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EC number: 203-002-1 | CAS number: 102-06-7
- 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 / bone marrow chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
- Reference Type:
- secondary source
- Title:
- SIDS Initial Assessment report for SIAM 14 - 1,3-diphenylguanidine
- Author:
- Anonymous
- Year:
- 2 002
- Bibliographic source:
- OECD - Paris, France, 26-28 March 2002
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 475 (Mammalian Bone Marrow Chromosome Aberration Test)
- Deviations:
- yes
- Remarks:
- one dose of DPG used
- GLP compliance:
- yes
- Type of assay:
- chromosome aberration assay
Test material
- Reference substance name:
- 1,3-diphenylguanidine
- EC Number:
- 203-002-1
- EC Name:
- 1,3-diphenylguanidine
- Cas Number:
- 102-06-7
- Molecular formula:
- C13H13N3
- IUPAC Name:
- 1,3-diphenylguanidine
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Portage, Portage, MI
- Age at study initiation: 8/9 wks old
- Weight at study initiation: no data
- Assigned to test groups randomly: [no/yes, under following basis: ]
- Fasting period before study: no data
- Housing: one or two per cage prior dosing, and one per cage after dosing ; in suspended, stainless steel cages with stainless steel mesh bottoms
- Diet (e.g. ad libitum): Certified Rodent Diet #5002 (PMI, St Louis, MO), ad libitum
- Water (e.g. ad libitum): supplied by the public water system of St Louis, MO, ad libitum
- Acclimation period: 10 days (minimum)
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 64-79°F
- Humidity (%): 40-70%
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- Corn oil
- Details on exposure:
- The potential for 1,3-diphenylguanidine to induce chromosomal aberrations in the bone marrow cells of Sprague-Dawley rats was tested.
In the range-finding experiment, 2 male and 2 female rats were treated with 1,3-diphenylguanidine at 50, 100, 200, 400, 600, 800, 1000 or 5000 mg/kg body weight. 1,3-Diphenylguanidine was found to be toxic to male rats at 400 mg/kg and higher, and toxic to female rats at 200 mg/kg and at 600 mg/kg and higher as indicated by clinical signs of toxicity and death. The combined male and female LD50 was determined to be 427.3 mg/kg by the Probit method.
Based on results from the toxicity range-finding experiments, DPG was administered via oral gavage to 20 male and 20 female rats at a target dose of 300 mg/kg body weight (approximately 70% of the combined LD50). Control groups received 10 ml/kg of body weight of vehicle control (corn oil) (15 males and 15 females) or a 40 mg/kg of body weight dose of positive control (cyclophosphamide)(5 males and 5 females). Bone marrow was sampled at 6, 24 and 48 hours after dosing with the vehicle or 1,3-diphenylguanidine. A single sampling time of 24 hours after dosing was used for the cyclophosphamide control group. Slides were scored for increases in the proportion of aberrant metaphases and in the frequency of aberrations/cell.
Solutions or suspensions of the test substance were prepared on the day of use using corn oil as the vehicle. Animals were treated by a single oral gavage dose of corn oil (vehicle control, 10 ml/kg body weight). 1.3-diphenylguanidine in corn oil (10 ml of solution/kg body weight) or cyclophosphamide in 0.9% saline (positive control, 10 ml of solution/kg body weight) The positive control used was commercial grade cyclophosphamide monohydrate. - Duration of treatment / exposure:
- single administration
- Frequency of treatment:
- single administration
- Post exposure period:
- 72 hours
Doses / concentrations
- Remarks:
- Doses / Concentrations:
300 mg/kg (maximum tolerated dose)
Basis:
actual ingested
- No. of animals per sex per dose:
- Groups treated with DPG : 20 animals/sex/dose
Control group (vehicle) : 15 animals/sex
Positive group : 5 animals/sex - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide
Examinations
- Tissues and cell types examined:
- Bone Marrow cells (femur)
- Details of tissue and slide preparation:
- Extraction of bone marrow cells and slide preparation:
Two to three hours prior to harvest animals were injected intraperitoneally with colchicine (4 mg/kg) to arrest dividing cells in metaphase. Animals were sacrified by CO2 inhalation. Both femurs were removed and the muscle tissue cleaned away. The bone marrow cells were aspirated from each femur into a centrifuge tube containing approximately 10 ml of PBS at 37°C. The bone marrow cells were centrifuged at 1000 rpm for 5 minutes. The PBS was decanted and approximately 10 ml of hypotonic KCl (0.075 M), prewarmed at 37°C, was added to each tube. The cells were incubated at 37°C for 12/15 minutes to swell the cells. The bone marrow cells were centrifuged at 1000 rpm for 5 minutes and the supernatant decanted. The bone marrow cells were resuspended by gently tapping the bottom of the tube. While agitating the tube, 0.5 ml of fresh Carnoy's fixative (methanol/acetic acid, 3:1, v/v) was slowly added. The cells were resuspended with a Pasteur pipette to disperse clumps. Fixative was added to each sample ti achieve a final volume of 10 ml. The cells were centrifuged, the supernatant decanted, and 5 ml of fresh fixative was added to each tube 2-3 times more times. Cells were resuspended in an appropriate volume of fixative and dropped nto clean, wet slides. Slides were dried on a slide warmer or over a flame. Slides were stained with 2% Giemsa stain.
Scoring of slides
The scoring for mitotic index and chromosomal aberrations was performed by Pharmakon USA, Waverly, PA.
To eliminate bias, all slides were coded prior to scoring. Whenever possible, 50 metaphases/animal (500 metaphases/treatment group) were scored for the presence of chromosome aberration. Both chromatid- and chromosome-type aberrations were scored. A total of 5000 cells/treatment group were evaluated for mitotic frequency. Mitotic frequency is expressed as mitotic index, which is the fraction of mitotic cells in the cell population scored. - Statistics:
- Each individual test animal was the unit used for analysis of mean body weight change. A Dunnett's t-test (one sided) was used for comparison of treatment groups and positive control values with vehicle control values. Chi-square analysis was performed to compare the proportion of aberrant cells in the cells from animals treated with the test substance to those from animals treated with vehicle only. Student's t-test was used to compare structural aberrations per cell in the treatment groups with vehicle controls Results were considered statistically significant at the probability level of p<= 5.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- at 300 mg/kg
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- In the range finding study, 1,3-diphenylguanidine was found to be toxic to male rats at 400 mg/kg and higher, and to female rats at 200 and 600 mg/kg and higher.The combined LD50 was determined to be 427.3 mg/kg. based on these result, a target dose of 300 kg/kg bw (approximately 70% of the combined LD50 value) was selected as the maximum dose for male and female rats that would insure a reasonable probability of observing signs of toxicity but allow survival of the treated animals through to the 48 hour time point.
In the main cytogenetic experiment, 1,3-diphenylguanidine was toxic to male and female rats dosed at 300 mg/kg as evidenced by clinical signs of toxicity (hypoactive and non responsive) and death. Five male rats and six female rats were found dead within 24 hours of dosing. No deaths or clinical signs were observed in the control groups (vehicle and positive control). Statistically significant decreases in mean body weight were observed in the DPG treated male and female rats at 6 and 24 hours alter treatment and in the positive control treated male rats 24 hours alter treatment.
No statistically significant increases in the proportion of aberrant cells or aberrations cell were observed at the 300 mg/kg treatment level at the 6, 24 and 48 hour time points. Significant induction of toxicity, measured as mitotic index depression was observed at the 300 mg/kg treatment level at the 6 hour (35%) and 24 hour (31%) lime points. No depression in mitotic index was observed at the 48 hour time point.
The positive control group (cyclophosphamide) yielded expected positive responses indicating the adequacy of our experimental conditions for the detection of clastogens.
Applicant's summary and conclusion
- Conclusions:
- The observations and findings of this study indicate that 1,3-diphenylguanidine was nonclastogenic. It did not induce increases in the proportion of aberrant cells or aberrations/cell under the experimental conditions utilized in this study.
- Executive summary:
The potential for 1,3-diphenylguanidine to induce chromosomal aberrations in the bone marrow cells of Sprague-Dawley rats was tested. Based on results from the toxicity rangefinding experiments, 1,3-Diphenylguanidine (DPG) was administered via oral gavage to male and female rats at a target dose of 300 mg/kg body weight (approximately 70% of the combined LD50). Control groups received 10 ml/kg of body weight of vehicle control (corn oil) or a 40 mg/kg of body weight dose of positive control (cyclophosphamide). Bone marrow was sampled at 6, 24 and 48 hours alter dosing with the vehicle or DPG. A single sampling time of 24 hours alter dosing was used for the cyclophosphamide control group. Slides were scored for increases in the proportion of aberrant metaphases and in the frequency of aberrations/cell.
In the main cytogenetic experiment, DPG was toxic to male and female rats as evidenced by clinical signs of toxicity (hypoactive and nonresponsive) and death. Five male rats and six female rats were found dead within 24 hours of dosing. Statistically significant decreases in mean body weight were observed in the DPG treated male and female rats at 6 and 24 hours alter treatment and in the positive control treated male rats 24 hours afier treatment.
No statistically significant increases in the proportion of aberrant cells or aberrations/cell were observed at the 6, 24 and 48 hour time points. Significant induction of toxicity, measured as mitotic index depression. was observed at the 6 hour (35%) and 24 hour (31%) time points. No depression in mitotic index was observed at the 48-hour time point.
The positive control group (cyclophosphamide) yielded expected positive responses indicating the adequacy of our experimental conditions for the detection of clastogens.
The observations and findings of this study indicate that 1,3-diphenylguanidine was non clastogenic. It did not induce increases in the proportion of aberrant cells or aberrations/cell under the experimental conditions utilized in this study.
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