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EC number: 807-560-2 | CAS number: 123944-63-8
- 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:
- 7 February 2005 to 9 March 2005
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted to GLP in accordance with generally accepted scientific principles, possibly with incomplete reporting or methodological deficiencies, which do not affect the quality of the relevant results.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 005
- Report date:
- 2005
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
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- 1,4-bis({3-[2-(2-hydroxyethoxy)ethoxy]propyl}amino)-9,10-dihydroanthracene-9,10-dione
- EC Number:
- 807-560-2
- Cas Number:
- 123944-63-8
- Molecular formula:
- C28H38N2O8
- IUPAC Name:
- 1,4-bis({3-[2-(2-hydroxyethoxy)ethoxy]propyl}amino)-9,10-dihydroanthracene-9,10-dione
- Test material form:
- other: opaque liquid
- Details on test material:
- - Appearance: Blue opaque liquid
- Storage conditions: Room temperature in the dark
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Strain: CBA/Ca (CBA/CaBkl)
- Age at study initiation: 8 to 12 weeks
- Weight at study initiation: 15 to 23 g
- Housing: The animals were individually housed in suspended solid-floor polypropylene cages furnished with softwood woodflakes
- Diet: ad libitum access to Certified Rat and Mouse Diet
- Water: ad libitum access to mains tap water
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 19 to 25 °C
- Humidity: 30 to 70 % (relative)
- Air changes: approximately 15 per hour
- Photoperiod (hrs dark / hrs light): the lighting was controlled by a time switch to give twelve hours continuous light (06:00 to 18:00) and twelve hours darkness.
IN-LIFE DATES: No data
Study design: in vivo (LLNA)
- Vehicle:
- other: The test material was administered undiluted and in dimethyl formamide
- Concentration:
- The test material was administered undiluted and at concentrations of 25 and 50 % v/v in dimethyl formamide.
- No. of animals per dose:
- 5 females per dose level
- Details on study design:
- PRELIMINARY SCREENING TEST
As no toxicological information was available regarding the systemic toxicity/irritancy potential of the test material a preliminary screening test was performed using one mouse. The mouse was treated by daily application of 25 µL of the undiluted test material to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The mouse was observed twice daily on Days 1, 2 and 3 and once daily on Days 4, 5 and 6. Any signs of toxicity or excessive local irritation noted during this period were recorded. The bodyweight of the mouse was recorded on Day 1 (prior to dosing) and on Day 6.
No signs of systemic toxicity were noted. Staining of the ears and fur was noted one hour post dosing on Day 1 and for the remainder of the test. Based on this information the dose levels selected for the main test were 25 and 50 % v/v in dimethyl formamide and 100 % (undiluted test material).
MAIN TEST
- Test Material Administration
The mice were treated by daily application of 25 µL of the appropriate concentration of the test material to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The test material formulation was administered using an automatic micropipette and spread over the dorsal surface of the ear using the tip of the pipette. A further group of five mice received the vehicle alone in the same manner.
- 3H-Methyl Thymidine Administration
Five days following the first topical application of the test material (Day 6) all mice were injected via the tail vein with 250 µL of phosphate buffered saline (PBS) containing 3H-methyl thymidine (3HTdR: 80 µCi/mL, specific activity 2.0 Ci/mmol) giving a total of 20 µCi to each mouse.
- Observations
Clinical Observations: All animals were observed twice daily on Days 1, 2 and 3 and on a daily basis on Days 4, 5 and 6. Any signs of toxicity or signs of ill health during the study were recorded.
Bodyweights: The bodyweight of each mouse was recorded on Day 1 (prior to dosing) and Day 6 (prior to termination).
- Terminal Procedures
Termination
Five hours following the administration of 3HTdR, all mice were killed by carbon dioxide asphyxiation. For each individual animal of each group the draining auricular lymph nodes were excised and processed. For each individual animal 1 mL of PBS was added to the lymph nodes.
Preparation of Single Cell Suspension
A single cell suspension of the lymph node cells for each individual animal was prepared by gentle mechanical disaggregation through a 200-mesh stainless steel gauze. The lymph node cells were rinsed through the gauze with 4 mL of PBS into a petri dish. The lymph node cells suspension was transferred to a 10 mL centrifuge tube. The petri dish was washed with an additional 5 mL of PBS to remove all remaining lymph node cells and these were added to the centrifuge tube. The lymph node cells were pelleted at 1400 rpm (approximately 190 g) for ten minutes. The pellet was re-suspended in 10 mL of PBS and re-pelleted. To precipitate out the radioactive material, the pellet was re-suspended in 3 mL of 5 % trichloroacetic acid (TCA).
Determination of 3HTdR incorporation
After overnight incubation at 4 °C, the precipitates were recovered by centrifugation at 2100 rpm (approximately 450 g) for ten minutes, re-suspended in 1 mL of TCA and transferred to 10 mL of scintillation fluid (Optiphase 'Trisafe'). 3HTdR incorporation was measured by β-scintillation counting. The "Poly Q" vials containing the samples and scintillation fluid were placed in the sample changer of the scintillator and left for approximately twenty minutes. The purpose of this period of time in darkness was to reduce the risk of luminescence, which has been shown to affect the reliability of the results. After approximately twenty minutes, the vials were shaken vigorously. The number of radioactive disintegrations per minute was then measured using the Beckman LS6500 scintillation system (Beckman Instruments Inc., Fullerton, CA). - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- Data was processed to give group mean values for dpm and standard deviations where appropriate. Individual and group mean dpm values were assessed for dose response relationships by analysis of homogeneity of variance followed by one way analysis of variance (ANOVA). In the event of a significant result from the ANOVA, pairwise comparisons were performed between control and treated groups. For homogenous datasets, Dunnett's Multiple Comparison test was used and for non-homogenous datasets Dunnett's T3 Multiple Comparison Method was used.
Results and discussion
- Positive control results:
- Three groups of five animals were treated with 50 µL (25 µL per ear) of α-hexylcinnamaldehyde as a solution in acetone/olive oil 4:1 at concentrations of 5, 10 and 25 % v/v. A further control group of five animals was treated with acetone/olive oil 4:1 alone.
The Stimulation Index (SI) expressed as the mean radioactive incorporation for each treatment group divided by the mean radioactive incorporation of the vehicle control group was 1.40, 2.23 and 6.09 for the 5, 10 and 25 % v/v dose groups, respectively. The value of 6.09 is considered to be a positive reaction in this test and therefore α-hexylcinnamaldehyde was considered to be a sensitiser under the conditions of the test.
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Remarks on result:
- other: The stimulation index (SI) for each dose group is given in Table 1. A stimulation index of less than 3 was recorded for the three concentrations of the test material (25 and 50 % v/v in dimethyl formamide and 100 %).
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: The radioactive disintegrations per minute (dpm) per lymph nodes for each individual animal are given in Table 1.
Any other information on results incl. tables
There were no deaths. No signs of systemic toxicity were noted in the test or control animals during the test. Staining of the ears and fur was noted in all test animals one hour post dosing on Day 1 and for the remainder of the test.
Body weight changes of the test animals between Day 1 and Day 6 were comparable to those observed in the corresponding control group animals over the same period.
Table 1: Individual dpm’s and the Group Stimulation Indices
Concentration (% v/v) in DMF |
Animal Number |
dpm/Animal* |
Mean dpm / Animal (± SD) |
Stimulation Index |
Result |
Vehicle |
1-1 |
735.47 |
792.28 ± 186.54 |
N/A |
N/A |
1-2 |
815.97 |
||||
1-3 |
1093.83 |
||||
1-4 |
722.99 |
||||
1-5 |
593.12 |
||||
25 |
2-1 |
686.35 |
1117.26 ± 307.51 |
1.41 |
Negative |
2-2 |
1326.38 |
||||
2-3 |
920.22 |
||||
2-4 |
1221.06 |
||||
2-5 |
1432.27 |
||||
50 |
3-1 |
1002.21 |
997.71 ± 257.08 |
1.26 |
Negative |
3-2 |
1249.93 |
||||
3-3 |
1256.64 |
||||
3-4 |
758.99 |
||||
3-5 |
720.78 |
||||
100 |
4-1 |
743.98 |
108.64 ± 305.01 |
1.36 |
Negative |
4-2 |
1055.03 |
||||
4-3 |
1297.37 |
||||
4-4 |
836.74 |
||||
4-5 |
1470.10 |
*Total number of lymph nodes per animal is 2
DMF = dimethyl formamide
SD = standard deviation
Applicant's summary and conclusion
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- Under the conditions of this study, the test material was considered to be a non-sensitiser.
- Executive summary:
A study was performed to assess the skin sensitisation potential of the test material in accordance with the standardised guidelines OECD 429 and EU Method B.42 under GLP conditions.
The assessment was carried out in the CBA/Ca strain mouse following topical application to the dorsal surface of the ear. Following a preliminary screening test, three groups of five animals were treated with 50 µL (25 µL per ear) of the undiluted test material or the test material as a solution in dimethyl formamide at concentrations of 25 and 50 % v/v. A further group of five animals was treated with dimethyl formamide alone.
The Stimulation Index (SI) expressed as the mean radioactive incorporation for each treatment group was 1.41, 1.26 and 1.36 for the 25, 50 and 100 % dose groups, respectively.
There were no deaths. No signs of systemic toxicity were noted in the test or control animals during the test. Body weight changes of the test animals between Day 1 and Day 6 were comparable to those observed in the corresponding control group animals over the same period.
Under the conditions of this study, the test material was considered to be a non-sensitiser.
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