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EC number: 203-404-7 | CAS number: 106-50-3
- 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
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: well performed study in compliance with elementary guideline requirements
Data source
Reference
- Reference Type:
- publication
- Title:
- COMPARISON OF THE LOCAL LYMPH NODE ASSAY WITH THE GUINEA-PIG MAXIMIZATION TEST FOR THE DETECTION OF A RANGE OF CONTACT ALLERGENS
- Author:
- BASKETTER D. A. and SCHOLES E. W.
- Year:
- 1 992
- Bibliographic source:
- Food and chemical toxicology, Vol 30, 65-69
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: Basketter et al., 1991 and OECD 429
- Deviations:
- yes
- Remarks:
- method prior to OECD guideline
- Principles of method if other than guideline:
- CBA/Ca mice were used at the age of 8-12 wk. Animals of both sexes were used, but single experiments were limited to one sex. The test substance was assayed at three consecutive concentrations from the following range: 100, 50, 25, 10, 5, 2.5, 1.0, 0.5, 0.25, 0.1, 0.05 and 0.01%. Groups of four mice were treated by a daily topical application of 25 µl of each concentration on the dorsal surface of each ear for 3 consecutive days. Control mice were treated with the vehicle alone. 4-5 days after the first topical application, all mice were injected intravenously through the tail vein with 250 µl phosphate buffered saline (PBS) containing [3H]methyl thymidine (3HTdR; 20 µCi). After 5 h the mice were killed by carbon dioxide asphyxiation, and the draining auricular lymph nodes were excised and pooled for each experimental group. A single-cell suspension of lymph node cells (LNC) was prepared by gentle mechanical disaggregation through a stainless-steel gauze (200-mesh size), using the plunger of a syringe. Pooled LNC were pelleted at 190 g for 10 min, washed twice with 10 ml PBS and resuspended in 3 ml trichloroacetic acid (TCA; 5%) for the precipitation of macromolecules. After an overnight incubation with TCA at 4°C, the precipitate was recovered by centrifugation, resuspended in 1 ml TCA and transferred to 10 ml scintillation fluid. 3HTdR incorporation was measured by β-scintillation counting. The proliferative response of LNC was expressed as radioactive disintegrations per min per lymph node (dpm/node), and as the ratio of 3HTdR incorporation into LNC of test nodes relative to that recorded for control nodes (test/control ratio). A chemical was regarded as a sensitizer in the LLNA if at least one concentration of the chemical resulted in a three-fold or greater increase in 3HTdR incorporation compared with control values. Also, the data had to be compatible with a biological dose response although an allowance was made, especially at high doses, for either local toxicity or immunological suppression.
- GLP compliance:
- not specified
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- p-phenylenediamine
- EC Number:
- 203-404-7
- EC Name:
- p-phenylenediamine
- Cas Number:
- 106-50-3
- Molecular formula:
- C6H8N2
- IUPAC Name:
- benzene-1,4-diamine
- Details on test material:
- Several substances were tested in this study, the vast majority of these compounds were more than 98% pure.
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- other: CBA/Ca
- Sex:
- male/female
- Details on test animals and environmental conditions:
- CBA/Ca mice were used at the age of 8-12 wk. Animals of both sexes were used, but single experiments were limited to one sex.
Study design: in vivo (LLNA)
- Vehicle:
- acetone/olive oil (4:1 v/v)
- Concentration:
- 2.5, 5, 10%
- No. of animals per dose:
- 4
- Details on study design:
- Exposure period: 4 d
- Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
Results and discussion
- Positive control results:
- T/C ratio (ratio of test to control lymphocyte proliferation) of Cinnamic aldehyde
5%: 12.5
10%: 18.4
25%: 15.4
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Remarks on result:
- other: T/C ratio (ratio of test to control lymphocyte proliferation) of p-Phenylene diamine 2.5%: 12.8 5%: 16.5 10%: 23.3
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: DPM data are not presented in the publication.
Applicant's summary and conclusion
- Interpretation of results:
- sensitising
- Remarks:
- Migrated information
- Conclusions:
- p-Phenylene diamine was considered to be a skin sensitiser under the conditions of this test.
- Executive summary:
A sample of p-Phenylene diamine was assessed for its skin sensitisation potential using the mouse Local Lymph Node Assay. The test sample was applied as 2.5, 5.0, 10.0 % preparations in acetone-olive oil (4:1, v/v).
p-Phenylene diamine was shown to have the capacity to cause skin sensitisation when apllied as 2.5, 5.0, 10.0 % preparations.
In a positive control study, hexylcinnamaldehyd was shown to have the capacity to cause skin sensitisation, confirming the validity of the protocol used in this study.
In conclusion, p-Phenylene diamine was considered to be a skin sensitiser under the conditions of this test.
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