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Toxicological information

Skin sensitisation

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Administrative data

Endpoint:
skin sensitisation: in vivo (LLNA)
Type of information:
experimental study
Adequacy of study:
key study
Study period:
Feb. - March 2007
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2007
Report date:
2007

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
Version / remarks:
2002
Qualifier:
according to guideline
Guideline:
EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
Version / remarks:
2004
Qualifier:
according to guideline
Guideline:
EPA OPPTS 870.2600 (Skin Sensitisation)
Version / remarks:
2003
GLP compliance:
yes
Type of study:
mouse local lymph node assay (LLNA)

Test material

In vivo test system

Test animals

Species:
mouse
Strain:
CBA
Sex:
female
Details on test animals and environmental conditions:
ANIMALS
- Species: Mouse, CBA strain, inbred, SPF-Quality. Recognized by the international guidelines as the recommended test system (e.g. OECD, EC, EPA); source: Charles River France, L'Arbresle Cedex, France.
- Number of animals: 20 females (nulliparous and non-pregnant), five females per group.
- Age and bodyweight: Young adult animals (approx. 11 weeks old) were selected. Body weight variation was within +/- 20% of the sex mean.
- Identification: Tail mark with marker pen.
- 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.
- Reliability check: The reliability test with Hexylcinnamic aldehyde was performed not more than 6 months previously or 2 months afterwards. Similar procedures were used in the reliability test and in this study.

HUSBANDRY
- Conditions: Animals were housed in a controlled environment, in which optimal conditions were considered to be approximately 15 air changes per hour, a temperature of 21.0 ± 3.0°C (actual range: 20.6 - 23.2°C), a relative humidity of 30-70% (actual range: 35 - 63%) and 12 hours artificial fluorescent light and 12 hours darkness per day.
- Accommodation: Individual housing in labeled Macrolon cages (MI type; height 12.5 cm) containing sterilized sawdust as bedding material (Litalabo, S.P.P.S., Argenteuil, France).
- Acclimatization period: The acclimatization period was at least 5 days before the start of treatment under laboratory conditions. Accommodation was as described above except that the animals were group housed in Macrolon cages (MIII type; height 18 cm). Paper (Enviro-dri, Wm. Lillico & Son (Wonham Mill Ud), Surrey, United Kingdom) was supplied as cage-enrichment.
- Diet: Free access to pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest, Germany).
- Water: Free access to tap water.
Results of analysis for each batch of diet (nutrients) and results of quarterly analysis of diet (contaminants), sawdust, paper and water were assessed and did not reveal any findings that were considered to have affected the study integrity. All certificates and results of analysis are retained in the NOTOX archives.

Study design: in vivo (LLNA)

Vehicle:
acetone/olive oil (4:1 v/v)
Concentration:
25 % open epicutaneous
50 % open epicutaneous
100 % open epicutaneous
No. of animals per dose:
5
Details on study design:
Three groups of five animals were treated with one test substance concentration (25%, 50%, 100%) per group. The highest test substance concentration was selected from the preliminary irritation study. One group of five animals was treated with vehicle.

INDUCTION - Days 1, 2 and 3
The dorsal surface of both ears was epidermally treated (25 µL/ear) with the test substance concentration, at approximately the same time per day. The concentrations were mixed thoroughly using a vortex mixer immediately prior to dosing. The control animals were treated the same as the experimental animals, except that, instead of the test substance, the vehicle alone was administered.

TREATMENT- Day 6
All animals: Each animal was injected via the tail vein with 0,25 mL of sterile phosphate buffered saline (PBS) (Merck, Darmstadt, Germany) containing 20 µCi of 3H-methyl thymidine (GE Health care,
Buckinghamshire, UK). After approximately five hours, all animals were killed by intraperitoneal injection with pentobarbital (0,2 mL/animal Euthesate®; Sanofi Sante BV, Maassluis, The Netherlands).
The draining (auricular) Iymph node of each ear was excised. The relative size of the nodes (as compared to normal) was estimated by visual examination and abnormalities of the nodes and surrounding area were recorded. The nodes were pooled for each animal in approximately 3 mL PBS.

TISSUE PROCESSING - Day 6
A single cell suspension of Iymph node cells (LNC) was prepared in PBS by gentle separation through stainless steel gauze (diameter 125 µm). LNC were washed twice with an excess of PBS by centrifugation at 200g for 10 minutes. To precipitate the DNA, the LNC were exposed to 5% trichloroacetic acid (TCA) (Merck, Darmstadt, Germany) at 4° C during the night.

RADIOACTIVITY MEASUREMENTS - Day 7
Precipitates were recovered by centrifugation, resuspended in 1 mL TCA and transferred to 10 mL of Ultima Gold cocktail (perkinEImer Life and Analytical Sciences, Boston, MA, US) as the scintillation fluid. Radioactive measurements were performed using a Packard scintillation counter (2800TR). Counting time was to a statistical precision of ± 0.2% or a maximum of 5 minutes whichever comes first The Packard 2800TR was programmed to automatically subtract background and convert Counts Per Minute (CPM) to Disintegrations Per Minute (DPM).
Positive control substance(s):
hexyl cinnamic aldehyde (CAS No 101-86-0)

Results and discussion

Positive control results:
The six monthly reliability check with Hexylcinnamic aldehyde (NOTOX Project 477214) indicates that the Local Lymph Node Assay as performed at NOTOX is an appropriate model for testing for contact hypersensitivity

In vivo (LLNA)

Resultsopen allclose all
Key result
Parameter:
EC3
Value:
42.3
Key result
Parameter:
SI
Value:
12
Test group / Remarks:
100%
Key result
Parameter:
SI
Value:
3.4
Test group / Remarks:
50%
Parameter:
SI
Value:
2.1
Test group / Remarks:
25%

Any other information on results incl. tables

Preliminary irritation study

Results of the epidermal exposures for the selection of highest test substance concentration to be tested in the main study:

- Animal 1 (50%): erythema grade 2, edema grade 0 (day 3)

- Animal 2 (100%): erythema grade 2, edema grade 0 (day 3)

Based on the results, the highest test substance concentration selected for the main study was a 100% concentration.

Skin reactions / Irritation

A dose related increase in irritation of the ears was seen, from slight erythema in all animals at low dose up to well-defined erythema in all animals at high dose. No oedema was observed in any of the animals examined.

Macroscopy of the auricular Iymph nodes and surrounding area

The majority of nodes were considered normal in size, except for the nodes of all animals treated at 100% that were enlarged. No macroscopic abnormalities of the surrounding area

were noted.

Body weights

Body weights and body weight gain of experimental animals remained in the same range as controls over the study period. The slight body weight loss, noted in some animals, was

considered not toxicologically significant.

Radioactivity measurements

Mean DPM/animal values for the experimental groups treated with test substance concentrations 25, 50 and 100% were 676, 1102 and 3878 respectively. The mean DPM/animal

value for the vehicle control group was 323.

Toxicity and Mortality

No mortality occurred and no symptoms of systemic toxicity were observed in the animals of the main study.

Applicant's summary and conclusion

Interpretation of results:
Category 1B (indication of skin sensitising potential) based on GHS criteria
Conclusions:
Based on the study results:
- according to the recommendations made in the test guidelines, the test substance would be regarded as skin sensitizer.
- according to the Globaily Harmonized System of Classification and Labeling of Chemicals (GHS) of the United Nations (New York and Geneva, 2017), the test substance should be classified as skin sensitizer (Category 1B).
- according to the EC criteria for classification and labeling requirements for dangerous substances and preparations (Council Directive 67/548/EEC), the test substance should be labeled as: may cause sensitization by skin contact (R 43).
- according to the ECETOC classification scheme for potency, the test substance would be regarded as weak skin sensitizer.
Executive summary:

Assessment for Contact Hypersensitivity to Sa 34 in the Mouse (Local Lymph Node Assay)

The study was carried out based on the guidelines described in:

OECD, Section 4, Health Effects, No.429 (2002),

EC, Council Directive 67/548/EEC, Annex V, B.42 (2004);

EPA, OPPTS 870.2600 (2003) "Skin Sensitisation".

Test substance concentrations selected for the main study were based on the results of a preliminary study.

In the main study, three groups of five experimental animals were treated with test substance concentrations of 25%, 50% or 100% on three consecutive days, by open application on the

ears. Five vehicle control animals were similarly treated, but with vehicle alone (Acetone/Olive oil (4: 1 v/v)). Three days after the last exposure, ail animals were injected with H-methyl

thymidine and after five hours the draining (auricular) Iymph nodes were excised.

After precipitating the DNA of the Iymph node ceils, radioactivity measurements were performed. The activity was expressed as the number of Disintegrations Per Minute (DPM) and a stimulation index (SI) was subsequently calculated for each group.

A dose related increase in irritation of the ears was seen, from slight erythema in all animals at low dose up to well-defined erythema in all animals at high dose. No oedema was observed in any of the animals examined.

The majority of nodes were considered normal in size, except for the nodes of all animals treated at 100% that were enlarged.

Mean DPM/animal values for the experimental groups treated with substance concentrations 25, 50 and 100% were 676, 1102 and 3878 respectively. The mean DPM/animal value for the

vehicle control group was 323.

The SI values calculated for the substance concentrations 25, 50 and 100% were 2.1, 3.4 and 12.0 respectively.

These results indicate that the test substance could elicit an SI >= 3. The data showed a dose-response and an EC3 value of 42.3% was calculated.

This conclusion should be taken with care, since a dose related increase in irritation of the ears was seen. It is known that irritation might stimulate the nodes, causing a false positive outcome of the local Iymph node assay. Based on the laboratory experience, irritation might induce an SI up to approximately 4. The SI of 12.0 in this study was considered indicative for sensitisation.

Based on these results:

- according to the recommendations made in the test guidelines, the test substance would be regarded as skin sensitizer.

- according to the Globaily Harmonized System of Classification and Labeling of Chemicals (GHS) of the United Nations (New York and Geneva, 2017), the test substance should be classified as skin sensitizer (Category 1B).

- according to the EC criteria for classification and labeling requirements for dangerous substances and preparations (Council Directive 67/548/EEC),

the test substance should be labeled as: may cause sensitization by skin contact (R 43).

- according to the ECETOC classification scheme for potency,

the test substance would be regarded as weak skin sensitizer.