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Diss Factsheets

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:
May-June 2008
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2008
Report date:
2008

Materials and methods

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

Test material

Constituent 1
Chemical structure
Reference substance name:
Esterification product of castor oil and tetrahydromethyl-1,3-isobenzofuranedione
EC Number:
700-064-6
Cas Number:
2105830-60-0
Molecular formula:
Not applicable as this is a UVCB substance
IUPAC Name:
Esterification product of castor oil and tetrahydromethyl-1,3-isobenzofuranedione
Test material form:
liquid
Details on test material:
- Molecular weight: 2800-3000
- CAS Name: Castor oil, polymer with tetrahydromethyl-1,3-isobenzofurandione
- Description: Very viscous amber liquid
- Test substance storage: At room temperature in the dark under nitrogen
- Stebility under storage conditions: Stable
- Expiry date: 01 January 2009
Specific details on test material used for the study:
- Hygroscopic: yes
- Specific Gravity: 1.10 g/cc

In vivo test system

Test animals

Species:
mouse
Strain:
CBA
Sex:
female
Details on test animals and environmental conditions:
ANIMALS
- 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
- 20 females (nulliparous and non-pregnant), five females per group.
- Young adult animals (approx. 9 weeks old) were selected.
- Body weight variation was within +/- 20% of the sex mean.
- Identification: Tail mark with marker pen.
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.

HUSBANDRY
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: 20.2-24,0°C), a relative humidity of 30-70% (actual range: 43 - 95%) 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). Paper (Enviro-dri, Wm. Lillico & Son (Wonham Mill Ltd). Surrey, United Kingdom) was supplied as cage-enrichment.
The paper was removed on Day 1 prior to dosing and was supplied again after scoring of the ears on Day 3.
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).
Diet: Free access to pelleted rodent diet (SM R/M-Z Irom SSNIFF® Spezialdia1:en GmbH, Soest, Germany).
Water: Free access to tap water.
Results of analysis lor each batch of diet (nutrients and 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:
dimethylformamide
Concentration:
0, 25, 50, 100 %
No. of animals per dose:
5
Details on study design:
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 (Dimethyl formamide).
Three days after the last exposure, all animals were injected with 3H-methyl thymidine and after five hours the draining (auricular) Iymph nodes were excised.
After precipitating the DNA of the Iymph node cells, radioaetivity measurements were performed. The activity was expressed as the number of Disinregrations Per Minute (DPM) and a stimulation index (SI) was subsequently calculated lor each group.
Positive control substance(s):
hexyl cinnamic aldehyde (CAS No 101-86-0)

Results and discussion

Positive control results:
The six monthly reliability check with Hexylcinnamaldehyde, indicates that the Local Lymph Node Assay as performed at NOTOX is an appropriate model for testing for contact hypersensitivity. An EC3 value of 13.8 % was calculated using linear interpolation. The calculated EC3 value was found to be in the acceptable range of 2 and 20%.

In vivo (LLNA)

Resultsopen allclose all
Key result
Parameter:
SI
Value:
7.2
Test group / Remarks:
25%
Key result
Parameter:
SI
Value:
11.8
Test group / Remarks:
50%
Key result
Parameter:
SI
Value:
13.3
Test group / Remarks:
100%
Parameter:
other: Mean DPM/animal
Value:
4 029
Test group / Remarks:
25%
Parameter:
other: Mean DPM/animal
Value:
6 576
Test group / Remarks:
50%
Parameter:
other: Mean DPM/animal
Value:
7 413
Test group / Remarks:
100%
Parameter:
other: Mean DPM/animal
Value:
557
Test group / Remarks:
vehicle control

Any other information on results incl. tables

Skin reactions / Irritation:

No irritation of the ears was seen in the control group and the 25% test substance treated group. The slight irritation of the ears as shown by the animals of the 50 and 100% treated groups was considered not to have a toxicologically significant effect on the activity of the nodes.

Macroscopy of the auricular lymph nodes and surrounding area:

All nodes of the experimental animals treated at 25% and control group were considered normal in size. Enlarged nodes were found in the groups treated at 50 and 100%. No macroscopic abnormalities of the surrounding area were noted.

Body weights:

The slight body weight loss, noted in some experimental animals, was considered not toxicologically significant.

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 1 (skin sensitising) based on GHS criteria
Conclusions:
The SI values calculated for the substance concentrations 25, 50 and 100% were 7.2, 11.8 and 13.3 respectively.
These results indicate that the test substance could elicit a SI >= 3. No reliable EC3 value could be calculated. It would have been possible to strengthen the outcome of the study by adding lower concentrations. Since the SI values clearly exceeded 3 and since extension of the study would not alter the classification, this was considered not appropriate for ethical reasons.
The six monthly reliability check with Hexylcinnamaldehyde, indicates that the Local Lymph Node Assay as performed at NOTOX is an appropriate model for testing for contact hypersensitivity.
Based on these results:
- according to the recommendations made in the test guidelines, the Substance would be regarded as skin sensitizer.
- according to the Globally Harmonized System of Classification and Labeling of Chemicals (GHS) of the United Nations (2007), the Substance should be classified as skin sensitizer (Category 1).
Executive summary:

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 (Dimethyl formamide).

Three days after the last exposure, all animals were injected with 3H-methyl thymidine and after five hours the draining (auricular) lymph nodes were excised.

After precipitating the DNA of the lymph node cells, 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.

No irritation of the ears was seen in the control group and the 25% test substance treated group. The slight irritation of the ears as shown by the animals of the 50 and 100% treated groups was considered not to have a toxicologically significant effect on the activity of the

nodes.

All nodes of the experimental animals treated at 25% and control group were considered normal in size. Enlarged nodes were found in the groups treated at 50 and 100%.

The slight body weight loss, noted in some experimental animals, was considered not toxicologically significant.

Mean DPM/animal values for the experimental groups treated with test substance concentrations 25, 50 and 100% were 4029, 6576 and 7413 respectively. The mean DPM/animal value for the vehicle control group was 557.

The SI values calculated for the substance concentrations 25, 50 and 100% were 7.2, 11.8 and 13.3 respectively. These results indicate that the test substance could elicit a SI >= 3. No reliable EC3 value could be calculated. It would have been possible to strengthen the outcome of the study by adding lower concentrations. Since the SI values clearly exceeded 3 and since extension of the study would not alter the classification, this was considered not appropriate for ethical reasons.