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EC number: 201-783-3 | CAS number: 87-91-2
- 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
Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From July 01 to August 12, 2015
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP study conducted in compliance with OECD Guideline No. 429 without any deviation.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 015
- Report date:
- 2015
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- inspected on July 13-16, 2015 / signed on September 14, 2015
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- Diethyl tartrate
- EC Number:
- 201-783-3
- EC Name:
- Diethyl tartrate
- Cas Number:
- 87-91-2
- Molecular formula:
- C8H14O6
- IUPAC Name:
- diethyl tartrate
- Test material form:
- other: liquid
- Details on test material:
- - Name of test material (as cited in study report): Tartrate diethyle
- Physical state: Incolor liquid
- Storage condition of test material: At room temperature in the dark
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- other: CBA/CaOlaHsd
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Envigo RMS B.V., Inc. Postbus 6174 5960 AD Horst / The Netherlands.
- Age at study initiation: Pre-test and main study: 9-10 weeks
- Weight at study initiation: 20.2 ± 0.6 g
- Housing: Animals were group housed in Makrolon Type II (pre-test) / III (main study), with wire mesh top
- Diet: 2018C Teklad Global 18% protein rodent diet (certified), ad libitum
- Water: Tap water, ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 22 ± 2 °C
- Humidity: 45-65%
- Air changes: at least 8 to 10 air changes per hour
- Photoperiod: 12 h dark / 12 h light
IN-LIFE DATES: From July 01 to August 12, 2015
Study design: in vivo (LLNA)
- Vehicle:
- dimethylformamide
- Concentration:
- Main test: 25, 50 and 100 % in dimethylformamide
- No. of animals per dose:
- 5
- Details on study design:
- RANGE FINDING TESTS:
- Two mice were treated by (epidermal) topical application to the dorsal surface of each ear with test item concentrations of 50 and 100% once daily each on three consecutive days. Prior to the first application of the test item and before sacrifice the body weight was determined. Clinical signs were recorded at least once daily. Eventual signs of local irritation were documented and a score was used to grade a possible erythema of the ear skin. Furthermore, prior to the first application of the test item (day 1), on day 3 and before sacrifice (day 6) the ear thickness was determined using a micrometer. Additionally, for both animals, the ears were punched after sacrifice (day 6) at the apical area using a biopsy punch (Ø 8 mm corresponding to 0.5 cm2) and were immediately pooled per animal and weighed using an analytical balance. Eventual ear irritation was considered to be excessive if an erythema of the ear skin of a score value ≥3 was observed at any observation time and/or if an increase in ear thickness of ≥25% was recorded on day 3 or day 6.
At the tested concentrations the animals did not show any signs of systemic toxicity (including a >5% reduction in bodyweight from Day 1 to Day 6) or local skin irritation. Maximum increases in ear thickness in the preliminary screening were 6.4 and 7.5% in the two animals treated with 50 and 100%, respectively.
Thus, the test item in the main study was assayed at 25, 50, and 100%. The highest concentration tested was the highest level that could be achieved whilst avoiding systemic toxicity and excessive local skin irritation as confirmed in the pre-experiment.
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Name of test method: LLNA
- Criteria used to consider a positive response: The test item will be regarded as a sensitiser if at least one concentration of the test item results in a threefold or greater increase in 3HTdR incorporation compared to control values. Any test item failing to produce a threefold or greater increase in 3HTdR incorporation will be classified as a ‘non-sensitiser’.
TREATMENT PREPARATION AND ADMINISTRATION: The highest test item concentration which can be technically used was the undiluted test item. Test item solutions at different concentrations were prepared using DMF as vehicle. The preparations were made freshly before each dosing occasion.
- Each test group of five mice was treated by (epidermal) topical application to the dorsal surface of each ear with test item concentrations of 25, 50, and 100% in acetone/olive oil (4+1, v/v). The application volume, 25 μL/ear/day, was spread over the entire dorsal surface (∅ ∼ 8 mm) of each ear with a micropipette, using the tip of the pipette. Treatment was conducted once daily for three consecutive days (Days 1, 2, and 3). A further group of five mice (control animals) was treated in the same manner with an equivalent volume of the relevant vehicle alone (control animals). Five days after the first topical application (Day 6) 250 μL of phosphate-buffered saline containing 19.7 μCi of 3H-methyl thymidine (equivalent to 79.0 μCi/mL 3HTdR) were injected into each test and control mouse via the tail vein. Approximately five hours after treatment with 3HTdR all mice were euthanised by using CO2, which was, after harvesting of the lymph nodes, followed by cervical dislocation to ensure death. The draining lymph nodes were rapidly excised and pooled for each individual animal (2 nodes per animal). For each individual animal, single cell suspensions (in phosphate buffered saline) of pooled lymph node cells were prepared by gentle mechanical disaggregation through stainless steel gauze (200 μm mesh size). After washing two times with phosphate buffered saline (approx. 10 mL) the lymph node cells were resuspended in 5 % trichloroacetic acid (approx. 3 mL) and incubated at approximately +4 °C for at least 18 hours for precipitation of macromolecules. The precipitates were then resuspended in 5 % trichloroacetic acid (1 mL) and transferred to scintillation vials with 10 mL of scintillation liquid and thoroughly mixed, preferably in darkness. The level of 3HTdR incorporation was then measured in a β-scintillation counter. Similarly, background 3HTdR levels were also measured in two 1 mL-aliquots of 5 % trichloroacetic acid. The β-scintillation counter expresses 3HTdR incorporation as the number of radioactive disintegrations per minute.
- The proliferation response of lymph node cells was expressed as the number of radioactive disintegrations per minute per animal and as the ratio of 3HTdR incorporation into lymph node cells of test nodes relative to that recorded for the control nodes (Stimulation Index). - 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 and for the DPM values (group mean DPM ± standard deviation).
The Dean-Dixon-Test and the Grubb’s test were used for identification of possible outliers (performed with validated program R Script Outlier.Rnw). An outlier (DPM value determined for animal 10) was detected in both outlier tests. However, as exclusion of the outlier value would have no impact on the study result, the value in question was not excluded from calculation.
Results and discussion
- Positive control results:
- The sensitivity and reliability of the experimental technique employed was assessed by use of α-hexyl cinnamaldehyde dissolved in acetone/olive oil (4+1, v/v) (compound listed in OECD 429 Guideline) which is known to have skin sensitisation properties in mice. SI for the positive control substance 25% hexyl cinnamic aldehyde (HCA), was 9.48 which demonstrates the validity of this study.
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Remarks on result:
- other: Stimulation index for vehicle, 25, 50 and 100 % were 1.00, 1.03, 0.70 and 0.97, respectively.
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: Mean DPM per animal for vehicle, 25, 50 and 100 % were 1307.6 ± 299.3, 1345.8 ± 928.2, 910.6 ± 92.9 and 1271.6 ± 417.4, respectively.
Any other information on results incl. tables
Table 7.4.1/1: Calculation of Stimulation Indices per Dose Group
Test item concentration
|
Group Calculation
|
Result |
||
Mean DPM per animal (2 lymph nodes)a)
|
SD |
S.I |
||
Vehicle Control Group (DMF)
|
1307.6 |
299.3 |
1.00 |
- |
25% |
1345.8 |
928.2 |
1.03 |
Negative |
50% |
910.6 |
92.9 |
0.70 |
Negative |
100% |
1271.6 |
417.4 |
0.97 |
Negative |
a)Mean DPM/animal was determined by dividing the sum of the measured values from lymph nodes of all animals within a group by the number of animals in that group (5 animals)
The EC3 value could not be calculated, since all S.I.´s are below the threshold value of 3.
Viability / Mortality: No deaths occurred during the study period.
Clinical Signs: No symptoms of local skin irritation at the ears of the animals and no signs of systemic toxicity were observed during the study period.
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.
Body weight change of the test animals between Day 1 and Day 6 were comparable to that observed in the corresponding control group animals over the same period.Applicant's summary and conclusion
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- Under the test conditions, test material is not classified as a skin sensitiser according to the annex VI of the Regulation EC No. 1272/2008 (CLP) and of the Directive 67/548/EEC.
- Executive summary:
A study was performed to assess the skin sensitisation potential of test material in the CBA/CaOlaHsd strain mouse following topical application to the dorsal surface of the ear. The method was conducted according to the OECD test guideline No 429 and in compliance with GLP.
Following a preliminary screening test in two animals in which no clinical signs of systemic toxicity or excessive local skin irritation were noted at a concentration of 50 and 100%, the latest concentration was selected as the highest dose investigated in the main test of the Local Lymph Node Assay. Maximum increases in ear thickness in the preliminary screening were 6.4 and 7.5% in the two animals treated with 50 and 100%, respectively. Therefore this local lymph node assay was performed using test item concentrations of 25, 50, and 100% in groups of five animals each. A further group of animals was treated with the vehicle DMF alone.
The animals did not show any signs of systemic toxicity or local skin irritation during the course of the study and no cases of mortality were observed.
Mean DPM per animal for vehicle, 25, 50 and 100 were 1307.6 ± 299.3, 1345.8 ± 928.2, 910.6 ± 92.9 and 1271.6 ± 417.4, respectively. In this study Stimulation Indices (S.I.) of 1.03, 0.70 and 0.97 were determined with the test item at concentrations of 25 and 50% in DMF and 100% of the undiluted test item, respectively.
SI for the positive control substance 25% hexyl cinnamic aldehyde (HCA), was 9.48 which demonstrates the validity of this study.
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