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EC number: 930-010-9 | CAS number: 461432-25-7
- 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
A key study completed under GLP conditions and in accordance with OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay) and EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
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:
- 04 April 2005 to 05 May 2005
- 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)
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- GLP compliance:
- yes
- Type of study:
- mouse local lymph node assay (LLNA)
- Species:
- mouse
- Strain:
- other:
- Sex:
- female
- Details on test animals and environmental conditions:
- At the start of the study the mice were in the weight range of 15 to 23 grams and were eight to twelve weeks old. One animal was above the maximum weight per standard test method (23 grams) but this was not considered to affect the integrity of the study. Free access to mains drinking water and food was allowed through out the study. The temperature and relative humidity were set to achieve limits of 19 to 25 C and 30 to 70% respectively. The rate of air exchange was at least 15 changes per hour and the lighting was controlled by a time switch to give 12 hours continuous light and 12 hours of darkness.
- Vehicle:
- dimethylformamide
- Concentration:
- test material at concentrations of 25%, 10% or 5% w/w
- No. of animals per dose:
- Three groups of five animals each were treated at each concentration group and a further group of five animals were treated as a control group with dimethyl formamide alone.
- Details on study design:
- The preliminary screening test suggested that the test material would not produce systemic toxicity or excessive local irritation at the highest suitable concentration. The mice were treated by daily application of 25 μl of the appropriate concentration of the test material to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3) by using a micropipette whose tip is used to spread the formulation over the dorsal surface of each ear. On Day 6 all mice were injected with 250 ul of a phophate buffered saline solution containing 3H-methyl thymidine (3HTdR ) to the tail vein giving a total of 20 uCi to each mouse. All animals were observed twice daily on Day 1, 2 and 3 and once daily on days 4 ,5, and 6. Any signs of toxicity or ill health were noted. Body weights of each mouse were recorded before dosing and before termination. Five hours after administration of 3HTdR all mice were killed by carbon dioxide asphyxiation and their auricular lymph nodes were excised and a 1 ml of phosphate buffered saline was added to each set of lymph nodes. Preparation of a single cell suspension was completed for the lymph nodes cells for each individual animal following standard procedures. Determination of the 3HTdR incorporation was completed by measuring radioactive disintegration for each animal's lymph node cells by using a beta-scintillation counter.
- Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- Group mean values for disintegration per minute (dpm) and standard deviations where appropriate are completed. Individual and dose mean dpm values were assessed for dose response relationships by analysis of homogenicity of variance followed by one way analysis of variance (ANOVA). If significant results were determined from the ANOVA then pairwise comparisons were performed between control and treated groups. For homogenous datasets Dunnett's Multiple Comparison test was used and for non-homogenous datasets Dunnett's T3 Multiple Comparison Method was used.
- Positive control results:
- α-Hexylcinnamaldehyde, Tech, 85% was considered to be a sensitiser under the conditions of the test with SI rates of 5%- 2.76( Negative), at 10% SI- 3.34 (Positive) and 25% a SI of 8.91% (Positive).
- Parameter:
- other: disintegrations per minute (DPM)
- Value:
- > 1 135.46 - < 1 821.76
- Test group / Remarks:
- all test groups (5%, 10% and 25%)
- Remarks on result:
- other: see Remark
- Remarks:
- Concentration of test material in the vehicle at 5 % resulted in a mean disintegration of 1275.64 dpm which is a negative result.Concentration of test material in the vehicle at 10 % resulted in a mean disintegration of 1135.46 dpm which is a negative result. Concentration of test material in the vehicle at 25 % resulted in a mean disintegration of 1821.76 dpm which is a negative result. The results of the statistical analysis of the data indicated there was no significant difference between the control group and the test groups.
- Parameter:
- SI
- Value:
- 1.28
- Test group / Remarks:
- 5%
- Remarks on result:
- other: negative
- Parameter:
- SI
- Value:
- 1.14
- Test group / Remarks:
- 10%
- Remarks on result:
- other: negative
- Parameter:
- SI
- Value:
- 1.83
- Test group / Remarks:
- 25%
- Remarks on result:
- other: negative
- Interpretation of results:
- not sensitising
- Conclusions:
- The test material was considered to be a non-sensitiser under the conditions of the test.
Reference
There were no deaths. No signs of systemic toxicity were noted in the test or control animals
during the test. Residual test material on the ears was noted on Days 1 to 3, one hour post dosing,
in all animals treated with the test material at concentrations of 10% and 25% w/w.
|
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
Concentration of test material in the vehicle at 5 % resulted in a stimulation index (SI) of 1.28 which is a negative result. Concentration of test material in the vehicle at 10 % resulted in a stimulation index (SI) of 1.14 which is a negative result. Concentration of test material in the vehicle at 25 % resulted in a stimulation index (SI) of 1.83 which is a negative result. A stimulation index of less than 3 was recorded for the three concentrations of the test material and the substance is considered not a skin sensitizer according to EU CLP regulations.
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