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EC number: 222-492-8 | CAS number: 3495-36-1
- 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
Key value for chemical safety assessment
Skin sensitisation
Link to relevant study records
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From October 13, 2008 to October 28, 2008
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- GLP compliance:
- yes
- Type of study:
- mouse local lymph node assay (LLNA)
- Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Harlan UK Limited, Bicester, Oxon, UK
- Age at study initiation: 8-12 week
- Weight at study initiation: 15-23 g
- Housing: Individually housed in suspended solid-floor polypropylene cages furnished with softwood woodflakes
- Diet (e.g. ad libitum): 2014 Teklad Global Rodent diet supplied by Harlan Teklad, Blackthorn, Bicester, Oxon, UK
- Water (e.g. ad libitum): Tap water, ad libitum
- Acclimation period: 5 d
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-25 °C
- Humidity (%): 30-70 %
- Air changes (per hr): 15 air changes per h
- Photoperiod (hrs dark / hrs light): 12 h light/12 h dark cycle - Vehicle:
- other: Ethanol/distilled water (7:3)
- Concentration:
- 50, 25 and 10 % w/w in ethanol/distilled water (7:3)
- No. of animals per dose:
- Four
- Details on study design:
- RANGE FINDING TESTS:
- Compound solubility: Test substance solution was prepared in ethanol/distilled water (7:3)
- Irritation: No
- Lymph node proliferation response: No
Preliminary Screening Test: Test substance (25 µL) at concentration of 50 % w/w in ethanol/distilled water (7:3) was applied to the dorsal surface of each ear of the mouse for 3 consecutive days (Days 1, 2 and 3) and then observed for systemic toxicity twice daily on Days 1, 2 and 3 and once daily on Days 4, 5 and 6. Body weights were recorded on Day 1 and 6.
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Name of test method: Local Lymph Node Assay
- Criteria used to consider a positive response: Stimulation index ≥ 3
INDUCTION EXPOSURE
- No. of exposures: Three
- Exposure period: Three consecutive days (Day 1-3)
- Test groups: 50, 25 and 10 % w/w
- Control group: Ethanol/distilled water (7:3)
- Site: Dorsal surface of the ear
- Frequency of applications: Once daily
- Duration: 1-3 d
- Concentrations: 50, 25 and 10 % w/w in ethanol/distilled water (7:3)
CHALLENGE CONTROLS
Negative control (vehicle): Ethanol/distilled water (7:3), four female mice
Positive control: α-Hexylcinnamaldehyde, Tech, 85 % (5, 10 and 25 % w/w in ethanol/distilled water 7:3), five animals in each group
TREATMENT PREPARATION AND ADMINISTRATION:
25 μL of the test substance (50, 25 and 10 % w/w) was applied to the entire dorsal surface of each ear of individual mouse using an automatic micropipette. The application was repeated on days 2 and 3. On day 6, 250 μL phosphate buffered saline (PBS) containing 20 μCi of 3H-methyl thymidine (3H-TdR: 80 μCi/mL, specific activity 2.0 Ci/mmol, GE Healthcare UK Ltd) was injected into the tail vein of each experimental mouse. Five hours later, all mice were killed by CO2 asphyxiation and the draining Auricular lymph node of each ear was excised into PBS. A single cell suspension of lymph node cells (LNC) bilaterally from individual mouse is prepared by gentle mechanical disaggregation through 200 μm-mesh stainless steel gauze. Lymph node cells are washed with an excess of PBS and precipitated with 5% trichloroacetic acid (TCA) at 4 °C for 18 h. Pellets were re-suspended in 1 mL TCA and transferred to scintillation vials containing 10 mL of scintillation fluid for 3H-counting. The number of radioactive disintegrations per minute (DPM) was measured using the Beckman LS6500 scintillation system. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Positive control results:
- The stimulation Index for α-Hexylcinnamaldehyde at concentrations of 5, 10, 25 % v/v in ethanol/distilled water 7:3 was as follows:
Concentration (% v/v) in ethanol/distilled water 7:3 Stimulation Index Result
5 4.70 Positive
10 10.57 Positive
25 17.76 Positive
where, Stimulation Index = Mean radioactivity of each treatment group / Mean radioactivity of vehicle control group - Key result
- Parameter:
- SI
- Value:
- 0.97
- Test group / Remarks:
- 10% w/w
- Key result
- Parameter:
- SI
- Value:
- 1.02
- Test group / Remarks:
- 25% w/w
- Key result
- Parameter:
- SI
- Value:
- 1.52
- Test group / Remarks:
- 50% w/w
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: Vehicle = 3761.32 dpm Test material (10 % w/w) = 3638.16 dpm Test material (25 % w/w) = 3838.19 dpm Test material (25 % w/w) = 5700.98 dpm
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- Under the study conditions the test substance was determined to be non-sensitizing.
- Executive summary:
A study was conducted to determine the skin sensitisation potential of the test substance in CBA/Ca strain mice according to OECD Guideline 429 and EU Method B.42 (Local Lymph Node Assay), in compliance with GLP. In the preliminary screening test, neither mortality nor clinical signs of toxicity were observed at concentration of 50% w/w, so this was selected as the highest dose for the main study. In the main study, three groups, each of four animals, were applied with 25 µL of the test substance (10, 25 and 50% w/w in ethanol/distilled water 7:3) to the entire dorsal surface of each ear. The negative control (vehicle) group was applied with ethanol/distilled water (7:3). Historic data of α-hexylcinnamaldehyde (5, 10 and 25% w/w in ethanol/distilled water 7:3) was used as the data for positive control group. The Stimulation Index for 10, 25 and 50% w/w of the test substance were observed to be 0.97, 1.02 and 1.52, respectively. The disintegrations per minute (dpm) for vehicle, 10, 25 and 50% w/w of the test substance were observed to be 3,761.32, 3,638.16, 3,838.19 and 5,700.98, respectively. The dpm/node for vehicle, 10, 25 and 50% w/w of the test substance were 470.17, 454.77, 479.77 and 712.62, respectively. Neither mortality nor symptoms of systemic toxicity were observed in the vehicle and treatment groups. Also, no significant changes in the body weights were seen in the animals during the study. Under the study conditions, the test substance was determined to be non-sensitizing (Sanders, 2009).
- Endpoint:
- skin sensitisation: in vitro
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Referenceopen allclose all
Neither mortality nor any signs of systemic toxicity were observed in the test or control animals during the study. No significant changes in the body weight were observed in the animals during the study.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
A study was conducted to determine the skin sensitisation potential of the test substance in CBA/Ca strain mice according to OECD Guideline 429 and EU Method B.42 (Local Lymph Node Assay), in compliance with GLP. In the preliminary screening test, neither mortality nor clinical signs of toxicity were observed at concentration of 50% w/w, so this was selected as the highest dose for the main study. In the main study, three groups, each of four animals, were applied with 25 µL of the test substance (10, 25 and 50% w/w in ethanol/distilled water 7:3) to the entire dorsal surface of each ear. The negative control (vehicle) group was applied with ethanol/distilled water (7:3). Historic data of α-hexylcinnamaldehyde (5, 10 and 25% w/w in ethanol/distilled water 7:3) was used as the data for positive control group. The Stimulation Index for 10, 25 and 50% w/w of the test substance were observed to be 0.97, 1.02 and 1.52, respectively. The disintegrations per minute (dpm) for vehicle, 10, 25 and 50% w/w of the test substance were observed to be 3,761.32, 3,638.16, 3,838.19 and 5,700.98, respectively. The dpm/node for vehicle, 10, 25 and 50% w/w of the test substance were 470.17, 454.77, 479.77 and 712.62, respectively. Neither mortality nor symptoms of systemic toxicity were observed in the vehicle and treatment groups. Also, no significant changes in the body weights were seen in the animals during the study. Under the study conditions, the test substance was determined to be non-sensitizing (Sanders, 2009).
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
The available in vivo data suggests that the substance is not sensitizing. No classification for this endpoint is therefore warranted according to CLP (EC 1272/2008) criteria.
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