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EC number: 281-161-6 | CAS number: 83877-91-2
- 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
Acute Toxicity: inhalation
Administrative data
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Data obtained from an authoritative secondary source. Read-across justification: The substance is hydrolytically unstable. When it comes in contact with water or moisture complete hydrolysis will take place with no significant reaction products other than alcohols, ethyl acetoacetate and hydrated titanium dioxide. The half-life of hydrolysis is < 10 minutes @ 25 ˚C. This rapid hydrolysis is the driving force for the toxicokinetics of target substance. Because of the rapid hydrolysis, the influence of the mode of administration through inhalation, dermal and oral is related to the most hazardous degradation products released from the target substance. In addition, because of rapid hydrolysis the dermal effects of the target substance are similar to the irritating properties of the degradation products. The identification of degradation products from the hydrolysis study conducted for the target substance verifies that there are no impurities in the mixture of particular alcohol and ethyl acetoacetate which might change the hazardous properties of the target substance compared to the properties of the pure alcohol and ethyl acetoacetate. As there is a mechanistic reasoning to the read-across, the unnecessary animal testing is avoided by using the read-across from the most hazardous degradation products (alcohols) to evaluate irritation, sensitization and the short-term and long-term toxicological effects of the target substance.
Data source
Reference
- Reference Type:
- secondary source
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2004
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- Male and females rats (10/sex/concentration) were exposed to isobutanol for 6 hours, immediately followed by a motor activity determination and a
functional observational battery (FOB). - GLP compliance:
- yes
- Remarks:
- No testing laboratory specified in the publication
Test material
- Reference substance name:
- 2-methylpropan-1-ol
- EC Number:
- 201-148-0
- EC Name:
- 2-methylpropan-1-ol
- Cas Number:
- 78-83-1
- Molecular formula:
- C4H10O
- IUPAC Name:
- 2-methylpropan-1-ol
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
Administration / exposure
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- not specified
- Duration of exposure:
- 6 h
- Concentrations:
- 0, 1500, 3000, and 6000 ppm (0, 4545, 9090, 18180 mg/m3)
- No. of animals per sex per dose:
- 10/sex/concentration
- Control animals:
- yes
- Details on study design:
- All of the rats on study were
subdivided into four FOB assessment groups and exposed (and data
collected) on different days in order to obtain timelier FOB assessments.
Body weight data was collected on Day 1 (pre-exposure), 7, and 14. During
exposure assessments were limited to a crude startle response reflex
determination for the animals visible thru the exposure chamber windows.
The stimulus startle response was initiated by sharply striking an object
against the stainless steel exterior wall of the chamber. Post-exposure motor
activity (60 minutes) and FOB tests were conducted pre-test (1-2 weeks
prior to exposure), immediately following exposure (Day 1) and seven and
fourteen days after the exposure. An additional motor activity test was
conducted on Day 2. FOB assessments were conducted approximately 10-
30 minutes after the motor activity test ended. An automated apparatus was
used to conduct motor activity tests while trained observers blind to the test
status of the animals conducted the FOB tests.
Results and discussion
Effect levels
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- 18 180 mg/m³ air
- Remarks on result:
- other: no mortality was observed at the highest concentration tested (18180 mg/m3)
- Mortality:
- no mortalities were observed
- Other findings:
- No exposure related differences were noted between the control and exposed groups. Hypoactivity and diminished response to a startle reflex was observed during exposure for the 3000 ppm (9090 mg/m3) and 6000 ppm (18180 mg/m3) exposures. Decreases in motor activity were noted post-exposure in the 6000 ppm (18180 mg/m3) group but not the 3000 ppm (9090 mg/m3) or 1500 ppm 4545 mg/m3) groups. No effect on motor activity was detected at the 7 and 14 day time points. No exposure-related effects were noted in the FOB
assessment.
Any other information on results incl. tables
Read-across justifications and data matrices are presented in IUCLID section 13.
Applicant's summary and conclusion
- Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: expert judgment
- Conclusions:
- Male and female rats exposed to atmospheric vapor levels of 0, 1500, 3000, or 6000 ppm (0, 4550, 9090, 18180 mg/m3) for six hours were evaluated in a neurobehavioral battery. No mortality was observed in any exposure groups. Thus, the LC50 value was concluded to be > 18180 mg/m3.
- Executive summary:
The exposed rats were evaluated in a neurobehavioral battery (motor activity determination and a functional observational battery) within two hours post-exposure. Hypoactivity and diminished response to a startle reflex (during the inhalation exposure) was observed during exposure for the 3000 and 6000 ppm (9090 and 18180 mg/m3) exposures. Decreases in motor activity were noted post-exposure in the 6000 ppm (18180 mg/m3 ) groups but not the 3000 or 1500 ppm (9090 or 4550 mg/m3 )groups. No effect on motor activity was detected at the 7 and 14 -day time points. No exposure-related effects were noted in the FOB assessment. Since no mortality was observed at the highest concentration level tested, the LC50 value is determined to be > 18180 mg/m3.
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