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EC number: 700-136-7 | 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:
- January 07 - February 02, 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Well documented and reported study, conducted according to internationally accepted technical guidelines and in compliance with GLP in recognized contract research organization.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- of 2002
- Deviations:
- yes
- Remarks:
- During the range-finding study animal housing at 16-22ºC and 20-65% relative humidity. These deviations did not affect the choice of dose range for the main study. Study integrity was not adversely affected by these deviations.
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- of 2008
- Deviations:
- yes
- Remarks:
- During the range-finding study animal housing at 16-22ºC and 20-65% relative humidity. These deviations did not affect the choice of dose range for the main study. Study integrity was not adversely affected by these deviations.
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.2600 (Skin Sensitisation)
- Version / remarks:
- of 2003
- Deviations:
- yes
- Remarks:
- During the range-finding study animal housing at 16-22ºC and 20-65% relative humidity. These deviations did not affect the choice of dose range for the main study. Study integrity was not adversely affected by these deviations.
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
Reference
- Name:
- Unnamed
- Type:
- Constituent
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Mouse (females only), strain: CBA/J (inbred, SPF-Quality), with appropriate range of bodyweight at study start.
- Source: Charles River France, L’Arbresle Cedex, France.
- Age at treatment start (1st induction): Approx. 10 weeks.
- Weight at treatment start (1st induction): Minimum 20 g, maximum 24 g.
- Housing: Individual housing in M I type cages. (During acclimatization group housing in M III type cages).
- Bedding material: Commercially available sterilized saw dust (Litalabo, S.P.P.S., Argenteuil, France).
- Cage enrichment: Commercially available paper (Enviro-dri, Wm. Lillico & Son (Wonham Mill Ltd), Surrey, UK).
This was removed from Day 1 (prior to dosing) until ear scoring on Day 3. - Diet (ad libitum): Commercially available pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest,
Germany).
- Water (ad libitum): Tap water
- Acclimation period: At least 5 days before treatment start under laboratory conditions.
- Health inspection: A health inspection was performed prior to treatment, to ensure that the animals are in a good state of health. Special attention was paid to the ears, which were intact and free from any abnormality.
ENVIRONMENTAL CONDITIONS
During the preliminary range-finding study the lower limits of temperature and relative humidity in the animal rooms were lower than recommended in the technical guidelines: 16-22ºC and 20-65% relative humidity. These deviations did not affect the choice of dose range for the main study. Study integrity was not adversely affected by these deviations.
During the main study animal housing and environmental conditions were appropriate for sensitization testing by the LLNA test in the mouse: Controlled environment with approximately 15 air changes per hour, 12 hours artificial fluorescent light and 12 hours darkness per day and 20 – 24ºC. The relative humidity during the main study was 38 – 63%.
Study design: in vivo (LLNA)
- Vehicle:
- dimethylformamide
- Concentration:
- Range-Finding Test:
Induction on Days 1, 2 and 3 at the following concentrations:
10% (1 female), 25% (3 females), 50% (2 females).
The concentrations of test substance are expressed as percentage of water- and minor impurity-free test substance in the vehicle (w/w). One animal of the 25% group was treated only on Days 1 and 2, as it was found dead on Day 3 prior to dosing.
Main Study:
Induction on Days 1, 2 and 3 at the following concentrations:
0% (vehicle control, 5 females), 10% (5 females), 25% (5 females), 50% (5 females).
The concentrations of test substance are expressed as percentage of water- and minor impurity-free test substance in the vehicle (w/w).
- No. of animals per dose:
- Range-Finding Test:
1 to 3 female animals per dose (for details see Table 2 in section "Remarks on results including tables and figures").
Main Study:
5 female animals per dose (for details see Table 3 in section "Remarks on results including tables and figures"). - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
Results and discussion
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Remarks on result:
- other: see Remark
- Remarks:
- Mean Stimulation Index (SI) values for the experimental groups treated with 10, 25 and 50% test substance dilutions* were 3.0, 7.9 and 3.9, respectively. Deatailed SI results are presented in Table 5 in section "Remarks on results including tables and figures". Table 4 of this section indicates which individual DPM values were included in the respective group mean DPM values and which were considered to be outliers. Group mean DPM values were used for calculation the SI values. ------------------------------------------------------------------------------------------------------------------------------------- * Expressed as percentage of water- and minor impurity-free test substance in the vehicle (w/w).
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: see Remark
- Remarks:
- Mean DPM/animal values for the experimental groups treated with 10, 25 and 50% test substance dilutions* were 1043, 2749 and 1361 DPM/animal, respectively. For the vehicle control group, on average 350 DPM/animal were recorded. Deatailed DPM results are presented in Tables 4 and 5 in section "Remarks on results including tables and figures". ------------------------------------------------------------------------------------------------------------------------------------- * Expressed as percentage of water- and minor impurity-free test substance in the vehicle (w/w).
Any other information on results incl. tables
Table 2: Range-finding (Preliminary Irritation) Study. |
|||||||
|
|
Day 1 |
Day 3 |
||||
|
|
|
Skin Reactions at Dorsal Ear SurfaceB |
|
|||
|
|
|
Left Ear |
Right Ear |
|
||
Animal No. |
% Test SubstanceA |
Bodyweight (g) |
Erythema |
Edema |
Erythema |
Edema |
Bodyweight (g) |
5 |
10 |
21 |
G |
0 |
G |
0 |
20 |
1 |
25 |
24 |
G |
0 |
G |
0 |
C |
3 |
25 |
23 |
G |
0 |
G |
0 |
22D |
6 |
25 |
22 |
G |
0 |
G |
0 |
20 |
2 |
50 |
24 |
G |
0 |
G |
0 |
22E |
4 |
50 |
22 |
G |
0 |
G |
0 |
21E |
A.Vehicle: Dimethylformamide. The concentrations of test substance in the vehicle are expressed as percentage of water- and minor impurity-free test substance in the vehicle (w/w).
B. Attempt was made to clean the ears of residual test substance with tap water and vehicle.
C. Animal was found dead prior to dosing on Day 3 (bodyweight 22 gram).
D. Animal was found on Day 4.
E. Hard ears and bold spots behind the ears observed.
G. No scoring possible due to brown discoloration of the ears by the test substance.
Table 3: Main Study Skin Reactions, Bodyweights and Relative Size of Auricular Lymph Nodes |
||||||||||
|
|
|
Day 1 |
Day 3 |
Day 6 |
|||||
|
|
|
|
Skin Reactions at |
|
Size Lymph NodesD |
||||
|
|
|
|
Left Ear |
Right Ear |
|
Left |
Right |
||
Group |
% Test SubstanceA |
Animal No.B |
BW |
Ery-thema |
Ede-ma |
Ery-thema |
Ede-ma |
BW |
|
|
1 |
0% |
1 |
24 |
0 |
0 |
0 |
0 |
23 |
n |
n |
|
(vehicle) |
2 |
22 |
0 |
0 |
0 |
0 |
21 |
n |
n |
|
|
3 |
21 |
0 |
0 |
0 |
0 |
21 |
n |
n |
|
|
4 |
22 |
0 |
0 |
0 |
0 |
21 |
n |
n |
|
|
5 |
24 |
0 |
0 |
0 |
0 |
23 |
n |
n |
2 |
10% |
6 |
22 |
G |
0 |
G |
0 |
21 |
n |
n |
|
|
7 |
20 |
G |
0 |
G |
0 |
21 |
n |
n |
|
|
8 |
21 |
G |
0 |
G |
0 |
22 |
n |
n |
|
|
9 |
23 |
G |
0 |
G |
0 |
23 |
n |
n |
|
|
10 |
23 |
G |
0 |
G |
0 |
21 |
n |
n |
3 |
25% |
11 |
21 |
G |
0 |
G |
0 |
21 |
+++ |
n |
|
|
12 |
22 |
G |
0 |
G |
0 |
22 |
n |
n |
|
|
13 |
24 |
G |
0 |
G |
0 |
22 |
+ |
n |
|
|
14 |
22 |
G |
0 |
G |
0 |
20 |
n |
n |
|
|
15 |
23 |
G |
0 |
G |
0 |
21 |
n |
n |
4 |
50%E |
16 |
21 |
G |
0 |
G |
0 |
21 |
n |
n |
|
|
17 |
20 |
G |
0 |
G |
0 |
20 |
n |
n |
|
|
18 |
23 |
G |
0 |
G |
0 |
23 |
n |
n |
|
|
19 |
22 |
G |
0 |
G |
0 |
21 |
n |
+ |
|
|
20 |
23 |
G |
0 |
G |
0 |
21 |
n |
n |
A.Vehicle: Dimethylformamide. The concentrations of test substance in the vehicle are expressed
as percentage of water- and minor impurity-free test substance in the vehicle (w/w).B. Animal (identification) number.
C. BW = bodyweight (grams).
D. Relative size of auricular lymph nodes (–, –– or –––: degree of reduction, +, ++ or +++: degree
of enlargement, n: considered to be normal).E. Hard ears and bold spots behind the ears observed.
G. No scoring possible due to brown discoloration of the ears by the test substance.
Table 4: Main Study |
|||
Group |
% Test SubstanceA |
Animal No. |
DPMB/Animal |
1 |
0% |
1 |
635 |
|
(vehicle) |
2 |
120 |
|
|
3 |
266 |
|
|
4 |
1279C |
|
|
5 |
378 |
2 |
10% |
6 |
747 |
|
|
7 |
952 |
|
|
8 |
1324 |
|
|
9 |
621 |
|
|
10 |
1573 |
3 |
25% |
11 |
8919D |
|
|
12 |
2379 |
|
|
13 |
2520 |
|
|
14 |
3566 |
|
|
15 |
2532 |
4 |
50% |
16 |
804 |
|
|
17 |
1273 |
|
|
18 |
835 |
|
|
19 |
3022 |
|
|
20 |
870 |
A.Vehicle:
Dimethylformamide. The concentrations of test substance in the vehicle
are
expressed as percentage of water- and minor impurity-free test substance
in the vehicle (w/w).
B. DPM = Disintegrations per Minute
C. Value rejected and not used for interpretation (outside historical range for vehicle).
D. Value rejected and not used for interpretation (outlier response).
Table 5: Main Study |
|||||||
Group |
% Test SubstanceA |
Mean DPM ± SEMB |
SI ± SEM |
||||
2 |
10% |
1043 |
± |
178 |
3.0 |
± |
1.1 |
3 |
25% |
2749 |
± |
274 |
7.9 |
± |
2.6 |
4 |
50% |
1361 |
± |
424 |
3.9 |
± |
1.7 |
1 |
0% (vehicle) |
350 |
± |
109 |
1.0 |
± |
0.4 |
A.Vehicle:
Dimethyl formamide. The concentrations of test substance in the vehicle
are
expressed as percentage of water- and minor impurity-free test substance
in the vehicle (w/w).
B. SEM = Standard Error of the Mean
Applicant's summary and conclusion
- Interpretation of results:
- sensitising
- Remarks:
- Migrated information
- Conclusions:
- In view of mean stimulation indices (SI) of 3.0, 7.9 and 3.9 attained in the 10%, 25% and 50% dose groups*, respectively, the substance was classified as "irritant (Xi)" and "May cause sensitisation by skin contact (R43)” according to EU-DSD classification rules [DIRECTIVE 67/548/EEC] and as "Category 1 (Warning: May cause an allergic skin reaction)" according to EU-GHS classification rules [REGULATION (EC) 1272/2008]. From the SI data attained, an EC3 value (the estimated test substance concentration that will give a SI of 3) of 10.1%* was determined by linear interpolation.
---------------------------------------------------------------------------------------------------------------------------
* Expressed as percentage of water- and minor impurity-free test substance in the vehicle (w/w). - Executive summary:
the test substance was tested for skin sensitisation in female CBA/J mice according to OECD Guideline 429 (Local Lymph Node Assay) and the corresponding EC and, EPA-OPPTS Technical Guidelines in compliance with GLP. Reliability grade 1 was assigned. The suitability of the mouse strain used and methods adopted by the testing laboratory were confirmed in previous reliability checks using hexyl cinnamic aldehyde (CAS No. 101-86-0) as a positive control agent.
From a preliminary range-finding (irritation) test, suitable concentrations of 10%, 25% and 50% the test substance in Dimethylformamide were chosen for the main LLNA sensitisation study. These concentrations are expressed as percentage of water- and minor impurity-free test substance in the vehicle Dimethylformamide (w/w). In the main study, 20 mice (5 females / dose group) were used of which 5 served as vehicle controls. On Days 1, 2 and 3, the animals were induced by epidermal administration of the vehicle or test substance dilutions (25μL/ear/day) onto the dorsal surface of both ears. Main study animals were checked for mortality/viability twice daily and for signs of systemic toxicity once daily. In addition, bodyweights were recorded on Days 1 (prior to treatment) and 6, and irritation of the ears (erythema and edema) as well as any other local effects were recorded approximately 3-4 hours after the third treatment. 3H-methyl thymidine diluted in sterile phosphate buffered saline was injected into the tail vein on Day 6 for radioactive labelling. Five hours afterwards the draining (auricular) lymph nodes were excised and pooled per animal. On Day 7, radioactivity of precipitated DNA from the excised lymph nodes was measured by scintillation counting and automatically expressed as Disintegrations per Minute (DPM). From these data, the stimulation index (SI) reflecting the ratio of lymphocyte proliferation in treated groups to that in the vehicle control group was calculated for each group.
Two outlier responses, one in the vehicle control group and one in the 25% dose group, with excessively high DPM values were eliminated from the group mean DPM. The mean DPM value of the vehicle control group was 350 DPM/animal. Mean DPM values in the 10%, 25% and 50% dose groups were, 1043, 2749 and 1361, corresponding to mean stimulation index (SI) values of 3.0, 7.9 and 3.9, respectively. Hence, the SI threshold of ≥ 3.0, indicating a positive sensitisation response, was attained in all treated groups, although a dose related increase was only evident at 10% and 25% and not at 50%. From these data an EC3 value (the estimated test substance concentration that will give a SI of 3) of 10.1% was calculated. The lower response in the 50% dose group than in the 25% group may have been related to the finding of hard ears seen in all animals of the 50% group which could have impaired skin penetration in this group. This could also explain mortality/survival attained in the preliminary range-finding test, in which two of three animals of the 25% dose group died whilst both animals of the 50% group survived. There were no premature deaths and no signs of systemic toxicity in the main study. Bodyweights did not distinguish treated groups from the vehicle control group. Scoring for erythema was not possible in treated animals, because of brown discoloration of the ears by the test substance. Edema were not evident. In two animals of the 25% dose group and one animal of the 50% group auricular lymph nodes of one of the ears were enlarged, in all other main study animals their size was considered to be normal.
According to EU-DSD classification rules [DIRECTIVE 67/548/EEC] the results attained in this study would lead to classification and labelling as “Xi” (irritant) and “R43” (May cause sensitisation by skin contact) and according to EU-GHS classification rules [REGULATION (EC) 1272/2008] they would lead to “Category 1” (Warning: May cause an allergic skin reaction).
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