Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 429-100-6 | CAS number: 23911-56-0
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Endpoint summary
Administrative data
Description of key information
In the key GLP compliant Guinea Pig Maximization Test according to OECD guideline 406, no evidence of delayed contact hypersensitivity was seen after treatment with the test item under the experimental conditions.
In a supporting GLP compliant study according to OECD guideline 406 (pre-guideline to OECD 429), test item was not a skin sensitizer at concentrations up to 30% and is thus designated as unlikely to be a moderate or strong skin sensitiser under the conditions of the test.
Conclusion: The test item was not a sensitiser in two different in vivo tests.
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:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 406 (Skin Sensitisation)
- Version / remarks:
- 1992 (pre-guideline to OECD 429)
- Deviations:
- no
- GLP compliance:
- yes
- Type of study:
- mouse local lymph node assay (LLNA)
- Species:
- mouse
- Strain:
- CBA/Ca
- Sex:
- male
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Age at study initiation: Young adults
- Housing: A maximum of 4 mice was housed per cage, in multiple mouse racks suitable for animals of this strain and weight range.
- Diet: Ad libitum
- Water: Ad libitum
- Acclimation period: For at least 4 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21±2
- Humidity (%): 55±15
- Air changes (per hr): At least 15 changes per hour
- Photoperiod (hrs dark / hrs light): 12/12
- IN-LIFE DATES: From 13 November 1996 to 18 November 1996 - Vehicle:
- other: acetone
- Concentration:
- 250 µL of a 1, 10 or 30% w/v test item solution
- No. of animals per dose:
- 4 animals per dose
- Details on study design:
- ANIMAL ASSIGNMENT AND TREATMENT
- Criteria used to consider a positive response: The criterion for a positive response is that one or more concentrations of the test substance should elicit a 3-fold or greater increase in isotope incorporation relative to the vehicle control group. The assay is able to identify those materials that elicit moderate or greater responses in standard guinea pig tests for skin sensitisation.
TREATMENT PREPARATION AND ADMINISTRATION: The substance solutions were applied to the dorsal surface of each ear. A vehicle control group was similarly treated using acetone alone. The procedure was repeated daily for 3 consecutive days. Three days alter the third application, all the animals were injected, via the tau vein, with approximately 250 µL of phosphate buffered saline (PBS) containing approximately 20 µCi of a 2.0 Ci/mmol specific activity 3H-methyl thymidine. Approximately 5 hours later, the animals were humanely killed by inhalation of halothane vapour followed by cervical dislocation. The draining auricular lymph nodes were removed from each animal and, together with the nodes from the other animals in the group, were placed in a container of PBS. A single cell suspension was prepared by mechanical disaggregation of lymph nodes through a 200-mesh stainless steel gauze. The cell suspensions were placed in round-bottomed centrifuge tubes and were washed three times by centrifugation with approximately 10 mL of PBS. The supematant was drawn off and discarded and approximately 3 mL of 5% w/v trichloroacetic acid (TCA) was added. After overnight precipitation at 4°C the samples were pelleted by centrifugation and the supernatant was again discarded. The cells were then resuspended in approximately 1 mL of TCA. Two days alter removal of lymph nodes, the suspensions were transferred to scintillation vials and 10 mL of scintillant (Optiphase) was added. The contents of each vial were thoroughly mixed prior to ß-scintillation counting using a Packard Tri-Carb 2500TR Liquid Scintillation Counter. Due to a high level of luminescence in one sample of the batch of studies analysed, all the samples were counted again one day later. The results from this second count were acceptable and are reported. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Positive control results:
- Hexylcinnamaldehyde was shown to have the capacity to cause skin sensitisation at concentrations of 3 and 10% w/v in acetone.
- Key result
- Parameter:
- SI
- Value:
- 1.87
- Test group / Remarks:
- 30 % (w/v)
- Key result
- Parameter:
- SI
- Value:
- 1.57
- Test group / Remarks:
- 10 % (w/v)
- Key result
- Parameter:
- SI
- Value:
- 0.67
- Test group / Remarks:
- 1 % (w/v)
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- The test item was not a skin sensitizer at concentrations up to 30% and is thus designated as unlikely to be a moderate or strong skin sensitiser under the conditions of the test.
- Executive summary:
In a GLP compliant study according to OECD guideline 406 (pre-guideline to OECD guideline 429), a sample of the test item was assessed for its skin sensitisation potential using the mouse Local Lymph Node Assay. The assay determines the level of T lymphocyte proliferation in the lymph nodes draining the site of chemical application, by measuring the amount of radiolabelled thymidine incorporated into the dividing cells. Groups of four male mice were used for this study. Approximately 25 µL of a 1, 10 or 30% w/v preparation of the test substance in acetone was applied to the dorsal surface of each ear. A vehicle control group was similarly treated using acetone alone. The procedure was repeated daily for 3 consecutive days.Three days after the third application, all the animals were injected, via the tail vein, with approximately 250 µL of phosphate buffered saline (PBS) containing approximately 20 µCi of a 2.0 Ci/mmol specific activity 3H-methyl thymidine. Approximately 5 hours later, the animals were humanely killed by inhalation of halothane vapour followed by cervical dislocation. The draining auricular lymph nodes were removed from each animal and pooled with the nodes from the other animals in the group. A single cell suspension was prepared by mechanical disaggregation of lymph nodes through a 200-mesh stainless steel gauze. The cell suspensions were washed three times by centrifugation with approximately 10 mL of PBS. Approximately 3 mL of 5% w/v trichloroacetic acid (TCA) was added. After overnight precipitation at 4°C, the samples were pelleted by centrifugation and the supernatant was again discarded. The cells were then resuspended in approximately 1 mL of TCA. Two days after removal of lymph nodes, the suspensions were transferred to scintillation vials, 10 mL of scintillant (Optiphase) was added and ß-scintillation was counted. In a positive control study, hexylcinnamaldehyde was shown to have the capacity to cause skin sensitisation at concentrations of 3 and 10% w/v in acetone, confirming the validity of the protocol used for this study.The test substance induced SI values of 0.67 (1% w/v), 1.57 (10% w/v) and 1.87 (30% w/v) and was thus considered to be not sensitizing in the concentrations tested. It was thus concluded that the test item does not have the capacity to cause moderate or strong skin sensitisation.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
Skin sensitisation in vivo, RL1
The dermal sensitising potential of the test item was investigated according to one of the methods recommended in the OECD Guidelines No. 406, "Skin Sensitisation", 1992 and the EEC Guideline "EEC 92/69 part 6B", 1992. The delayed contact hypersensitivity test used was the Guinea Pig Maximization Test described by B. Magnusson and A. M. Kligman. Thirty animals divided into a test group of 20 animals and a negative control group of 10 animals were included in the study. The study comprised an induction and a challenge phase. The animals in the test group were induced with the test article whereas the animals in the control group were induced with Arachis oil for intradermal induction and Ethanol/diethylphthlate 1:1 for dermal induction. The induction procedure included intradermal injections and a closed patch topical application one week apart. All animals were challenged by a closed patch topical application of the test article for 24 hours. The challenge procedure included a closed patch topical treatment of the test article an the flank 3 weeks after the intradermal injection. The skin reactions were evaluated 24 and 48 hours after the challenge application. A 6% (w/w) test article concentration in Arachis oil was used for the intradermal induction. A 50% (w/w) test article concentration in Ethanol/diethylphthlate 1:1 was used for the topical induction and a 25% (w/w) test article concentration in Ethanol/diethylphthlate 1:1 was used for the challenge application. Under these experimental conditions no evidence of delayed contact hypersensitivity was seen after treatment with the test item.
Skin sensitisation in vivo, RL2
In a GLP compliant study according to OECD guideline 406 (pre-guideline to OECD guideline 429), a sample of the test item was assessed for its skin sensitisation potential using the mouse Local Lymph Node Assay. The assay determines the level of T lymphocyte proliferation in the lymph nodes draining the site of chemical application, by measuring the amount of radiolabelled thymidine incorporated into the dividing cells. Groups of four male mice were used for this study. Approximately 25 µL of a 1, 10 or 30% w/v preparation of the test substance in acetone was applied to the dorsal surface of each ear. A vehicle control group was similarly treated using acetone alone. The procedure was repeated daily for 3 consecutive days.Three days after the third application, all the animals were injected, via the tail vein, with approximately 250 µL of phosphate buffered saline (PBS) containing approximately 20 µCi of a 2.0 Ci/mmol specific activity 3H-methyl thymidine. Approximately 5 hours later, the animals were humanely killed by inhalation of halothane vapour followed by cervical dislocation. The draining auricular lymph nodes were removed from each animal and pooled with the nodes from the other animals in the group. A single cell suspension was prepared by mechanical disaggregation of lymph nodes through a 200-mesh stainless steel gauze. The cell suspensions were washed three times by centrifugation with approximately 10 mL of PBS. Approximately 3 mL of 5% w/v trichloroacetic acid (TCA) was added. After overnight precipitation at 4°C, the samples were pelleted by centrifugation and the supernatant was again discarded. The cells were then resuspended in approximately 1 mL of TCA. Two days after removal of lymph nodes, the suspensions were transferred to scintillation vials, 10 mL of scintillant (Optiphase) was added and ß-scintillation was counted. In a positive control study, hexylcinnamaldehyde was shown to have the capacity to cause skin sensitisation at concentrations of 3 and 10% w/v in acetone, confirming the validity of the protocol used for this study.The test substance induced SI values of 0.67 (1% w/v), 1.57 (10% w/v) and 1.87 (30% w/v) and was thus considered to be not sensitizing in the concentrations tested. It was thus concluded that the test item does not have the capacity to cause moderate or strong skin sensitisation.
Conclusion: The test item was not a sensitiser in two different in vivo tests.
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
Classification, Labeling, and Packaging Regulation (EC) No 1272/2008
The available test data are reliable and suitable for classification purposes under Regulation (EC) No 1272/2008. Thus, the test item is considered to be not classified for skin sensitisation under Regulation (EC) No 1272/2008, as amended for fifteenth time in Regulation (EU) No 2020/1182.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
![ECHA](/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/echa_logo.png)