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EC number: 224-030-0 | CAS number: 4170-30-3
- 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:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Published Data
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 967
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Deviations:
- yes
- Remarks:
- analytical
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- no
Test material
- Reference substance name:
- Crotonaldehyde
- EC Number:
- 224-030-0
- EC Name:
- Crotonaldehyde
- Cas Number:
- 4170-30-3
- Molecular formula:
- C4H6O
- IUPAC Name:
- but-2-enal
- Details on test material:
- 90% purity
Eastman Organic Chemical P1878
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- 120-150 g
Administration / exposure
- Route of administration:
- inhalation
- Type of inhalation exposure:
- whole body
- Vehicle:
- other: unchanged (no vehicle)
- Details on inhalation exposure:
- None
- Analytical verification of test atmosphere concentrations:
- yes
- Remarks:
- colorimetric reaction of aldehydes with modified schiff-elvove reagent
- Duration of exposure:
- 4 h
- Concentrations:
- 50,60,70,100, 120, 240 ppm (analytical)
120, 110, 135, 175, 200, 390 ppm (nominal) - No. of animals per sex per dose:
- 10 animals per dose at 15, 30, 60, and 240 min exposures
- Control animals:
- yes
- Details on study design:
- animals were exposed to crotonaldhyde vapor for a period of 5 min to 4 hours at concentrations ranging rom 50 to 240 ppm.
Crotonaldehyde vapors were generated by bubbling dry nitrogen gas through the liquid crotonaldehyde. The saturated vapors were mixed with the appropriate amount of air to achieve the desired nominal concentration and passed into either a 20 liter glass chamber operating under positive pressure or (in the case of lower concentrations) a 1700 liter wooden chamber operating under negative pressure. Concentrations were varied by altering the nitrogen flow through the dispersion bubbler in order to volatilize varying amounts of crotonaldehyde per unit time or by varying the airflow through the chambers so as to change the dilution factor. In no case was the volume of added nitrogen more than 15% of the total flow, thereby maintaining an oxygen content of 17.8% or greater in the exposure vapor mixture. Dilutions of oxygen to this lower limit were made only in a very few exposures of five minutes duration, so the temporary decrease in oxygen content was not expected to have a physiological effect on the animals. After allowing sufficient time for the chambers to equilibrate, the animals were quickly introduced for the desired exposure period.
The method used for the studies reported herein is based on the colorimetric reaction of aldehydes with modified Schiff-Elvove reagent. Samples (two - five, depending on duration of exposure) of the chambers wre collected at intervals in aldehyde-free 1% methanol water. after dilution to an appropriate volume, Schiff Elvove reagent was added; the color was developed to a maximum for 60 to 75 minutes and read at a spectral wavelength of 888mu. it was found most desirable to run several standards with each batch of samples. It was also found that the samples could be kept stoppered for later analysis with no loss in anlytically determined quantities for up to 48 hours after sampling. Sample taken within a given exposure showed good agreement with a variability of no greater tha 5%; that is, for an average of 500ppm , samples would lie withint 475-525 ppm. On the other hand, analytical recoveries as a percentage of nominal concentration only averaged 42% and where quite variable 61% of theoretical. it is thought that absorption on chamber walls was largely responsible, although oxidation and polymerization are possible causes. No fixed pattern was observed that could be realted to concentration, airflow, chamber surface, etc. - Statistics:
- The LC50 data were visually estimated from log-probit plots of the data at the indicated postexposure observation periods.
Results and discussion
- Preliminary study:
- not applicable
Effect levelsopen allclose all
- Sex:
- male
- Dose descriptor:
- LC50
- Effect level:
- 120 ppm
- Exp. duration:
- 4 h
- Sex:
- male
- Dose descriptor:
- LC50
- Effect level:
- 600 ppm
- Exp. duration:
- 1 h
- Sex:
- male
- Dose descriptor:
- LC50
- Effect level:
- 800 ppm
- Exp. duration:
- 30 min
- Sex:
- male
- Dose descriptor:
- LC50
- Effect level:
- 1 300 ppm
- Exp. duration:
- 15 min
- Sex:
- male
- Dose descriptor:
- LC50
- Effect level:
- 1 820 ppm
- Exp. duration:
- 10 min
- Mortality:
- see table in remarks
- Clinical signs:
- other: All animals exposed developed some signs of respiratory distress. Gasping was particularly prominent and was usually associated with a lower respiratory rate. Animals exposure to concentrations in excess of 1000 ppm also showed evidence of excitatory s
- Body weight:
- Weight losses in rats were quite pronounced following exposure, with survivors losing 10-25% of body weight by 24 hours post exposure, whereas nonexposed control animals gained on average 5% per day. The degree of weight loss was roughly proportional to the severity of the exposure as indicated by mortality. Recovery to pre-exposure weights required from 3 days to 2 weeks, again depending on the severity of the exposure. In several instances, the maximum weight loss did not occur until the second or third day after exposure. It was our experience that no animal died the was recovering toward its pre-exposure weight.
- Gross pathology:
- A few animals subjected to autopsy showed pulmonary congestion, but other organs appeared grossly normal.
- Other findings:
- none reported
Any other information on results incl. tables
Exposure Time (min) |
Analytical average (ppm) |
Time after exposure (days) |
|||||
1 |
2 |
3 |
4 |
7 |
14 |
||
0 |
0 0 |
0/5 0/6 |
0/5 0/6 |
0/5 0/6 |
0/5 0/6 |
0/5 0/6 |
0/5 0/6 |
5 |
1920 2420 2680 3180 4160 4640 |
0/5 0/5 0/5 3/5 4/5 4/5 |
0/5 0/5 1/5 3/5 4/5 5/5 |
0/5 0/5 1/5 3/5 4/5 5/5 |
0/5 0/5 1/5 3/5 4/5 5/5 |
0/5 0/5 1/5 3/5 4/5 5/5 |
0/5 1/5 1/5 3/5 4/5 5/5 |
10 |
800 1110 1380 1820 2050 |
0/12 0/12 3/12 6/12 8/12 |
0/12 0/12 4/12 7/12 8/12 |
0/12 0/12 4/12 7/12 9/12 |
0/12 0/12 4/12 7/12 9/12 |
1/12 1/12 4/12 7/12 9/12 |
1/12 4/12 6/12 7/12 9/12 |
15 |
550 680 750 850 980 1090 1290 |
0/10 0/10 2/10 2/10 3/10 3/10 5/10 |
0/10 2/10 4/10 3/10 6/10 5/10 7/10 |
0/10 2/10 4/10 5/10 6/10 7/10 9/10 |
0/10 2/10 4/10 5/10 6/10 7/10 10/10 |
0/10 2/10 4/10 5/10 7/10 8/10 10/10 |
0/10 2/10 5/10 7/10 7/10 8/10 10/10 |
30 |
370 420 530 675 800 890 |
0/10 1/10 2/10 4/10 5/10 6/10 |
0/10 2/10 4/10 6/10 7/10 9/10 |
0/10 2/10 4/10 6/10 7/10 9/10 |
0/10 2/10 4/10 6/10 7/10 9/10 |
0/10 2/10 4/10 6/10 7/10 9/10 |
0/10 2/10 4/10 6/10 8/10 9/10 |
60 |
1040 1090 910 1150 1450 |
1/10 3/10 3/10 4/10 8/10 |
1/10 4/10 5/10 6/10 9/10 |
1/10 4/10 5/10 7/10 10/10 |
2/10 5/10 6/10 7/10 10/10 |
3/10 5/10 6/10 7/10 10/10 |
4/10 6/10 7/10 7/10 10/10 |
240 |
50 60 70 100 120 200 |
0/10 0/10 0/10 4/10 5/10 6/10 |
0/10 0/10 1/10 5/10 5/10 6/10 |
1/10 0/10 1/10 5/10 6/10 7/10 |
1/10 2/10 3/10 5/10 8/10 9/10 |
1/10 2/10 3/10 5/10 8/10 9/10 |
1/10 2/10 4/10 6/10 8/10 9/10 |
Applicant's summary and conclusion
- Interpretation of results:
- toxic
- Remarks:
- Migrated information Criteria used for interpretation of results: US CPSC / US OSHA
- Conclusions:
- Toxic by inhalation based on 4 hour LC 50 in rats
- Executive summary:
This study determined the LC50 values of crotonaldehyde vapor in Wistar rats. At exposure times of 15, 30, 60 and 240 minutes, 10 male animals per dose were exposed whole body in a chamber. The animals were observed for 14 days post exposure. LC50 value for for the 4 hour exposure was 120 ppm (336 mg/m3), nevertheless, a threshold level value ceiling of has been established at 0.3 ppm (0.86 mg/m3) to minimize the potential for rapid irritation to the respiratory tract and eyes.
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