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EC number: 943-540-0 | CAS number: -
- 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
Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 11 November 2014 to 02 December 2015
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 015
- Report date:
- 2015
Materials and methods
Test guidelineopen allclose all
- 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 (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- Reaction Products of Diphosphorus Pentaoxide with Alcohols, C14-18 even, salted with Amines, C12-14, Tert-alkyl
- EC Number:
- 943-540-0
- Molecular formula:
- Too complex
- IUPAC Name:
- Reaction Products of Diphosphorus Pentaoxide with Alcohols, C14-18 even, salted with Amines, C12-14, Tert-alkyl
- Details on test material:
- Purity: 100%
Physical state / Appearance: pale amber liquid
Expiry date: 09 May 2016
Storage Conditions: room temperature in the dark
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- Female CBA/Ca (CBA/CaOlaHsd) strain mice were nulliparous and non-pregnant.
Acclimatization period of at least five days.
Animals were in the weight range of 15 to 23 g, and were eight to twelve weeks old.
Free access to mains tap water and food.
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 approximately fifteen changes per hour.
The lighting was controlled by a time switch to give twelve hours continuous light (06.00 to 18.00) and twelve hours darkness.
Study design: in vivo (LLNA)
- Vehicle:
- other: Neat and in Butanone
- Concentration:
- 100% neat and 10% and 1% v/v in butanone
- No. of animals per dose:
- 5
- Details on study design:
- Groups of five mice were treated with the test item at concentrations of 100%, 10% or 1.0% v/v in butanone. The preliminary screening test suggested that the test item 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 item to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3).
The test item formulation was administered using an automatic micropipette and spread over the dorsal surface ofthe ear using the tip of the pipette.
A further group of five mice received the vehicle alone in the same manner.
The positive control animals were similarly treated to the test animals except that 25 µL of the positive control item, alpha-Hexylcinnamaldehyde, tech., 85%, at a concentration of 15% v/v in butanone as applied to the dorsal surface of each ear.
The thickness of each ear was measured and recorded as described in the preliminary screening test.
Five hours following the administration of 3HTdR all mice were killed by carbon dioxide asphyxiation followed by cervical separation.
Preparation of Single Cell Suspension: A single cell suspension of the lymph node cells for each individual animal was prepared by gentle mechanical disaggregation. The lymph node cells were rinsed through the gauze with 4 mL of PBS into a petri dish labeled with the study number and dose concentration. The lymph node cells suspension was transferred to a centrifuge tube. The petri dish was washed with an additional 5 mL of PBS to remove all remaining lymph node cells and these were added to the centrifiige tube. The lymph node cells were pelleted at 1400 rpm (approximately 190 g) for ten minutes. The pellet was re-suspended in 10 mL of PBS and re-pelleted. To precipitate out the radioactive material, the pellet was re-suspended in 3 mL of 5% Trichloroacetic acid (TCA).
3HTdR incorporation was measured by B-scintillation counting. The number of radioactive disintegrations per minute was then measured. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- Data was processed to give group mean values for disintegrations per minute and standard deviations where appropriate. Individual and group meandisintegrations per minute values were assessed for dose response relationships. Data was first assessed for suitability by analysis of normality and homogeneity of variance. If the assumptions that the data are both normally distributed and has homogeneity of ariances, then parametric one way analysis of variance (ANOVA) and Durmett’s multiple comparison procedure were used to determine statistical significance. If the assumptions were not met, non-parametric Kruskal-Wallis Rank Sum and Mann-Whitney U test procedures were used.
Results and discussion
- Positive control results:
- 15% v/v of the positive control in butanone gives positive results with a stimulation Index score of 8.23
In vivo (LLNA)
Resultsopen allclose all
- Key result
- Parameter:
- SI
- Value:
- 1.55
- Test group / Remarks:
- 1%
- Key result
- Parameter:
- SI
- Value:
- 2.79
- Test group / Remarks:
- 10%
- Key result
- Parameter:
- SI
- Value:
- 10.01
- Test group / Remarks:
- 100%
Any other information on results incl. tables
There were no deaths. No signs of systemic toxicity were noted in the test or control animals during the test. No observations of erythema were noted on the ears of all animals treated with the test item or positive control item.
Body weight change of the test animals between Day 1 and Day 6 was comparable to that observed in the corresponding control group animals over the same period.
Calculation of EC3 value
EC3 = 10 + [[(3 -2.79) / (10.01 - 2.79)] x (100 - 10)] = 13
The concentration of test item expected to cause a 3 -fold increase in 3HTdR incorporation (EC3 value) was calculated to be 13 %.
Applicant's summary and conclusion
- Interpretation of results:
- sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The test item was considered to be a sensitiser under the conditions of the test and the concentration of test item expected to cause a 3 -fold increase in 3HTdR incorporation (EC3 value) was calculated to be 13 %. Alpha-Hexylcinnamaldehyde, tech., 85% gave a Stimulation Index of greater than 3 when tested at a concentration of 15% v/v in butanone thus demonstrating the sensitivity and reliability of the test system.
- Executive summary:
Introduction
A study was performed to assess the skin sensitization potential of the test item in the CBA/Ca strain mouse following topical application to the dorsal surface of the ear. The method was designed to be compatible with the OECD Guideline for the Testing of Chemicals No. 429 "Skin Sensitization: Local Lymph Node Assay" (adopted 22 July 2010) and Method B.42 Skin Sensitization (Local Lymph Node Assay) of Commission Regulation (EC) No. 440/2008.
Methods
Following a preliminary screening test in which no clinical signs of toxicity were noted at a concentration of 100%, this concentration was selected as the highest dose investigated in the main test of the Local Lymph Node Assay. Three groups, each of five animals, were treated with 50 µL (25 µL per ear) of the test item as a solution in butanone at concentrations of 100% or 10% or 1 % v/v in butanone. A further group of five animals was treated with butanone alone. A concurrent positive control test, using a group of five animals, was also performed with the known sensitizer, alpha-Hexylcinnamaldehyde tech., 85%, at a concentration of 15% v/v in butanone.
The Stimulation Index expressed as the mean radioactive incorporation for each treatment group divided by the mean radioactive incorporation of the vehicle control group are as follows:
1% v/v of the test item in butanone gave negative results with a stimulation Index score of 1.55
10% v/v of the test item in butanone gave negative results with a stimulation Index score of 2.79
100% v/v of the test item gave positive results with a stimulation Index score of 10.01
25% v/v of the positive control in butanone gave positive results with a stimulation Index score of 8.23
Conclusion
The test item was considered to be a sensitiser under the conditions of the test and the concentration of test item expected to cause a 3 -fold increase in 3HTdR incorporation (EC3 value) was calculated to be 13 %. Alpha-Hexylcinnamaldehyde, tech., 85% gave a Stimulation Index of greater than 3 when tested at a concentration of 15% v/v in butanone thus demonstrating the sensitivity and reliability of the test system.
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