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EC number: 946-615-6 | 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
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- Nanomaterial pour density
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- 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:
- 05 September to 15 December 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- GLP study conducted in compliance with OECD Guideline No. 429 without any deviation.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 017
- Report date:
- 2018
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- adopted 22 July 2010
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- UK GLP Compliance Programme (inspected on July 05, 2016/ signed on October 28, 2016)
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- Concrete of honeycomb cells of the bee by hexane extraction
- EC Number:
- 946-615-6
- IUPAC Name:
- Concrete of honeycomb cells of the bee by hexane extraction
- Test material form:
- solid
- Details on test material:
- - Appearance: pale brown solid, wax-like
Constituent 1
- Specific details on test material used for the study:
- - Storage conditions: At room temperature, protected from moisture (Dry area, unopened containers, optimum temp. 11-25 °C / 52-77 °F)
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA/Ca
- Remarks:
- CBA/CaOlaHsd
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Envigo RMS B.V., Inc., Horst, The Netherlands.
- Females nulliparous and non-pregnant: Yes
- Age at study initiation: 8-12 weeks
- Weight at study initiation: 15-23 g
- Housing: Animals were housed in suspended solid floor polypropylene cages furnished with softwood woodflakes.
- Diet: Food (2014C Teklad Global Rodent diet supplied by Envigo RMS (UK) Limited, Oxon, UK), ad libitum
- Water: Mains tap water, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 19-25 °C
- Humidity: 30-70 %
- Air changes: at least 15 changes per hour
- Photoperiod: 12 hours continuous light and 12 hours darkness
Study design: in vivo (LLNA)
- Vehicle:
- other: Tetrahydrofuran
- Concentration:
- 10%, 5% and 2.5 %
- No. of animals per dose:
- 5
- Details on study design:
- PRE-SCREEN TESTS:
- Compound solubility: For the purpose of the study, solubility checks were performed in house. All of the vehicles available (acetone/olive oil, DMF, butanone, DMSO, acetone, 1% Pluronic L92 in distilled water, 7:3 ethanol/distilled water and propylene glycol) have been investigated and none have found to be suitable, down to a concentration of 5%, even after heating to 80°C. Therefore, Tetrahydrofuran (THF) was found to produce a suitable formulation at a maximum attainable concentration of 10%. THF was shown to be a suitable vehicle in a validation study for positive control (α Hexylcinnamaldehyde, tech., 85% in tetrahydrofuran; there was no toxicity and no irritation and it produced a very acceptable dose response).
- Preliminary Screening test: As no toxicological information was available regarding the systemic toxicity/irritancy potential of the test item, a preliminary screening test was performed using one mouse. The mouse was treated by daily application of 25 μL of the test item at a concentration of 10% in THF (maximum attainable concentration), to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The mouse was observed twice daily on Days 1, 2 and 3 and once daily on Days 4, 5 and 6. Local skin irritation was scored daily. Any clinical signs of toxicity, if present, were also recorded. The body weight of the mouse was recorded on Day 1 (prior to dosing) and on Day 6.
The thickness of each ear was measured using a Mitutoyo 547-300S gauge (Mitutoyo Corporation), pre-dose and post dose on Day 1, post dose on Days 2 and 3 and on Days 4, 5 and 6. Any changes in the ear thickness were noted. Mean ear thickness changes were calculated between time periods Days 1 and 3 and Days 1 and 6. A mean ear thickness increase of equal to or greater than 25% was considered to indicate excessive irritation and limited biological relevance to the endpoint of sensitization.
- Irritation: no signs of local skin irritation were observed during the preliminary screening test at 10% in THF (maximum attainable concentration).
- Systemic toxicity: no signs of toxicity were observed during the preliminary screening test at 10% in THF (maximum attainable concentration).
- Ear thickness measurements: no marked increase in ear thickness was observed during the preliminary screening test at 10% in THF (maximum attainable concentration).
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Name of test method: Local Lymph Node Assay, individual method
- Criteria used to consider a positive response: The test item will be regarded as a sensitizer if at least one concentration of the test item results in a threefold or greater increase in 3HTdR incorporation compared to control values. Any test item failing to produce a threefold or greater increase in 3HTdR incorporation will be classified as a "non sensitizer".
TREATMENT PREPARATION AND ADMINISTRATION:
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 of the 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, α-Hexylcinnamaldehyde, tech., 85%, at a concentration of 25% v/v in Tetrahydrofuran (THF), was applied to the dorsal surface of each ear.
Local skin irritation was scored daily. The thickness of each ear was measured and recorded pre and post dose on Day 1, post dose on Days 2 and 3 and on Days 4, 5 and 6.
Five days following the first topical application of the test item, vehicle control item or positive control item (Day 6) all mice were injected via the tail vein with 0.25 mL (250 μL) of phosphate buffered saline (PBS) containing 3H-methyl thymidine (3HTdR: 80 μCi/mL, specific activity 2.0 Ci/mmoL, ARC UK Ltd) giving a total of 20 μCi to each mouse.
Termination: Five hours following the administration of 3HTdR all mice were killed by carbon dioxide asphyxiation followed by cervical separation. For each individual animal of each group the draining auricular lymph nodes were excised and processed. For each individual animal 1 mL of PBS was added to the lymph nodes.
Preparation of Single Cell Suspension: A single cell suspension of the lymph node cells for each individual animal was prepared by gentle mechanical disaggregation through a 200-mesh stainless steel gauze. 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 centrifuge tube. The lymph node cells were pelleted at 1400 rpm (approximately 190 g) for 10 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).
Determination of 3HTdR Incorporation: After approximately 18 hours incubation at approximately 4 °C, the precipitates were recovered by centrifugation at 2100 rpm (approximately 450 g) for 10 minutes, re-suspended in 1 mL of TCA and transferred to 10 mL of scintillation fluid. 3HTdR incorporation was measured by β-scintillation counting. The "Poly Q™" vials containing the samples and scintillation fluid were placed in the sample changer of the scintillator and left to stand in darkness for approximately 20 minutes. The purpose of this period of time in darkness was to reduce the risk of luminescence, which has been shown to affect the reliability of the results. After approximately 20 minutes, the vials were shaken vigorously. The number of radioactive disintegrations per minute was then measured using the Beckman LS6500 scintillation system (Beckman Instruments Inc, Fullerton, CA, USA). - 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 mean disintegrations 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 variances, then parametric one way analysis of variance (ANOVA) and Dunnett’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:
- The positive control α Hexylcinnamaldehyde, tech., 85% gave a Stimulation Index of greater than 3 (4.02) when tested at a concentration of 25% v/v in Tetrahydrofuran, thus, demonstrating the sensitivity and reliability of the test system.
In vivo (LLNA)
Resultsopen allclose all
- Key result
- Parameter:
- SI
- Value:
- 0.98
- Test group / Remarks:
- 10% in Tetrahydrofuran
- Key result
- Parameter:
- SI
- Value:
- 0.98
- Test group / Remarks:
- 5% in tetrathydrofuran
- Key result
- Parameter:
- SI
- Value:
- 1.03
- Test group / Remarks:
- 2.5% in tetrathydrofuran
- Cellular proliferation data / Observations:
- CELLULAR PROLIFERATION DATA:
See Table 7.4.1/1 below.
DETAILS ON STIMULATION INDEX CALCULATION
Stimulation index for 2.5, 5 and 10% in tetrahydrofuran were 1.03, 0.98 and 0.98, respectively.
EC3 CALCULATION
No EC3 calculation since the substance did not induced a stimulation index higher than 3 at tested cocnentrations (up to 10%).
CLINICAL OBSERVATIONS: There were no deaths. No signs of systemic toxicity, visual local skin irritation or irritation indicated by an equal to or greater than 25% increase in mean ear thickness were noted in the test or control animals during the test (See Table 7.4.2 & 7.4.3 below).
BODY WEIGHTS: 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.
Any other information on results incl. tables
Table 7.4.1/1: Individual Disintegrations per Minute and Stimulation Index
Treatment Group |
Animal Number |
dpm/Animal (a) |
Mean dpm/Animal |
Stimulation Index(b) |
Result |
Vehicle |
1-1 |
1127.45 |
1570.55 |
na |
na |
1-2 |
1740.78 |
||||
1-3 |
1406.20 |
||||
1-4 |
1956.74 |
||||
1-5 |
1621.58 |
||||
Test Item |
2-1 |
1766.36 |
1610.31 |
1.03 |
Negative |
2-2 |
1373.16 |
||||
2-3 |
1889.09 |
||||
2-4 |
2128.35 |
||||
2-5 |
894.57 |
||||
Test Item 5% in tetrahydrofuran |
3-1 |
1598.93 |
1535.81 |
0.98 |
Negative |
3-2 |
826.48 |
||||
3-3 |
2454.61 |
||||
3-4 |
1732.12 |
||||
3-5 |
1066.91 |
||||
Test Item 10% in tetrahydrofuran |
4-1 |
1150.31 |
1541.74 |
0.98 |
Negative |
4-2 |
1971.18 |
||||
4-3 |
2211.67 |
||||
4-4 |
1251.51 |
||||
4-5 |
1124.02 |
||||
Positive Control Item |
5-1 |
5147.55 |
6317.55 |
4.02 |
Positive |
5-2 |
10006.96 |
||||
5-3 |
6314.46 |
||||
5-4 |
5662.22 |
||||
5-5 |
4456.58 |
dpm= Disintegrations per minute
a= Total number of lymph nodes per animal is 2
b= Stimulation Index of 3.0 or greater indicates a positive result
Table 7.4.1/2: Individual Clinical Observations and Mortality Data
Treatment Group |
Animal Number |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
|||
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
|||||
Vehicle |
1-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
Test Item |
2-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
Test Item |
3-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
3-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
Test Item |
4-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
4-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
4-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
4-5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
Positive Control Item |
5-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
5-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
5-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
5-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
5-5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0= No signs of systemic toxicity
Table 7.4.1/3: Local Skin Irritation
Treatment Group |
Animal Number |
Local Skin Irritation |
|||||||||||
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
||||||||
left |
right |
left |
right |
left |
right |
left |
right |
left |
right |
left |
right |
||
Vehicle |
1-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
Test Item |
2-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
Test Item |
3-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
3-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
Test Item |
4-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
4-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
4-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
4-5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
Positive Control |
5-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
5-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
5-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
5-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
5-5 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- Under the test conditions, test material is classified as a non-sensitizer according to Regulation (EC) No. 1272/2008.
- Executive summary:
A study was performed to assess the skin sensitisation potential of test material in the CBA/Ca strain mouse following topical application to the dorsal surface of the ear. The method was conducted according to the OECD test guideline No 429 and in compliance with GLP.
Following a preliminary screening test in which no clinical signs of toxicity or excessive local irritation were noted at a concentration of 10% w/w, 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 Tetrahydrofuran (THF) at concentrations of 10%, 5% or 2.5% v/v. A further group of five animals was treated with THF alone. A concurrent positive control test, using a group of five animals, was also performed with the known sensitizer, α‑Hexylcinnamaldehyde tech., 85%, at a concentration of 25% v/v in THF.
The proliferative response of the lymph node cells (LNC) from the draining auricular lymph nodes was assessed five days following the initial application, by measurement of the incorporation of 3H-methyl Thymidine (3HTdR) by β-scintillation counting of LNC suspensions. The response was expressed as radioactive disintegrations per minute per lymph node (dpm/node) and as the ratio of 3HTdR incorporation into LNC of test nodes relative to that recorded for control nodes (test/control ratio), termed as Stimulation Index (SI).
Stimulation index for 2.5%, 5% or 10% v/v in THF were 1.03, 0.98 and 0.98, respectively. There were no deaths. No signs of systemic toxicity or local skin irritation (visual and ear thickness measurements) were noted in the test or control animals during the test.
The positive control α-Hexylcinnamaldehyde, tech., 85% gave a Stimulation Index of greater than 3 (4.02) when tested at a concentration of 25% v/v in THF, thus, demonstrating the sensitivity and reliability of the test system.
Under the test conditions, test material is classified as a non-sensitizer according to Regulation (EC) No. 1272/2008.
This study is considered as acceptable and satisfies the requirement for sensitisation endpoint.
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