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EC number: 223-437-0 | CAS number: 3891-33-6
- 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
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:
- 2015-05-30 to 2015-05-05
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP and guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- 2010
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- 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: Envigo Laboratories B.V. Postbus 6174 5960 AD Horst / The Netherlands
- Age at study initiation: Pre-test: 9 - 10 weeks Main study: 8 - 9 weeks
- Weight at study initiation: 17.8-20.9 g
- Housing: grouped by test groups, Makrolon Type II (pre-test) / III (main study), with wire mesh top
- Diet: ad libitum 2018C Teklad Global 18 % protein rodent diet
- Water: ad libitum tap water
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 2
- Humidity (%): 45-65
- Photoperiod (hrs dark / hrs light): 12/12 - Vehicle:
- dimethylformamide
- Concentration:
- 25, 50, 100 %
- No. of animals per dose:
- 5
- Details on study design:
- RANGE FINDING TESTS:
- Compound solubility: experiment was performed according to the recommendations given by OECD 429
- Irritation: 2 animals treated with 50 and 100 % on 3 consecutive days
- Lymph node proliferation response: no
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Name of test method: LLNA
- Criteria used to consider a positive response: a) exposure to at least one concentration of the test item resulted in an incorporation of 3HTdR at least 3-fold or greater than that recorded in control mice, as indicated by the Stimulation Index b) data are compatible with a conventional dose response, although allowance must be made (especially at high topical concentrations) for either local toxicity or immunological suppression.
TREATMENT PREPARATION AND ADMINISTRATION:
- Animals were treated topically on the dorsal surface of each ear (25 μL/ear/day) on 3 consecutive days
- 5 days after first application 81.3 μCi/mL 3HTdR were injected
- 5 h after injection animals were sacrificed - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- The mean values and standard deviations were calculated in the body weight tables, for the ear weights, the lymph node weights and lymph node cell count, and for the DPM values (group mean DPM ± standard deviation).
Where appropriate, the EC3 value was calculated according to the equation
EC3 = (a-c) [(3-d)/(b-d)] + c
where EC3 is the estimated concentration of the test item required to produce a 3-fold increase in draining lymph node cell proliferative activity; (a, b) and (c, d) are respectively the co-ordinates of the two pair of data lying immediately above and below the S.I. value of 3 on the local lymph node assay dose response plot.
A statistical analysis was conducted on the DPM values, the ear weights, the lymph node weights and the lymph node cell count to assess whether the difference was statistically significant between the test item groups and negative control group. For all statistical calculations validated statistical program R Script DecisionTree_2.Rnw was used. Statistical significance was set at the five per cent level (p < 0.05).
The Dean-Dixon-Test and the Grubb’s test were used for detection of possible outliers (performed with validated statistical program R Script Outlier.Rnw).
However, both biological and statistical significance were considered together. - Parameter:
- SI
- Remarks on result:
- other: - Vehicle control: 1.0 - 25 %: 1.45 - 50 %: 2.06 - 100 %: 6.49
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: Mean DPM per animal (2 lymph nodes) - Vehicle control: 1716.3 ± 358.7 - 25 %: 2481.9 ± 967.9 - 50 %: 3528.1 ± 1020.7 - 100 %: 11131.3 ± 7052.4
- Interpretation of results:
- Category 1 (skin sensitising) based on GHS criteria
- Remarks:
- Migrated information
- Conclusions:
- The test item 1,4-Butanediol Divinyl Ether was found to be a skin sensitizer and an EC3 value of 60.6% (w/w) was derived.
Reference
Viability / Mortality
No deaths occurred during the study period.
Clinical Signs
No signs of systemic toxicity were observed during the study period. From day 2 (1 hour after the second application) to day 5, the animals treated with a test item concentration of 100 % showed an erythema of the ear skin (score 1). Additionally the animals treated with the undiluted test item transiently showed reduced spontaneous activity on day 2 and burrowed themselves in the bedding (1 hour after the second application). Animals treated with 25 and 50 % test item concentration did not show any signs of local skin irritation or symptoms of toxicity.
Body Weights
The body weight of the animals, recorded prior to the first application and prior to treatment with 3HTdR, was within the range commonly recorded for animals of this strain and age.
Lymph Node Weights and Cell Counts
A statistically significant increase in lymph node cell counts was observed in the mid and high dose group in comparison to the vehicle control group. Additionally, a statistically significant increase in lymph node weight was observed in the high dose group in comparison to the vehicle control group. For BALB/c mice, a cut-off value for the lymph node cell count index of 1.55 was reported for a positive response. The indices determined for the lymph node cell exceeded this threshold in the mid and high dose group (index of 1.75 and 2.65, respectively).
Ear Weights
The measured ear weight of all animals treated was recorded on test day 6 (after necropsy). A biologically relevant or statistically significant increase in ear weights was not observed. Furthermore, the cut-off value (1.1) of the ear weight index for a positive response regarding ear skin irritation reported for BALB/c mice was not reached or exceeded in any of the treated groups.
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed (sensitising)
- Additional information:
1,4-Butanediol Divinyl Ether was assessed for its skin sensitising potential using the Local Lymph Node Assay (LLNA) in mice. Test item concentrations of 25, 50% and 100% (w/w) were used. No cases of mortality were observed. From day 2 (1 hour after the second application) to day 5, the animals treated with a test item concentration of 100% showed a very slight erythema of the ear skin (score 1). Additionally the animals treated with the undiluted test item transiently showed reduced spontaneous activity on day 2 (1 hour after the second application) and burrowed themselves in the bedding. Animals treated with 25 and 50% test item concentration did not show any signs of local skin irritation nor symptoms of toxicity. As the clinical signs observed in the high dose group were only noted temporarily and all animals gained body weight during the study, they were considered to be not biologically relevant. In this study Stimulation Indices (S.I.) of 1.45, 2.06, and 6.49 were determined with the test item at concentrations of 25 and 50% (w/w), and 100% (undiluted test item) in DMF, respectively. The test item 1,4-Butanediol Divinyl Ether was found to be a skin sensitizer and an EC3 value of 60.6% (w/w) was derived.
Migrated from Short description of key information:
1,4-Butanediol Divinyl Ether was found to be a skin sensitizer and an EC3 value of 60.6% (w/w) was derived.
Justification for selection of skin sensitisation endpoint:
GLP key study
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
Skin sensitisation
Dangerous Substance Directive
(67/548/EEC)
The available studies are considered reliable and suitable for
classification purposes under Directive 67/548/EEC. As a result the
substance has to be classified for skin sensitisation (R43) under
Directive 67/548/EEC, as amended for the 31st time in Directive
2009/2/EG.
Classification, Labelling, and Packaging Regulation (EC) No 1272/2008
The available studies are considered reliable and suitable for classification purposes under Classification, Labelling, and Packaging Regulation (EC) No 1272/2008. As a result the substance has to be classified for skin sensitisation (H317).
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