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EC number: 201-539-6 | CAS number: 84-54-8
- 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
Endpoint summary
Administrative data
Description of key information
No skin sensitization effects were observed in test group or control group. Therefore, the test chemical was considered to be not sensitizing to human skin.
Key value for chemical safety assessment
Skin sensitisation
Link to relevant study records
- Endpoint:
- skin sensitisation: in vivo (non-LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- Data is from publication.
- Qualifier:
- according to guideline
- Guideline:
- other: As mention below
- Principles of method if other than guideline:
- Patch test wawsperfromed to evaluate the sensitization potential of the test chemical among workers working in a furniture factory
- GLP compliance:
- not specified
- Type of study:
- patch test
- Justification for non-LLNA method:
- Not specified.
- Species:
- other: Human
- Strain:
- other:
- Remarks:
- Not applicable
- Sex:
- not specified
- Details on test animals and environmental conditions:
- Details on test animal
TEST ANIMALS
72 furniture factory workers were investigated with the history of allergic contact eczema caused by true teak (Tectona grandis). All the 72 workers were interviewed and examined for skin lesions. - Route:
- epicutaneous, occlusive
- Vehicle:
- not specified
- Concentration / amount:
- Native teak dust was applied which contain unknown concentration of 2-methyl-9,10-anthraquinone.
- Day(s)/duration:
- 24 hour
- Adequacy of induction:
- not specified
- No.:
- #1
- Route:
- epicutaneous, occlusive
- Vehicle:
- other: Acetone
- Concentration / amount:
- 0.1,0.5, 1 and 2%
- Day(s)/duration:
- 24 hour
- Adequacy of challenge:
- not specified
- No. of animals per dose:
- 72 Human volunteers
- Details on study design:
- Details on study design
MAIN STUDY
A. INDUCTION EXPOSURE
- No. of exposures: single
1- Exposure period: 24 hour
- Test groups: 72
- Control group:10
- Site: The patch was applied on the volar side of the left forearm.
- Frequency of applications: No data available.
- Duration: 24 hour
- Concentrations: native teak dust was applied which contain unknown concentration of the test chemical
B. CHALLENGE EXPOSURE
- No. of exposures:4
- Day(s) of challenge: No data available.
- Exposure period: 24 hour
- Test groups:72
- Control group:10
- Site: The patch was applied on the volar side of the left forearm.
- Concentrations: 0.1,0.5, 1 and 2%
- Evaluation (hr after challenge):24 ,48 and 72 hour
Other:The interpretation of the patch testswas based on the usual criteria and was recorded as allergic, toxic, or negative. - Challenge controls:
- Yes, 10 challenge controls were investigated
- Positive control substance(s):
- not specified
- Positive control results:
- No data available.
- Key result
- Reading:
- 1st reading
- Hours after challenge:
- 24
- Group:
- test chemical
- Dose level:
- 0.1,0.5, 1 and 2%
- No. with + reactions:
- 0
- Total no. in group:
- 72
- Clinical observations:
- No skin sensitization effect were observed.
- Remarks on result:
- no indication of skin sensitisation
- Key result
- Reading:
- 1st reading
- Hours after challenge:
- 48
- Group:
- test chemical
- Dose level:
- 0.1,0.5, 1 and 2%
- No. with + reactions:
- 0
- Total no. in group:
- 72
- Clinical observations:
- No skin sensitization effect were observed.
- Remarks on result:
- no indication of skin sensitisation
- Key result
- Reading:
- 1st reading
- Hours after challenge:
- 72
- Group:
- test chemical
- Dose level:
- 0.1,0.5, 1 and 2%
- No. with + reactions:
- 0
- Total no. in group:
- 72
- Clinical observations:
- No skin sensitization effect were observed.
- Remarks on result:
- no indication of skin sensitisation
- Interpretation of results:
- other: not sensitizing
- Conclusions:
- No skin sensitization effects were observed in test group or control group. Therefore, the test chemical was considered to be not sensitizing to human skin.
- Executive summary:
Patch test was performed to evaluate the sensitization potential of the test chemical among workers working in a furniture factory
A group of 72 furniture factory workers were investigated with the history of allergic contact eczema caused by true teak (Tectona grandis). All the 72 workers were interviewed and examined for skin lesions. For this purpose a Patch test was performed with native teak dust. The patch were applied for 24 hours on the volar side of the left forearm and read at the end of this period and read again after 48 and 72 hours. A challenge exposure was performed on the workers who showed allergic reactions. The patch was applied at the concentration of 0.1, 0.5, 1 and 2% test chemical. Acetone was used as vehicle.The interpretation of the patch tests was based on the usual criteria and was recorded as allergic, toxic, or negative.Identical Patch tests were applied on 10 controls. No skin sensitization effects were observed in test group or control group. Therefore, the test chemical was considered to be not sensitizing to human skin.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
Various studies have been reviewed to determine the allergic potential of the test chemical in living organisms. These include in vivo experimental studies in humans as well as estimated data for the test chemical. The results are summarized as follows:
Patch test was performed to evaluate the sensitization potential of the test chemical among workers working in a furniture factory
A group of 72 furniture factory workers were investigated with the history of allergic contact eczema caused by true teak (Tectona grandis). All the 72 workers were interviewed and examined for skin lesions. For this purpose a Patch test was performed with native teak dust. The patch were applied for 24 hours on the volar side of the left forearm and read at the end of this period and read again after 48 and 72 hours. A challenge exposure was performed on the workers who showed allergic reactions. The patch was applied at the concentration of 0.1, 0.5, 1 and 2% test chemical. Acetone was used as vehicle.The interpretation of the patch tests was based on the usual criteria and was recorded as allergic, toxic, or negative.Identical Patch tests were applied on 10 controls. No skin sensitization effects were observed in test group or control group. Therefore, the test chemical was considered to be not sensitizing to human skin.
Skin sensitization effects were also estimated by three different models i.e, Battery, Leadscope and SciQSAR used within Danish QSAR database for the test chemical
Based on estimation, no skin sensitization reactions were observed in guinea pigs and humans. Therefore, the test chemical was considered to be not sensitizing.
The estimated result is further supported by a series of Patch tests performed with native teak dust moistened with water were applied on 10 "controls" and 112 workers who were exposed to teak in various working procedures. Moistened teak dust produced toxic reactions in 20.5 %, while native teak dust did not have primary irritant effects and was, therefore, considered to be the substance of choice for patch testing.
Patch tests were applied both with fresh native teak dust and dust moistened with water. The patch tests were carried out in the usual way and applied on the volar side of the left forearm. The patches were applied for 24 hours and read at the end of this period and read again after 48 and 72 hours. The interpretation of the patch tests was based on the usual criteria, and was recorded as allergic, toxic, or negative.
Patch testing was performed using the same technique on 10 nurses used as "controls". The testing was repeated after four weeks using teak dust which had been kept unsealed.
The patch tests with native teak dust were all negative at the first application. An allergic reaction was recorded in two cases when retested. Using moistened teak dust, toxic reactions were registered in seven cases, and four of these were of the bullous type. On repetition four weeks later, the toxic reactions had diminished, and in three cases they had disappeared. No bullous reaction was recorded.
18.7% of the workers showed an allergic skin reaction to native teak dust. The diagnosis of allergic contact eczema was made in 12. 5% and 6.2% were considered to have latent allergy. Primary irritant (contact) eczema was considered to be present in four individuals who had experienced acute, transitory, eczematous eruptions during the hot part of the summer when they perspired freely.
Since, positive reactions were observed in only 18-21 workers of the 112 tested, the test chemical can be considered to be not sensitizing to skin.
Based on the available results, the test chemical can be considered to lack the potential to cause dermal sensitization. Hence, the test chemical can be considered to be not sensitizing to skin.
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
Based on the available results, the test chemical can be considered to lack the potential to cause dermal sensitization. Hence, the test chemical can be considered to be not sensitizing to skin.
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