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1-ol, [[4-[(3-aminophenyl)amino]-6-chloro-1,3,5-triazin-2-yl]amino]-2-[(E)-2-ylazo]-, polysulfonate, polynaphthen, sodium salt (1:?), diazotized, reaction products with 2-[(aminophenyl)sulfonyl]ethyl hydrogen sulfate, 1-naphthalenol, 8-amino- (1:1), polysulfonates, sodium salts and 2,4,6-trihalogeno-1,3,5-triazine
EC number: - | CAS number: -
- 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:
- 2008-02-12 till 2008-03-04
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 008
- Report date:
- 2008
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (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
- Name:
- Unnamed
- Type:
- Constituent
- Details on test material:
- - Name of test material (as cited in study report): FAT 40840/A TE
- Substance type: colouring dye
- Physical state: solid, dark red powder
- Analytical purity: approx. 78.9% org. part (NA-salt), MC: 37.7%, Oligomers: 19.2%
- Lot/batch No.: ROE 358 BOP 01/07
- Expiration date of the lot/batch: June 30, 2012
- Storage condition of test material: At room temperature at about 20°C
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Harlan Netherlands, B.V. Postbus 6174, NL-5960 AD Horst/The Netherlands
- Age at study initiation: 8-9 weeks
- Weight at study initiation: 19.7 - 20.9g
- Housing: single
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: At least 5 days prior to the start of dosing under test conditions after health examination. Only animals without any visible signs of illness were used for the study.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 +/- 3°C
- Humidity (%): 30-70%
- Photoperiod (hrs dark / hrs light): 6.00 a..m. - 6.00 p.m.
Study design: in vivo (LLNA)
- Vehicle:
- other: Ethanol:deionised water, 30+70
- Concentration:
- 30:70
- No. of animals per dose:
- 4
- Details on study design:
- RANGE FINDING TESTS:
- Compound solubility: A solubility experiment was performed according to the recommendations given by OECD 429. The highest test item concentration, which can be technically used was a 20 % solution in ethanol:deionised water (30+70).
To determine the highest non-irritant test concentration, a pre-test was performed in two
animals. Two mice were treated with concentrations of 2.5, 5, 10, and 20 % on one ear
each on three consecutive days. Clinical signs were recorded 24 ± 4 hours after each
application. At the tested concentrations the animals did not show any signs of irritation or
systemic toxicity.
The test item in the main study was assayed at 5, 10, and 20%. The top dose is the
highest technically achievable concentration whilst avoiding systemic toxicity and
excessive local irritation. No severe irritant effects were tolerated choosing the test
concentrations.
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Name of test method:OECD Guidelines for Testing of Chemicals, Updated Guideline 429: Skin Sensitisation:
Local Lymph Node Assay (adopted 24 April 2002).
- Criteria used to consider a positive response:A test item is regarded as a sensitiser in the LLNA if the following criteria are fulfilled:
- First, that 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.
- Second, that the 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.
Results and discussion
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Remarks on result:
- other: concentration: S.I. 5 1.31 10 1.65 20 1.53
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: concentrations: Measurement DPM: control: 3715 5: 4858 10: 6101 20: 5671
Any other information on results incl. tables
Viability/Mortality:
No deaths occurred during the study period.
Clinical Signs:
The animals did not show any clinical signs during the course of the study and no cases of mortality were observed.
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.
Calculation and results of individual data
Test Item concentration % (w/v) | Group | Measurement DPM | Calculation | Result | ||
DPM-BG a) | number of lymph nodes | DPM per lymph node b) | S.I. | |||
--- | BG I | 21 | --- | --- | --- | --- |
--- | BG II | 26 | --- | --- | --- | --- |
--- | 1 | 3715 | 3692 | 8 | 461.4 | |
5 | 2 | 4858 | 4835 | 8 | 604.3 | 1.31 |
10 | 3 | 6101 | 6078 | 8 | 759.7 | 1.65 |
20 | 4 | 5671 | 5648 | 8 | 705.9 | 1.53 |
BG = Background (1 ml 5% trichloroacetic acid) in duplicate
1 = Control Group
2-4 = Test Group S.I. = Stimulation Index
a) = The mean value was taken from the figures BG I and BG II
b) = Since the lymph nodes of the animals of a dose group were pooled, DPM/node was determined by dividing the measured value by the number of lymph nodes pooled
The EC3 value could not be calculated, since all S.I.´s are below 3.
Applicant's summary and conclusion
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information
- Conclusions:
- The test item FAT 40840/A TE was found to be not a skin sensitiser under the described conditions.
- Executive summary:
The animals did not show any clinical signs during the course of the study and no cases of mortality were observed. A test item is regarded as a sensitiser in the LLNA if the exposure to one or more test concentration resulted in 3-fold or greater increase in incorporation of 3HTdR compared with concurrent controls, as indicated by the Stimulation Index (S.I.). The estimated concentration of test item required to produce a S.I. of 3 is referred to as the EC3 value. In this study Stimulation Indices of 1.31, 1.65 and 1.53 were determined with the test item at concentrations of 5, 10, and 20% in ethanol:deionised water (30+70). The EC3 value could not be calculated, since none of the tested concentrations induced an S.I. greater than 3.
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