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EC number: 226-164-5 | CAS number: 5307-14-2
- 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
Carcinogenicity
Administrative data
Description of key information
non carcinogenic NOAEL was considered to be 110 mg/kg bw/day when Fischer 344 male rats were treated with 2-Nitro-p-phenylenediamine orally in feed for 78 weeks.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Link to relevant study records
- Endpoint:
- carcinogenicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Principles of method if other than guideline:
- Carcinogen toxicity conducted on Fischer 344 male rat
- GLP compliance:
- no
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Source: A. R. Schmidt, Madison, Wisconsin, and LaboratorySupply Company, Inc., Indianapolis, Indiana.Age at study initiation:6 weeks oldWeight at study initiation: No dataFasting period before study: Housing: polycarbonate cages suspended from aluminum racks. Ab-sorb-dri® hardwoodchip beddingDiet (e.g. ad libitum): Wayne Lab-Blox meal, ad libitum Water (e.g. ad libitum): Acidulated water (pH 2.5) was supplied to animals in water bottles filled by an automated metering device, ad libitumAcclimation period: quarantined for 2 weeks prior to initiationENVIRONMENTAL CONDITIONSTemperature (°C): 22° to 26°CHumidity (%): 45 and 55 percentAir changes (per hr): Incomingair was filtered through HEPA filters, at a rate of 12 to 15 complete changes of room air per hour. Photoperiod (hrs dark / hrs light):Fluorescent lighting was provided 8 hours per day (9:00 a.m. to 5:00 p.m.).
- Route of administration:
- oral: feed
- Type of inhalation exposure (if applicable):
- not specified
- Vehicle:
- other: basal laboratory diet
- Details on exposure:
- DIET PREPARATIONThe chemical was removed from its container and a proper amount was blended with an aliquot of the ground feed using a mortar and pestle. Once visual homogeneity was attained, the mixture was placed in a 6 kg capacity Patterson-Kelley standard model twin-shell stainless steel V-blender along with the remainder of the feed to be prepared. After 20 minutes of blending, the mixtures were placed in double plastic bags and stored in the dark at 4°C. The mixture was prepared once weekly.
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analytical verification of doses or concentrationSpectrophotometrically
- Duration of treatment / exposure:
- 78 weeks treatment
- Frequency of treatment:
- daily
- Post exposure period:
- 27 weeks observation
- Remarks:
- Doses / Concentrations:27.5mg/kgbw and 55 mg/kgbwBasis:
- No. of animals per sex per dose:
- 50 male rats /dose group
- Control animals:
- yes
- Details on study design:
- Dose selection rationale:To establish the maximum tolerated concentrations of 2-nitro-p- phenylenediamine for administration to dosed animals in the chronic studies, subchronic toxicity tests were conducted with 5 male rats/ dose group.No abnormal clinical signs were recorded for any rat group. The high concentration selected for administration to dosed male rats in the chronic bioassay was 55mg/kgbw
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes / No / No data: No data Time schedule: No dataCage side observations checked in table [No.?] were included.: No dataDETAILED CLINICAL OBSERVATIONS: Yes / No / No data: YesTime schedule: No dataBODY WEIGHT: Yes / No / No data: YesTime schedule for examinations:once a week for the first 6 weeks, every 2 weeks for the next 12 weeks, and at monthly intervals thereafterFOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): YesFood consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes / No / No data: Food consumption data were collected at monthly intervals from 20% of the animals in each group.Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes / No / No data: No dataFOOD EFFICIENCY:Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: Yes / No / No data: No dataWATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes / No / No data: No dataTime schedule for examinations:No dataOPHTHALMOSCOPIC EXAMINATION: Yes / No / No data: No dataHAEMATOLOGY: Yes / No / No data: No dataCLINICAL CHEMISTRY: Yes / No / No data: No dataURINALYSIS: Yes / No / No dataNo dataNEUROBEHAVIOURAL EXAMINATION: Yes / No / No data: No data
- Sacrifice and pathology:
- GROSS PATHOLOGY: Yes (see table) / No / No data: YesHISTOPATHOLOGY: Yes (see table) / No / No data: Yes
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- effects observed, treatment-related
- Details on results:
- CLINICAL SIGNS AND MORTALITY:No other abnormal clinical signs were recorded. The Tarone’s test for association between dosage and mortality was not significant for males.BODY WEIGHT AND WEIGHT GAIN:Dose-related mean body weight depression was apparent in male rats from week 12 until week 87FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): No dataFOOD EFFICIENCY: No dataWATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study):No dataOPHTHALMOSCOPIC EXAMINATION:HAEMATOLOGY: No data CLINICAL CHEMISTRY: No dataURINALYSIS: No dataNEUROBEHAVIOUR: No dataORGAN WEIGHTS: No dataGROSS PATHOLOGY:There were adequate numbers of male rats at risk from late developing tumors as 94 percent (47/50) of the high dose, 92 percent (46/50) of the low dose, and 80 percent (16/20) of the controls survived on test until the termination of the study.HISTOPATHOLOGY: NON-NEOPLASTIC:There was also a variety of nonneoplastic lesions in both control and dosed animals. Such lesions have been encountered previously as spontaneous occurrences in laboratory ratsHISTOPATHOLOGY: NEOPLASTIC (if applicable):A variety of neoplasms was seen in both control and dosed rats.Each type of tumor represented had been encountered previously as a spontaneous lesion in rats. HISTORICAL CONTROL DATA (if applicable):No dataOTHER FINDINGS: Statistical analysis of the results :For male rats, the Cochran-Armitage test indicated a significant (p = 0.017) positive association between dose and the combined 1ncidence of C-cell carcinomas or C-cell adenomas of the thyroid. However, the Fisher exact tests comparing high dose to control and low dose to control were not significant. For male rats there was the possibility of a negative association between dose and the combined incidence of leukemia or malignant lymphoma as the Cochran-Armitage test and the Fisher exact tests indicated significant negative results.The theoretical possibility of tumor induction in rats by 2-nitro-p-phenylenediamine could not be established under the conditions of this test.
- Dose descriptor:
- NOAEL
- Effect level:
- 110 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- other: No carcinogenic effect on Testis
- Remarks on result:
- other: Effect type: carcinogenicity (migrated information)
- Conclusions:
- Non carcinogenic NOAEL was considered to be 110 mg/kg bw/day when Fischer 344 male rats were treated with 2-Nitro-p-phenylenediamine orally in feed for 78 weeks.
- Executive summary:
In a Chronic carcinogenicity test, Fischer 344 male rats were treated by using 2-Nitro-p-phenylenediamine in the concentration of 0, 55 and 110 mg/kg bw/day for male orally in diet. No significant effect on survival and clinical sign of treated male rats were observed as compared to control. Decrease in body weight was observed in treated male rats throughout study as compared to control. Nonneoplastic and neoplastic such as Leukemia or Malignant Lymphoma of Hematopoietic System, C-Cell Carcinoma or C-Cell Adenoma of Thyroid, Islet-Cell Adenoma of Pancreatic Islets and Interstitial-Cell Tumor of Testis were observed in treated male rats. But, the observed Nonneoplastic and neoplastic lesion are considered to represent spontaneous lesions in these animals. Therefore, non carcinogenic NOAEL was considered to be 110 mg/kg bw/day when Fischer 344 male rats were treated with 2-Nitro-p-phenylenediamine orally in feed for 78 weeks.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 110 ng/kg bw/day
- Study duration:
- chronic
- Species:
- rat
- Quality of whole database:
- Data is of K1 and from peer reviewed publication
Justification for classification or non-classification
2-Nitro-p-phenylenediamine (CAS no 5307-14-2) as per CLP regulation likely to be non hazardus
Additional information
In a study conducted by U.S. DEPARTMENT OF HEALTH, EDUCATION, AND WELFARE (1979), carcinogenicity was evaluated in Fischer 344 male rats by using 2-Nitro-p-phenylenediamine in the concentration of 0, 55 and 110 mg/kg bw/day for male orally in diet. No significant effect on survival and clinical sign of treated male rats were observed as compared to control. Decrease in body weight was observed in treated male rats throughout study as compared to control. Nonneoplastic and neoplastic such as Leukemia or Malignant Lymphoma of Hematopoietic System, C-Cell Carcinoma or C-Cell Adenoma of Thyroid, Islet-Cell Adenoma of Pancreatic Islets and Interstitial-Cell Tumor of Testis were observed in treated male rats. But, the observed Nonneoplastic and neoplastic lesion are considered to represent spontaneous lesions in these animals. Therefore, non carcinogenic NOAEL was considered to be 110 mg/kg bw/day when Fischer 344 male rats were treated with 2-Nitro-p-phenylenediamine orally in feed for 78 weeks.
In the above similar study, carcinogenicity was evaluated in Fischer 344 female rats by using 2-Nitro-p-phenylenediamine in the concentration of 0, 110 and 220 mg/kg bw/day for female orally in diet. No significant effect on survival and clinical sign of treated male rats were observed as compared to control. Decrease in body weight was observed in treated male rats throughout study as compared to control. Nonneoplastic and neoplastic such as Leukemia or Malignant Lymphoma of Hematopoietic System, Chromophobe Adenoma of Pituitary and Endometrial Stromal Polyp of Uterus were observed in treated female rats. But, the observed Nonneoplastic and neoplastic lesion are considered to represent spontaneous lesions in these animals. Therefore, non carcinogenic NOAEL was considered to be 220 mg/kg bw/day when Fischer 344 male rats were treated with 2-Nitro-p-phenylenediamine orally in feed for 78 weeks.
In the above similar study, carcinogenicity was evaluated in B6C3FI male and female mice using 2-Nitro-p-phenylenediamine in the concentration of 0, 330 and 660 mg/kg bw/day in diet. No significant effect on survival and clinical sign of treated male and female mice were observed as compared to control. Decrease in body weight was observed in treated male and female mice throughout study as compared to control. Alveolar/Bronchiolar Adenoma of Lung, Leukemia orMalignant Lymphoma of Hematopoietic System and Hepatocellular Carcinoma or Hepatocellular Adenoma were observed in male mice at 330 and 660 mg/kg bw/day, but tumors were of the usual types and in the usual incidences seen in aging B6C3Fl male mice. In female mice, Hepatocellular adenoma and hepatocellular carcinoma were observed both at 330 and 660 mg/kg bw/day as compared to control. Therefore, Non carcinogenic NOAEL for male mice was considered to be 660 mg/kg bw/day and carcinogenic LOAEL for female mice was 330 mg/kg bw/day when B6C3FI male and female mice were treated with 2-Nitro-p-phenylenediamine orally in diet. Thus, based on the above available data, 2-Nitro-p-phenylenediamine (CAS no 5307-14-2) as per CLP regulation likely to be non hazardus
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