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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Administrative data

Description of key information

Key value for chemical safety assessment

Skin sensitisation

Link to relevant study records
Reference
Endpoint:
skin sensitisation: in vivo (LLNA)
Type of information:
experimental study
Adequacy of study:
key study
Study period:
From 18 Jun to 07 Jul 2014
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: Study run to a method comparable with current guidelines and to GLP
Qualifier:
according to guideline
Guideline:
OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
Deviations:
no
GLP compliance:
yes
Type of study:
mouse local lymph node assay (LLNA)
Species:
mouse
Strain:
CBA
Sex:
female
Details on test animals and environmental conditions:
TEST ANIMALS
- Source: Janvier, Le Genest-Saint-Isle, France
- Age at study initiation: approx. 10 weeks old
- Weight at study initiation: Body weight variation was within +/- 20% of the sex mean
- Housing: labeled Makrolon cages containing sterilised sawdust as bedding material. Paper and shelters were supplied as cage-enrichment.
- Diet (e.g. ad libitum): pelleted rodent diet
- Water (e.g. ad libitum): tap water
- Acclimation period: at least 5 days before the start of treatment under laboratory conditions

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 18 to 24°C
- Humidity (%): 40 to 70%
- Air changes (per hr): at least 10 air changes/hour
- Photoperiod (hrs dark / hrs light): a 12-hour light/12-hour dark cycle

IN-LIFE DATES: From 18 Jun to 07 Jul 2014
Vehicle:
acetone/olive oil (4:1 v/v)
Concentration:
10, 25 or 50% w/w
No. of animals per dose:
five females
Details on study design:
RANGE FINDING TESTS:
No irritation and no signs of systemic toxicity were observed in any of the animals examined except for the scaliness noted for the animals at 50% on Day 6. Bald spots behind the ears were found on one animal at 50% on Day 6. White test substance remnants were present on the dorsal surface of theears of both animals at 25% (Days 1-3) and 50% (Days 1-4 and one animal on one ear at Day 5), which did not hamper scoring of the skin reactions. Variations in ear thickness during the observation period were less than 25% from Day 1 pre-dose values.
Based on these results, the highest test substance concentration selected for the main study was a 50% concentration.

MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Criteria used to consider a positive response: If the results indicate a SI ≥ 3, the test substance may be regarded as a skin sensitizer.

TREATMENT PREPARATION AND ADMINISTRATION:
- Induction - Days 1, 2 and 3:
The dorsal surface of both ears was topically treated (25 µL/ear) with the test substance concentration of 10, 25 or 50% w/w on three consecutive days. The concentrations were stirred with a magnetic stirrer immediately prior to dosing. The control animals were treated in the same way as the experimental animals, except that the vehicle was administered instead of the test substance.
- Excision of the nodes - Day 6:
Each animal was injected via the tail vein with 0.25 mL of sterile phosphate buffered saline (PBS) containing 20 µCi of 3H-methyl thymidine. After approximately five hours, all animals were killed by intraperitoneal injection (0.2 mL/animal) with Euthasol 20%. The draining (auricular) lymph 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 for radioactivity - Day 6:
Following excision of the nodes, a single cell suspension of lymph 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 200 g for 10 minutes at 4ºC. To precipitate the DNA, the LNC were exposed to 5% trichloroacetic acid and stored in the refrigerator until the next day.
- Radioactivity measurements - Day 7:
Precipitates were recovered by centrifugation, resuspended in 1 mL TCA and transferred to 10 mL of Ultima Gold cocktail 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 came first. The scintillation counter was programmed to automatically subtract background and convert Counts
Per Minute (CPM) to Disintegrations Per Minute (DPM).
- Observations:
Mortality/Viability: Twice daily.
Body weights: On Day 1 (pre-dose) and Day 6 (prior to necropsy).
Clinical signs: Once daily on Days 1-6 (on Days 1-3 between 3 and 4 hours after dosing).
Irritation: Once daily on Days 1-6 (on Days 1-3 within 1 hour after dosing) according to the following numerical scoring system. Furthermore, a description of all other (local) effects was recorded.
Statistics:
None stated
Parameter:
SI
Remarks on result:
other: The SI values calculated for the substance concentrations 10, 25 and 50% were 1.2, 1.0 and 1.3, respectively.
Parameter:
other: disintegrations per minute (DPM)
Remarks on result:
other: Mean DPM/animal values for the experimental groups treated with test substance concentrations 10, 25 and 50% were 359, 311 and 414 DPM, respectively. The mean DPM/animal value for the vehicle control group was 310 DPM.

Skin reactions / Irritation:

No irritation of the ears was observed in any of the animals examined. White test substance remnants were present on the dorsal surface of the ears of all animals at 25% (Days 2 and 3) and 50% (Days 1-3), which did not hamper scoring of the skin reactions.

Systemic toxicity:

No mortality occurred and no clinical signs of systemic toxicity were observed in the animals of the main study. Body weights and body weight gain of experimental animals remained in the same range as controls over the study period.

Macroscopy of the auricular lymph nodes and surrounding area:

All auricular lymph nodes of the animals of the experimental and control groups were considered normal in size. No macroscopic abnormalities of the surrounding area were noted for any of the animals.

Interpretation of results:
not sensitising
Remarks:
Migrated information Criteria used for interpretation of results: EU
Conclusions:
Since there was no indication that the test substance elicited a SI ≥ 3 when tested up to 50%, the test substance was not considered to be a skin sensitizer.
Endpoint conclusion
Endpoint conclusion:
no adverse effect observed (not sensitising)
Additional information:

One study is available which was conducted according to OECD Guideline 429 under GLP (Latour, 2014).

Since there was no indication that the test substance elicited a SI ≥ 3 when tested up to 50%, the test substance was not considered to be a skin sensitizer.


Migrated from Short description of key information:
One study is available (Latour, 2014). Since there was no indication that the test substance elicited a SI ≥ 3 when tested up to 50%, the test substance was not considered to be a skin sensitizer.

Justification for selection of skin sensitisation endpoint:
Study run to a method comparable with current guidelines and to GLP

Justification for classification or non-classification

Skin sensitisation:

Animal test gave negative result (LLNA result SI < 3 (actual value 1.3)).

Therefore in accordance with Regulation (EC) No. 1272/2008 (as amended by Regulation (EC) No. 286/2011) Table 3.4.2, this substance should not be classified as skin sensitiser based on the test data.