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EC number: 301-097-5 | CAS number: 93981-14-7
- 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
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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study was conducted by a GLP accredited laboratory using OECD Testing Guideline 429.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
- Species:
- mouse
- Strain:
- other: CBA/Ca
- Sex:
- female
- Details on test animals and environmental conditions:
- Species Selection
The sex and strain of mouse has been selected for this study in conformance with the design of the validated test method (OECD Guidelines for Testing of Chemicals Method 429 adopted 22 July 2010).
Animal Specifications and Acclimatisation
Nulliparous, non-pregnant female CBA/CaCrl strain mice were obtained from Charles River (UK) Ltd, Margate. All animals were given a clinical inspection for ill health on arrival and a sample was weighed. Mice were arbitrarily selected from the delivery boxes and allocated to the appropriate number of cages. The condition of the animals was assessed daily throughout the acclimatisation period of 8 to 15 days. A second inspection was performed prior to study commencement to ensure the animals were suitable for the study. Overtly healthy animals were arbitrarily allocated to the study groups on the day prior to commencement of treatment. Animals in the main study were in a body weight range of 17 to 20 g on the day before dosing commenced. Individual body weights were within ± 20% of the mean body weight for mice on the study. Based on information from the supplier the mice were approximately 9 to 10 weeks old on Day 1.
Environmental Conditions, Diet, and Water
The animals were kept in the following conditions except for short periods of time where experimental procedures dictated otherwise.
Housing
The animals were group housed during acclimatisation and individually housed from Day –1 in cages that conformed to the 'Code of Practice for the Housing and Care of Animals Used in Scientific Procedures' (Home Office, London, 1989).
Bedding was provided on a weekly basis to each cage by use of clean European softwood bedding (Datesand Ltd, Manchester, UK).
Each batch of bedding was analysed for specific contaminants. No contaminants were present in bedding at levels which might have interfered with achieving the objective of the study. Results are retained on file at Covance.
Diet
Throughout the study the animals had access ad libitum to SQC Rat and Mouse Maintenance Diet No 1, Expanded, (Special Diets Services Ltd, Witham, UK). Each batch of diet was analysed for specific constituents and contaminants.
No contaminants were present in diet at levels which might have interfered with achieving the objective of the study. Results are retained on file at Covance.
Water
Mains water was provided ad libitum via water bottles. The water is periodically analysed for specific contaminants.
No contaminants were present in water at levels which might have interfered with achieving the objective of the study. Results are retained on file at Covance.
Environment
Rooms were air conditioned to provide a minimum 15 to 20 air changes/hour. The temperature and relative humidity ranges were maintained in the specified ranges of 20 to 24°C and 45 to 65%, respectively.
Fluorescent lighting was controlled automatically to give a cycle of 12 hours light and 12 hours dark.
Environmental Enrichment
In order to enrich both the environment and the welfare of the animals, they were provided with wooden Aspen chew blocks and nesting materials. The nesting materials were removed from the cages the day before dosing.
Animal Identification and Assignment to Study
The animals were arbitrarily assigned to treatment groups one day before treatment commenced.
A number written in indelible ink on the tail individually identified the mice. A colour coded card on each cage gave information including study number, animal number and sex. - Vehicle:
- dimethylformamide
- Concentration:
- Following a preliminary screening test using 50% w/v formulation, the test substance was prepared for administration at 10, 25 and 50% w/v in dimethylformamide (DMF)
- No. of animals per dose:
- 4 females
- Details on study design:
- Preliminary screening test
As no toxicological information was available regarding the systemic toxicity/irritancy potential of the test substance, a preliminary screening test was performed with one mouse. The mouse was treated by daily application of 25 µl of the test substance at the maximum suitable concentration (50% w/v in DMF) to the dorsal surface of each ear for three consecutive days (Days 1, 2 and 3). The mouse was observed daily for six days from the initiation of treatment. Any signs of toxicity or irritation during this period were recorded. Ear thickness measurements were made using a thickness gauge on Day 1 (pre-treatment), Day 3 and Day 6.
Both ears were also observed for erythema and scored using the following scale:
No erythema: Score = 0
Very slight erythema (barely perceptible): Score = 1
Well-defined eryhthema: Score = 2
Moderate to severe erythema: Score = 3
Severe erythema (beet redness) to eschar formation preventing grading of erythema: Score = 4
Body weight was recorded on Day 1 and on Day 6. The animal was killed by intraperitoneal injection of sodium pentobarbitone. Death was confirmed by cervical dislocation.
Constitution and function of groups
Groups of four female mice were assigned to study according to the table given below. Doses were selected from the concentration series 50%, 25%, 10%, 5%, 2.5%, 1.0%, 0.5% etc. Three consecutive concentrations were selected on the basis of the preliminary screening test so that the highest concentration maximised exposure whilst avoiding systemic toxicity and excessive local irritation.
Group number Group description Concentration (% w/v) Number of animals in group
1 Vehicle control - 4
2 Test – low concentration 10 4
3 Test – intermediate concentration 25 4
4 Test – high concentration 50 4 - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- mercaptobenzothiazole (CAS No 149-30-4)
- Key result
- Parameter:
- SI
- Remarks on result:
- other: see Remark
- Remarks:
- Test results were expressed in terms of Stimulation Indices, the ratios of the scintillation count per group obtained from the test groups relative to the corresponding scintillation count from controls. The threshold level for the Stimulation Index to be considered a positive indicator of the potential to cause skin sensitisation is 3.0. Test substance (10% w/v): 1.3 Test susbtance (25% w/v): 1.3 Test substance (50% w/v): 2.0
- Key result
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: Vehicle control: 696 DPM Test substance (10% w/v): 886 DPM Test substance (25% w/v): 937 DPM Test substance (50% w/v): 1376 DPM Scintillation fluid with 5% w/v trichloroacetic acid: 43 DPM
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The Local Lymph Node Assay (LLNA) demonstrated that 6-[(p-tosyl)amino] hexanoic acid, compound with 2,2',2''-nitrilotriethanol (1:1) does not have the potential to cause skin sensitisation. The test substance did not meet the criteria for classification as a skin sensitiser according to EU CLP criteria.
- Executive summary:
The skin sensitisation potential of the test substance was determined in accordance with the OECD Guideline for Testing of Chemicals 429. Following a preliminary screening test using 50% w/v of the test substance in dimethylformamide (DMF), the test substance was prepared for administration to groups of four female CBA/CaCrl mice. Volumes of 10% w/v, 25% w/v and 50% w/v of the test substance in DMF were applied to the ears of each mouse. A further group was exposed to the vehicle only (DMF). On Day 6 a 20 μCi dose of tritiated 3H-methyl thymidine was injected intravenously into each mouse. Approximately five hours later the auricular lymph nodes were recovered from each animal. The nodes from mice subjected to the same treatment were pooled and suspensions of the cellular components of the lymph nodes were prepared in 5% w/v trichloroacetic acid and processed through a scintillation counter.
Test results are expressed in terms of Stimulation Indices, the ratios of the mean scintillation count per group obtained from the test groups relative to the corresponding mean scintillation count from controls. The threshold level for the Stimulation Index to be considered a positive indicator of the potential to cause skin sensitisation is 3.0. The Stimulation Indices were found to be 1.3 for the 10% w/v test substance group, 1.3 for the 25% w/v test substance group, and 2.0 for the 50% w/v test substance group. The Local Lymph Node Assay (LLNA) demonstrated that 6-[(p-tosyl)amino] hexanoic acid, compound with 2,2',2''-nitrilotriethanol (1:1) does not have the potential to cause skin sensitisation. The test substance did not meet the criteria for classification as a skin sensitiser according to EU CLP criteria.
Reference
Preliminary screening test
Death or signs of systemic toxicty/excessive irritation were not noted. Based on this information the dose levels selected for the main test were 10%, 25% and 50% w/v in dimethylformamide.
Main test
Mortality
All animals survived treatment.
Clinical signs
There were no clinical signs indicative of a systemic effect. The vehicle and test formulation application sites remained free of irritation. Greasy fur to the back of the head and neck was noted in all Group 4 animals from Day 3 to Day 6.
Body weights
There was no indication of a treatment related effect on body weight.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
The skin sensitisation potential of the registered substance was determined in accordance with the OECD Guideline for Testing of Chemicals 429. Following a preliminary screening test using 50% w/v of the test substance in dimethylformamide (DMF), the test substance was prepared for administration to groups of four female CBA/CaCrl mice. Volumes of 10% w/v, 25% w/v and 50% w/v of the test substance in DMF were applied to the ears of each mouse. A further group was exposed to the vehicle only (DMF). On Day 6 a 20 μCi dose of tritiated 3H-methyl thymidine was injected intravenously into each mouse. Approximately five hours later the auricular lymph nodes were recovered from each animal. The nodes from mice subjected to the same treatment were pooled and suspensions of the cellular components of the lymph nodes were prepared in 5% w/v trichloroacetic acid and processed through a scintillation counter.
Test results are expressed in terms of Stimulation Indices, the ratios of the mean scintillation count per group obtained from the test groups relative to the corresponding mean scintillation count from controls. The threshold level for the Stimulation Index to be considered a positive indicator of the potential to cause skin sensitisation is 3.0. The Stimulation Indices were found to be 1.3 for the 10% w/v test substance group, 1.3 for the 25% w/v test substance group, and 2.0 for the 50% w/v test substance group. The Local Lymph Node Assay (LLNA) demonstrated that 6-[(p-tosyl)amino] hexanoic acid, compound with 2,2',2''-nitrilotriethanol (1:1) does not have the potential to cause skin sensitisation. The test substance did not meet the criteria for classification as a skin sensitiser according to EU CLP criteria.
Migrated from Short description of key information:
A study was conducted using OECD Testing Guideline 429. The substance was found to show no skin sensitisation potential.
Justification for selection of skin sensitisation endpoint:
Study was conducted by a GLP accredited laboratory using OECD Testing Guideline 429.
Justification for classification or non-classification
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.
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