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EC number: 201-289-8 | CAS number: 80-54-6
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Jan 11th, - March 19th, 2000
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 000
- Report date:
- 2000
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Principles of method if other than guideline:
- The micronucleus assay was conducted using established and validated procedures (Heddle, 1973; Hayashi et al., 1994; Mavournin et al ., 1990).
- Heddle, J.A. 1973. A rapid in vivo test for chromosomal damage. Mutation Res. 18:187-190
- Hayashi, M., et al., 1994. In vivo rodent erythrocyte micronucleus assay. Mutation Res. 312: 293-304
- Mavournin, K .H., et al., 1990. The in vivo micronucleus assay in mammalian bone marrow and peripheral blood. A report of the U.S. Environmental Protection Agency Gene-Tox Program. Mutation Res. 239: 29-80. - GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 2-(4-tert-butylbenzyl)propionaldehyde
- EC Number:
- 201-289-8
- EC Name:
- 2-(4-tert-butylbenzyl)propionaldehyde
- Cas Number:
- 80-54-6
- Molecular formula:
- C14H20O
- IUPAC Name:
- 3-(4-tert-butylphenyl)-2-methylpropanal
- Details on test material:
- - Name of test material (as cited in study report): p-Butyl-alpha-methylhydrocinnamic aldehyde
- Analytical purity: not reported
- Physical state and appearance: liquid, colourless and clear
- Lot No.: 9000349505
- Storage: in the dark, at room temperature
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- ICR
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- - Source: Sprague Dawley, Inc., Frederick, MD
- Age at study initiation: 6-8 weeks
- Body weight range at study initiation: MN Study; 29.7 - 33.6g (male), 25.7 - 30.7 g (female), Toxicity Study: 25.0 - 28.4 g (male), 25.7 - 28.6 g (female)
- Housing: 5/sex/cage
- Diet: ad libitum (Harlan TEKLAD certified Rodent 7012C). There were no relevant contaminants in the feed
- Water: ad libitum (Washington Suburban Sanitary Commission, Potomac Plant). Met USEPA drinking water standards
- Acclimation: at least 5 days (animals were healthy at begin of study)
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20.6 - 23.9
- Humidity (%): 30-70
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle: corn oil
- Rationale for choice: Based on information provided by the Sponsor and because the vehicle was compatible with the test system animals.
- Application volume: 2 ml/100 g bw - Duration of treatment / exposure:
- 24 h and 48 h
- Frequency of treatment:
- single administration
Doses / concentrationsopen allclose all
- Dose / conc.:
- 150 mg/kg bw (total dose)
- Dose / conc.:
- 300 mg/kg bw (total dose)
- Dose / conc.:
- 600 mg/kg bw (total dose)
- No. of animals per sex per dose:
- See table 1 below
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- - Cyclophosphamide (CP)
- Vehicle: sterile water
- Concentration tested: 2.5 mg/ml
- Route of application: ip
Examinations
- Tissues and cell types examined:
- Bone marrow cells were examined for micronucleated polychromatic erythrocytes
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
- Based on the findings of a preliminary toxicity assay, the highest dose in MN assay was set at approximately 75% of the LD50 of 800 mg/kg bw for male and females.
TREATMENT AND SAMPLING TIMES:
- Administration volume: 2 ml/100g bw
- Sampling time: 24 h (all doses), 48 h (control and highest dose)
DETAILS OF SLIDE PREPARATION:
- Flushing of femur: with fetal calf serum
- Centrifugation of bone marrow cells: 100 x g, 5 min, in fetal calf serum
- Fixation agent: methanol
- Staining agent: May-Gruenwald-Giemsa
METHOD OF ANALYSIS:
- Using oil immersion, 2000 polychromatic erythrocytes were scored for micronuclei
- The proportion of polychromatic erythrocytes to total erythrocytes was also recorded per 1000 erythrocytes
- Micronuclei defined as; round, darkly staining nuclear fragments, having a sharp contour with diameters usually from 1/20 to 1/5 of the erythrocyte - Evaluation criteria:
- CRITERIA FOR POSITIVE TEST
The test article was considered to induce a positive response if a dose-responsive increase in micronucleated polychromatic erythrocytes is observed and one or more doses were statistically elevated relative to the vehicle control (p<=0.05, Kastenbaum-Bowman Tables) at any sampling time. If a single treatment group is significantly elevated at one sacrifice time with no evidence of a dose-response, the assay is considered a suspect or unconfirmed positive and a repeat experiment is needed. The test article is judged negative if no statistically significant increase in micronucleated polychromatic erythrocytes above the concurrent vehicle control values are observed at any sampling time.
CRITERIA FOR VALID TEST
The mean incidence of micronucleated polychromatic erythrocytes must not exceed 5/1000 polychromatic erythrocytes (0.5%) in the vehicle control. The incidence of micronucleated polychromatic erythrocytes in the positive control group must be significantly increased relative to the vehicle control group (p<= 0.05, Kastenbaum-Bowman Tables). - Statistics:
- Statistical significance was determined using the Kastenbaum-Bowman tables which are based on the binomial distribution (Kastenbaum and Bowman, 1970).
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Number of animals: 5 males/5 females
- Dose range: 300, 500, 700, or 1000 mg/kg bw/d
- Clinical signs of toxicity in test animals: lethargy and piloerection in male and female mice at 300, 500, 700 and 1000 mg/kg. Prostration and irregular breathing were observed in males and females at 700 and 1000 mg/kg, crusty eyes in males at 700 and in males and females at 1000 mg/kg and convulsions in males and females at 1000 mg/kg
- Mortality: 5/5 male mice and 5/5 female mice at 1000 mg/kg, occured within 3 days
- Solubility: The test article was soluble in corn oil at 50 mg/ml, the maximum concentration tested in the study.
RESULTS OF DEFINITIVE STUDY
- Mortality: no mortality was noted at any dose
- Clinical signs: see table 2 and 3 of result
- Genotoxicity: Systemic bioavailability was clearly demonstrated by the PCE/total erythrocyte ratio in the top dose group at 24 hours sacrifice interval (-15% or -30% of control [male; female]).
A statistically significant increase of micronucleated cells (MN) in males after 48 hours and a non-significant increase in females after 24 hours in the highest dose group (600 mg/kg bw/d) was found, the only dose showing signs of systemic toxicity in each tested animal. The statistically significant increase of micronucleated cells in males after 48 hours is not considered biologically relevant, since only one animal of this dose group had 3 MN/2000 polychromatic erythrocytes (PCE) which is well within the historical range of solvent control (0-7 MN/1000 PCE). All other animals had no more than 2 MN/2000 PCE (2,1,2 and 1 MN/2000 PCE, respectively). The statistical significance stems from the low individual MN values of the respective study control animals (1,0,0,1 and 0 MN/2000 PCE).
Furthermore, the small increase observed in the female high dose group 24 hours after treatment (mean 1.2 MN /1000 PCE), are well within the HC range of 0-7 MN/1000 PCE. Single animal data (control animals: 1,1,1,1,1 MN per 2000 PCE versus treated animals: 1,2,1,4,4 MN per 2000 PCE), show only 2 treated females with slightly increased MN numbers. The treatment group mean value reached no statistical significance. Thus, all single values obtained were within the inter-animal variability of the mouse strain used in this study type. In line with the above, no statistically significant increase and no dose-responsive increase were observed in any other test article treated group regardless of dose level, sex or bone marrow collection time. Furthermore, no significant or dose-related increase was observed in any other dose group regardless of sex or bone marrow collection time.
The sensitivity of the test system was shown since the positive control substance caused chromosomal aberrations.
Any other information on results incl. tables
Table 2: Summary of results of the MN assay after 24 h
Treatment (mg/kg bw) |
Sex |
Clinical signs |
PCE/Total Erythrocytes Mean ± SD |
Micronucleuted PCEs/ PCEs scored |
|
0 |
M |
- |
0.48 ± 0.08 |
3/10000 |
|
F |
- |
0.50 ± 0.04 |
5/10000 |
||
150 |
M |
- |
0.47 ± 0.07 |
5/10000 |
|
F |
- |
0.48 ± 0.06 |
4/10000 |
||
300 |
M |
Lethargy and Piloerection |
3/5 |
0.50 ± 0.05 |
4/10000 |
F |
4/5 |
0.46 ± 0.06 |
2/10000 |
||
600 |
M |
Lethargy and Piloerection (15/15) Prostration and irregular breathing (2/15) |
0.40 ± 0.08 |
6/10000 |
|
F |
0.35 ± 0.04 |
12/10000 |
|||
CP (50 mg/kg bw) |
M |
- |
0.44 ± 0.06 |
174*/10000 |
|
F |
- |
0.47 ± 0.13 |
200*/10000 |
* significantly increased compared to control p<= 0.05
Table 3: Summary of results of the MN assay after 48 h
Treatment (mg/kg bw) |
Sex |
PCE/Total Erythrocytes Mean ± SD |
Micronucleuted PCEs / PCEs scored |
0 |
M |
0.55 ± 0.04 |
2/10000 |
F |
0.57 ± 0.05 |
2/10000 |
|
600 |
M |
0.50 ± 0.05 |
9sig/10000 |
F |
0.52 ± 0.06 |
5/10000 |
sig:significantly increased compared to control p<= 0.05. This response is not considered biologically relevant, since only one animal had 3 MNPCE which is within the historical range of solvent control (0-7 MN/2000 PCE/animal). All other animals had no more than 2 MNPCE.
Applicant's summary and conclusion
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