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EC number: 202-430-6 | CAS number: 95-54-5
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 980
- Reference Type:
- publication
- Title:
- The in vivo micronucleus assay in mammalian bone marrow and peripheral blood. A report of the U.S. Environmental Protection Agency gene-tox program.
- Author:
- Mavournin, K.H., Blakey, D.H., Cimino, M.C., Salamone, M.F., and Heddle, J.A.
- Year:
- 1 992
- Bibliographic source:
- Mutat. Res., 239:29-80 (cited in Yang, W.L., Klopman, G. and Rosenkranz, H.S. (1992) Structural basis in the in vivo induction of micronuclei. Mutat. Res., 272(2):111-124.
- Reference Type:
- publication
- Title:
- Mutagenic effects of the ortho-phenylenediamine in mammalian somatic and germ cells.
- Author:
- Wild, D. Gocke, E. and Turan, Z.
- Year:
- 1 981
- Bibliographic source:
- Mutat. Res., 85(4):292
Materials and methods
- Principles of method if other than guideline:
- The micronucleus test was conducted with animals receiving 2 equal doses separated by a 24 hour interval. Six hours after the second dose, bone marrow was isolated. Smears were prepared and stained with May-Grünwald and Giesma. Slides were coded and usually 1000 polychromatic erythrocytes (PCEs) from each animal were analyzed for micronuclei.
- GLP compliance:
- no
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 95-45-5
- IUPAC Name:
- 95-45-5
- Details on test material:
- Test substance( as cited in study report): o-phenylenediamine
Purity: 99%.
Purchased from: Fluka AG.
Constituent 1
Test animals
- Species:
- guinea pig
- Strain:
- other: albino
- Sex:
- male/female
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- 0.9% NaCl
- Details on exposure:
- MICRONUCLEUS TEST:
- Animals received 2 equal doses separated by a 24 hour interval.
- Six hours after the second dose, bone marrow was isolated.
- Smears were prepared and stained with May-Grünwald and Giesma.
- Slides were coded and usually 1000 polychromatic erythrocytes (PCEs) from each animal were analyzed for micronuclei.
- Cytogenetic damage is expressed by an increased frequency of micronucleus-containing PCEs.
- The proportion of polychromatic among total (poly and normo-chromatic) PCEs (PE/PE + NE) is based on the differentiation of 1000 total erythrocytes. - Duration of treatment / exposure:
- The injections were 24 hours apart.
- Frequency of treatment:
- Two i.p. injections
Doses / concentrationsopen allclose all
- Dose / conc.:
- 108 other: mg/kg
- Dose / conc.:
- 216 other: mg/kg
- Dose / conc.:
- 324 other: mg/kg
- No. of animals per sex per dose:
- Three male and female guinea pigs per exposure group and control (12 total guinea pigs.)
- Control animals:
- yes, concurrent vehicle
Examinations
- Tissues and cell types examined:
- bone marrow
- Details of tissue and slide preparation:
- 6 hr after the second dose bone marrow was isolated, smears were prepared and stained with May-Grunwald and Giemsa; slides were coded and usually 1000 polychromatic erythrocytes from each animal were analyzed for micronuclei.
Results and discussion
Test results
- Genotoxicity:
- positive
- Additional information on results:
- - All doses were non-lethal under the experimental conditions.
- The test substance (TS) produced a higher percentage of micronucleated polychromatic erythrocytes (MPEs.)
- i.p.: Significant increase in all dose groups compared to the control.
- oPDA was active at 2 doses of 108 mg/kg and at higher doses.
- There was considerable not sex-related interindividual variation of the cytogenetic effect.
Any other information on results incl. tables
.
Table 1. Micronucleus tests with ortho-phenylenediamine on bone marrow of Guinea pigs |
|||||||
Chemical (vehicle) |
Species |
Route of Application |
Dose (mg/kg) |
Surviving/ treated animals |
PE / (PE + NE) |
Micronucleated / Total PE |
|
Mean % |
Range of valuesc |
||||||
O-phenylene-diamine (0.9% NaCl) |
|||||||
Guinea pig |
i.p. |
2 x 324 |
3/3 |
0.05 |
33.8a |
13-62 |
|
2 x 216 |
3/3 |
0.21 |
16.0a |
6-28 |
|||
2 x 108 |
3/3 |
0.21 |
6.5b |
3-11 |
|||
0 |
3/3 |
0.25 |
3.2 |
2-5 |
|||
PE: polychromatic erythrocytes, NE: normochromatic erythrocytes |
|||||||
ap≤0.01, bp≤0.05 |
|||||||
cWhole numbers are given, the actual experimental values can slightly differ because occasionally slightly more than 1000 PE were analyzed. |
Applicant's summary and conclusion
- Conclusions:
- Chromosomal damage was detected in guinea pigs following intraperitoneal injections of the TS. Specifically, a dose-dependent increase in the mean percentage of micronucleated polychromatic erythrocytes was observed for 108 mg/kg and above.
- Executive summary:
Chromosomal damage was detected in guinea pigs following intraperitoneal injections of the TS. Specifically, a dose-dependent increase in the mean percentage of micronucleated polychromatic erythrocytes was observed for 108 mg/kg and above.
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