are adequately documented and considered to be of sufficient quality to allow an evaluation of this endpoint.
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:
- 1954
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well performed study, study performance before implementation of GLP, purity of test item not reported.
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Principles of method if other than guideline:
- not applicable
- GLP compliance:
- no
- Test type:
- standard acute method
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: raised at Mellon Institute of Industrial Research
- Age at study initiation: young adults
- Weight at study initiation: 90-120 grams - Route of administration:
- oral: gavage
- Vehicle:
- not specified
- Details on oral exposure:
- Single exposure
- Doses:
- other
- No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- The tested chemicals were diluted with water, corn oil, or a 1 % solution of sodium 3,9-diethyl-6-tridecanol sulfate (Tergitol Penetrant 7) when
necessary to bring the volume given to one rat to between 1 and 10 ml. However, it is unknown which (if any) solvent and at which concentration was used in the case of dibutyl ether. - Statistics:
- The most probable LD50 value and its fiducial range were estimated by the method of Thompson (1947) using the tables of Weil (1952).
- Preliminary study:
- not applicable
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 7 400 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- > 6 410 - < 8 530
- Mortality:
- no information available
- Clinical signs:
- other: no information available
- Gross pathology:
- no information available
- Other findings:
- no information available
- Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- Under the conditions of the study, the acute oral LD50 of dibutyl ether is 7400 mg/kg body weight with 95% CL ranging between 6410 - 8530 mg/kg body weight and will not be classified.
- Executive summary:
In this study, single dose oral toxicity for rats was estimated by intubation of dosages in a logarithmic series to groups of five male Carworth-Wistar rats (90 to 120 g), raised at the Mellon Institute of Industrial Research, University of Pittsburgh, USA. The tested chemicals were diluted with water, corn oil, or a 1 % solution of sodium 3,9-diethyl-6-tridecanol sulfate (Tergitol Penetrant 7) when necessary to bring the volume given to one rat to between 1 and 10 ml. However, it is unknown which (if any) solvent and at which concentration was used in the case of dibutyl ether. Fourteen days after dosing, mortality was considered complete. The most probable LD50 value and its fiducial range were estimated by the method of Thompson (1947) using the tables of Weil (1952). Clinical signs were not reported. Under the conditions of the study, the acute oral LD50 of dibutyl ether is 7400 mg/kg body weight with 95% CL ranging between 6410 - 8530 mg/kg body weight and will not be classified.
Reference
None
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 7 400 mg/kg bw
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:
- 1954
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well performed study, study performance before implementation of GLP, purity of test item not reported
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Principles of method if other than guideline:
- not applicable
- 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:
- TEST ANIMALS
- Source: raised at Mellon Institute of Industrial Research
- Age at study initiation: young adults
- Weight at study initiation: 90-120 grams - Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- air
- Details on inhalation exposure:
- The stream was prepared by various styles of proportioning pumps. Nominal concentrations were recorded, not confirmed by analytical methods. Exposures were four hours long. Concentrations were in an essentially logarithmic series with a factor of two.
- Analytical verification of test atmosphere concentrations:
- no
- Duration of exposure:
- 4 h
- Concentrations:
- other
- No. of animals per sex per dose:
- 6
- Control animals:
- no
- Details on study design:
- Groups of six male Carworth-Wistar rats (90 to 120 g), raised at the Mellon Institute of Industrial Research, University of Pittsburgh, USA, were exposed to a flowing stream of known vapor concentrations of dibutyl ether. The stream was prepared by various styles of proportioning pumps. Nominal concentrations were recorded, not confirmed by analytical methods. Exposures were four hours long. Concentrations were in an essentially logarithmic series with a factor of two. The concentration yielding fractional mortality among six rats within 14 days was recorded. Clinical signs were not reported.
- Statistics:
- no information available
- Preliminary study:
- not applicable
- Sex:
- male
- Dose descriptor:
- other: approximate LC50
- Effect level:
- ca. 21 600 mg/m³ air (nominal)
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- other: approximately 4000 ppm
- Mortality:
- The 4-hour exposure to 4000 ppm dibutyl ether killed 2/6 rats within 14 days.
- Clinical signs:
- other: no information available
- Body weight:
- no information available
- Gross pathology:
- no information available
- Other findings:
- no information available
- Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The 4-hour exposure to 4000 ppm dibutyl ether killed 2/6 rats within 14 days. This substance is not classified for Acute toxicity
- Executive summary:
In this study, groups of six male Carworth-Wistar rats (90 -120 grams) were exposed to a flowing stream of known vapour concentrations of dibutyl ether for 4 hours. Under the conditions of the study, the 4-hour exposure to 4000 ppm dibutyl ether killed 2/6 rats within 14 days and this substance is not classified for Acute toxicity.
Reference
4000 ppm are at 25 °C and 1013 hPa equal to 21600 mg/m³.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LC50
- Value:
- 21 600 mg/m³ air
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1954
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well performed study, study performance before , implementation of GLP, purity of test item not reported.
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- Principles of method if other than guideline:
- Study conducted prior to guidelines but study conduct comparable to current OECD TG 402
- 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:
- TEST ANIMALS
- Weight at study initiation: 2.5 -3.5 kg - Type of coverage:
- occlusive
- Vehicle:
- other: no vehicle used
- Details on dermal exposure:
- The fur was closely clipped over the entire trunk, and the doses, retained beneath an impervious plastic film, the exposure area corresponded to about 1/10 of the body surface. After 24 hours of contact the film was removed.
- Duration of exposure:
- 24 hours
- Doses:
- no information available
- No. of animals per sex per dose:
- 4
- Control animals:
- no
- Details on study design:
- The acute dermal toxicity of dibutyl ether for rabbits was estimated by the technique of Draize et al. (1944), using groups of four male New Zealand giant albino rabbits weighing 2.5 to 3.5 kg. The fur was closely clipped over the entire trunk, and the doses, retained beneath an impervious plastic film, the exposed area corresponding to about 1/10 of the body surface. After 24 hours of contact the film was removed. Animals were observed for mortality fourteen days after dosing. Clinica;l signs were not reported.
- Statistics:
- The most probable LD50 value and its fiducial range were estimated by the method of Thompson (1947) using the tables of Weil (1952)
- Preliminary study:
- not applicable
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 10.08 mL/kg bw
- Based on:
- test mat.
- 95% CL:
- 4.41 - 23.04
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 7 741 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- 3 387 - 17 695
- Mortality:
- no information available
- Clinical signs:
- other: no information available
- Gross pathology:
- no information available
- Other findings:
- no information available
- Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- Under the conditions of the study, the LD50 of dibutyl ether was 10.8 ml/kg; which is equal to 7741 (3387 - 17695) mg/kg body weight to rabbits, therefore this substance is not classified.
- Executive summary:
In this study, the acute dermal toxicity of dibutyl ether for rabbits was estimated by the technique of Draize et al. (1944), using groups of four male New Zealand giant albino rabbits weighing 2.5 to 3.5 kg. The fur was closely clipped over the entire trunk, and the doses, retained beneath an impervious plastic film, the exposed area corresponding to about 1/10 of the body surface. After 24 hours of contact the film was removed. Animals were observed for mortality for fourteen days after dosing. The most probable LD50 value and its fiducial range were estimated by the method of Thompson (1947) using the tables of Weil (1952). Clinical signs were not reported.
Under the conditions of the study, the LD50 of dibutyl ether was 10.8 ml/kg; which is equal to 7741 (3387 - 17695) mg/kg body weight to rabbits, therefore this substance is not classified.
Reference
Original values given by the authors in ml/kg bw: LD50 (95 % C.I.) 10.08 (4.41 - 23.04) ml/kg bw, which is equal to 7741 (3387 - 17695) mg/kg bw (density of dibutyl ether: 0.768 g/cm³).
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 7 741 mg/kg bw
Additional information
Inhalation
The 4-hour exposure to 21 600 mg dibutyl ether/m³ (4000 ppm) killed 2/6 rats within 14 days. This approximate 4-hour LC50 for dibutyl ether was determined in groups of six male Wistar rats. The rats were exposed to a flowing stream of dibutyl ether. Concentrations tested were in an essentially logarithmic series with a factor of two. Nominal concentrations not confirmed by analytical methods were tested and the concentration yielding fractional mortality within 14 days was published. Clinical signs were not reported (Smyth et al., 1954). In an inhalation hazard test, groups of six male Wistar rats were exposed between 30 minutes and 8 hours to highly enriched/saturated dibutyl ether vapor which was generated at room temperature. 30 Minutes was the longest exposure period which allowed all rats to survive 14 days. Clinical signs, as well as the exposure period that had killed half of the rats within 14 days, the concentration of dibutyl ether, and information as to whether the deaths were attributable to dibutyl ether or to asphyxia were not reported (Smyth et al., 1954). A single 6-hour exposure to 10 000 mg/m³ in a 7-day range finding study induced ataxia, piloerection and blepharospasm in male Wistar rats, but the chemical was apparently not narcotic. Because of these clear signs of toxicity immediately after the first exposure to 10 000 mg/m³, the top concentration level for male rats for the remainder of the 7-day range finding study was then reduced to 6500 mg/m³. The top concentration level for females, whose exposure started as scheduled one day later, was 6500 mg/m³ during the whole 7-day range-finding study. As clinical signs at 6500 mg/m³, only slight labored breathing after the first exposure in male and female Wistar rats (exposure day two for males and exposure day 1 for females), and, in females only, blepharospasm and sluggishness after the second and third exposures occurred (TNO, 2005).
Dermal
The dermal LD50value for dibutyl ether in male albinorabbits after a 14-day observation period was 7741 mg/kg bw (10.08 ml/kg bw). Clinical signs were not reported (Smyth et al., 1954).
Oral
An oral LD50-value of 7400 mg/kg bw was determined in male Wistar rats. Clinical signs were not reported (Smyth et al., 1954).
Studies in Humans
Inhalation
Volunteers were exposed in a gas cabinet to the substance for a period of 15 minutes. At 300 ppm (corresponding to 1599 mg/m³) the odor was not noticeable to the majority of subjects (Silverman, Schulte, and First, 1946).
Justification for classification or non-classification
Dibutyl ether is of low acute toxicity after inhalation (approximate 4-hour LC50rat: 21 600 mg/m³ (4000 ppm)), dermal (LD50rabbit: 7741 mg/kg bw (10.08 ml/kg bw)) and oral exposure (oral LD50rat: 7400 mg/kg bw). Dibutyl ether has no pronounced narcotic potential. The LD50 values are all high indicating a lack of acute toxicity. Therefore, the substance does not need to be classified and labelled for acute toxicity, according to the Regulation 1271/2008 and the Directive 67/548/EEC.
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.