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EC number: 202-338-6 | CAS number: 94-49-5
- 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
Endpoint summary
Administrative data
Description of key information
When tested up to and including 25%, Ethylene glycol dibenzoate did not elicit an SI ≥ 3 and was therefore not considered to be a skin sensitizer. It was established that the EC3 value exceeds 25%. The test substance is not classified for skin sensitising properties.
Key value for chemical safety assessment
Skin sensitisation
Link to relevant study records
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 01 April 2017 - 02 May 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- in vivo required for non-EU registration
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- July 2010
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- May 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.2600 (Skin Sensitisation)
- Version / remarks:
- March 2003
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- dd. 03 Nov 2015
- Type of study:
- mouse local lymph node assay (LLNA)
- Specific details on test material used for the study:
- Solubility in vehicle: not indicated
Stability in vehicle: not indicated - Species:
- mouse
- Strain:
- CBA:J
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Charles River France, L’Arbresle, France
- Females nulliparous and non-pregnant: yes
- Age at study initiation: approx 9 weeks old
- Weight at study initiation: 16.6 to 23.4 g
- Housing: 5 animals together in polycarbonate cages
- Diet: pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest, Germany), ad libitum
- Water: tap-water, ad libitum
- Acclimation period: 5 days
- Indication of any skin lesions: no; animals were checked before initiation of dosing and any animals considered unsuitable for use in the study were replaced.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21 to 22
- Humidity (%): 42 to 47
- Air changes (per hr): 10
- Photoperiod (hrs dark / hrs light): 12/12
- IN-LIFE DATES: From: 26 April to 01 May 2017 - Vehicle:
- acetone/olive oil (4:1 v/v)
- No. of animals per dose:
- 5
- Details on study design:
- PRE-SCREEN TESTS:
- Concentrations: 25% and 50%
- Systemic toxicity: no signs at 25%; hunched posture in both animals on days 2 and 3 and slight erythema in one animal on day 2.
- Ear thickness measurements: on day 1 and 3 (prior to dosing) and on day 6, using a digital thickness gauge. Variations in ear thickness during the observation period were less than 25% from Day 1 pre-dose values.
MAIN STUDY: Three groups of five animals were treated with one test item concentration per group (5, 10 and 25%). The highest test item concentration was selected from the pre-screen test. One group of five animals was treated with the vehicle.
ANIMAL ASSIGNMENT AND TREATMENT
- Criteria used to consider a positive response: if the results indicate a SI ≥ 3, the test item may be regarded as a skin sensitizer.
TREATMENT PREPARATION AND ADMINISTRATION:
- Induction (days 1, 2 and 3): both ears were topically treated with 25 μL test item per ear.
- Excision of the nodes (day 6): each animal was injected via the tail vein with 0.25 mL of sterile phosphate buffered saline containing 20 μCi of 3H-methyl thymidine
- 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 (maze size: 200 μm, diameter: ± 1.5 cm). LNC were washed twice with an excess of PBS by centrifugation at 200g for 10 minutes at 4ºC. To precipitate the DNA, the LNC were exposed to 5% trichloroacetic acid (TCA) (Merck, Darmstadt, Germany) and then 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. Radioactivity 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).
ANALYSIS:
DPM values were calculated for each animal and for each dose group. A Stimulation Index (SI) was calculated for each group using the individual SI values. The individual SI is the ratio of the DPM/animal compared to the DPM/vehicle control group mean.
If the results indicate a SI ≥ 3, the test item may be regarded as a skin sensitizer. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Positive control results:
- The six-month reliability check with Alpha-hexylcinnamaldehyde indicates that the Local Lymph Node Assay as performed at the testing facility is an appropriate model for testing for contact hypersensitivity
- Key result
- Parameter:
- SI
- Value:
- 1.7
- Test group / Remarks:
- 5% test item concentration group
- Key result
- Parameter:
- SI
- Value:
- 1
- Test group / Remarks:
- 10% test item concentration group
- Key result
- Parameter:
- SI
- Value:
- 1.5
- Test group / Remarks:
- 25% test item concentration group
- Key result
- Parameter:
- EC3
- Value:
- > 25
- Test group / Remarks:
- all treatment groups
- Cellular proliferation data / Observations:
- - No erythema was observed in any of the animals, scaliness was noted in one animal treated at 10% on Day 5 only. Test item remnants were present on the dorsal surface of the ears of all animals at 25% (between Days 2 and 4), which did not hamper scoring of the skin reactions.
- Mean DPM/animal values for the experimental groups treated with test item concentrations 5, 10 and 25% were 429, 242 and 363 DPM, respectively. The mean DPM/animal value for the vehicle control group was 250 DPM.
- 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.
- The six-month reliability check with Alpha-hexylcinnamaldehyde indicates that the Local Lymph Node Assay as performed at the test facility is an appropriate model for testing for contact hypersensitivity. - Interpretation of results:
- GHS criteria not met
- Remarks:
- Not classified according to Regulation (EC) 1272/2008
- Conclusions:
- When tested up to and including 25%, Ethylene glycol dibenzoate did not elicit an SI ≥ 3 and was therefore not considered to be a skin sensitizer. It was established that the EC3 value exceeds 25%. The test substance is not classified for skin sensitising properties according to GHS and Regulation (EC) 1272/2008.
- Endpoint:
- skin sensitisation: in vitro
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- an in vitro skin sensitisation study does not need to be conducted because adequate data from an in vivo skin sensitisation study are available
Referenceopen allclose all
Results of the pre-screen test:
At a 25% test item concentration no signs of systemic toxicity were noted and no erythema was observed. At a 50% test item concentration hunched posture was noted for both animals on Days 2 and 3 and slight erythema was noted for one of the animals on Day 2.
Test item remnants were present on the dorsal surface of the ears of all animals (between Days 1 and 6), 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 the tolerability of the test item, the highest test item concentration selected for the main study was a 25% concentration.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
- Additional information:
As chemical respiratory sensitisers also elicit positive results in predictive tests for contact sensitisation, a negative outcome for dermal sensitisation is also predictive for non respiratory sensitisation of the substance.
As indicated in REACH guidance R.7.3.5 it can be concluded that chemicals that are negative in the LLNA, as well as being considered as not being skin sensitizers, can also be regarded as lacking the potential to cause allergic sensitisation of the respiratory tract.
At present, recognised and validated animal models for the testing of respiratory hypersensitivity are not available.
Justification for classification or non-classification
Based on the outcome of the available study the substance is not classifed as a skin or respiratory sensitizer.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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