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Diss Factsheets
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EC number: 203-988-3 | CAS number: 112-59-4
- 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
Acute Toxicity: oral
Administrative data
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1985
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
- Remarks:
- Purity of the test material was not listed.
Data source
Reference
- Reference Type:
- publication
- Title:
- The comparative acute toxicity and primary irritancy of the monohexyl ethers of ethylene and diethylene glycol.
- Author:
- Ballantyne B.; Myers R. C.
- Year:
- 1 987
- Bibliographic source:
- Vet Human Tox 29:361-366
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Hilltop-Wistar albino rats, weighing between 200 and 300 g, received the test material by stomach intubation to evaluate the acute oral toxicity of the test substance.
- GLP compliance:
- no
- Test type:
- fixed dose procedure
- Limit test:
- no
Test material
- Reference substance name:
- 2-(2-hexyloxyethoxy)ethanol
- EC Number:
- 203-988-3
- EC Name:
- 2-(2-hexyloxyethoxy)ethanol
- Cas Number:
- 112-59-4
- Molecular formula:
- C10H22O3
- IUPAC Name:
- 2-[2-(hexyloxy)ethoxy]ethan-1-ol
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): diethylene glycol monohexyl ether (DGHE)
- Physical state: Colorless liquid
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- The animals were maintained on appropriate commercial diet and municipal water. Both were available adlibitum except during periods of fasting.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- Hilltop-Wistar albino rats, weighing between 200 and 300 g, received the test material by stomach intubation with a ball-end stainless steel needle.
The sample is injected through the needle by means of a syringe and doses were varied by adjusting the volume of the test material or its dilution.
The rats were fasted overnight before dosing. Five males and 5 females were included on each level. - Doses:
- Males: 1, 2, 4, 8 or 16 mL/kg
Females: 2, 4, or 8 mL/kg - No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- The animals were maintained on appropriate commercial diet and municipal water. Both were available adlibitum except during periods of fasting.
Dosage levels for the toxicity tests normally differ by a factor of 2 in a geometric series , but may differ by other constant factors if required . The maximum dosage for the peroral and percutaneous tests is 16 ml/kg. Dosages are reduced until significant signs of toxicity are not observed.
LD50's were calculated by the moving average method (Thompson, 1947) and were based on a 14-day observation period. Animal weights were recorded at 0 days ( before dose), 7 days and 14 days ( just prior to sacrifice ) . At death or sacrifice , each animal is subjected to gross pathologic evaluation. Hilltop-Wistar albino rats , weighing between 200 and 300 g, received the test material by stomach intubation with a ball-end stainless steel needle. The sample is injected through the needle by means of a syringe and doses were varied by adjusting the volume of the test material or its dilution . The rats were fasted overnight before dosing. Five males and five females were included on each level. - Statistics:
- Dosage levels for the toxicity tests normally differ by a factor of 2 in a geometric series , but might differ by other constant factors if required.
LD50's were calculated by the moving average method (Thompson, 1947) and were based on a 14-day observation period.
Results and discussion
- Preliminary study:
- No data available
Effect levelsopen allclose all
- Key result
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 4.92 mL/kg bw
- Key result
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- 3.73 mL/kg bw
- Mortality:
- Mortality rates for males treated with 4, 8 or 16 mL/kg were 2/5, 4/5 and 5/5 and for females treated with 4 or 8 ml/kg were 3/5 and 5/5. All animals treated with 1 or 2 mL/kg survived. All deaths occurred within 1 day of dosing.
- Clinical signs:
- other: Sluggishness, unsteady gait and prostrate appearance were among the signs of toxicity observed.
- Gross pathology:
- Findings at necropsy included dark red or dark pink lungs, but only for animals that died during the study.
- Other findings:
- None
Any other information on results incl. tables
The LD50 values (with 95% confidence limits) were 4.92 mL/kg (3.09 -7.84) for males and 3.73 mL/kg (3488 mg/kg/bw) (2.52 - 5.52) for females. The slope of the dose-mortality curve was higher for females (4.96) than males (3.00).
Applicant's summary and conclusion
- Interpretation of results:
- Category 5 based on GHS criteria
- Conclusions:
- The LD50 values (with 95% confidence limits) were 4.92 mL/kg (3.09 -7.84) for males and 3.73 mL/kg (3488 mg/kg/bw) (2.52 - 5.52) for females.
- Executive summary:
Fasted male and female rats (200 to 260 g) were divided into 5 groups of five animals each (males) and 3 groups of 5 animals each (females). Undiluted test material was administered by gavage to each group at the following concentrations: 1, 2, 4, 8 or 16 ml/kg (males) and 2, 4, or 8 ml/kg (females). Animals were inspected twice daily for signs of toxicity for 14 days. Body weights were taken before dosing, and 7 and 4 days after dosing. Animals that died and all animals surviving the 14 day period were necropsied. LD50 values and their slopes were calculated by the moving average method. Mortality rates for males treated with 4, 8 or 16 ml/kg were 2/5, 4/5 and 5/5 and for females treated with 4 or 8 ml/kg were 3/5 and 5/5. All animals treated with 1 or 2 ml/kg survived. All deaths occurred within 1 day of dosing. Signs of toxicity included sluggishness, unsteady gait and prostrated appearance. Animals that died had red or dark pink lungs. All survivors gained weight over the 14 day period and had normal pathology. The LD50 values (with 95% confidence limits) were 4.92 ml/kg (3.09 -7.84) for males and 3.73 ml/kg (3488 mg/kg/bw) (2.52 - 5.52) for females. The slope of the dose-mortality curve was higher for females (4.96) than males (3.00).
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