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EC number: 201-635-8 | CAS number: 85-83-6
- 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
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- repeated dose toxicity: oral, other
- Remarks:
- Combined repeated dose repro-devp. Screen
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- secondary literature
- Justification for type of information:
- Data is from NTIS report
Data source
Reference
- Reference Type:
- other: NTIS
- Title:
- Bioassay of Diarylanilide Yellow for Possible Carcinogenicity
- Author:
- U. S. Department of Commerce
- Year:
- 1 977
- Bibliographic source:
- National Technical Information Services,
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: Refer below principle
- Principles of method if other than guideline:
- Combined repeated dose – carcinogenicity assay was performed to determine the toxic nature of test chemical upon repeated exposure by oral route
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- 2,2'-[(3,3'-dichloro[1,1'-biphenyl]-4,4'-diyl)bis(azo)]bis[3-oxo-N-phenylbutyramide]
- EC Number:
- 228-787-8
- EC Name:
- 2,2'-[(3,3'-dichloro[1,1'-biphenyl]-4,4'-diyl)bis(azo)]bis[3-oxo-N-phenylbutyramide]
- Cas Number:
- 6358-85-6
- Molecular formula:
- C32H26Cl2N6O4
- IUPAC Name:
- 2,2'-[(3,3'-dichlorobiphenyl-4,4'-diyl)didiazene-2,1-diyl]bis(3-oxo-N-phenylbutanamide)
- Details on test material:
- CAS name: 2,2'-[(3,3'-dichlorobiphenyl-4,4'-diyl)didiazene-2,1-diyl]bis(3-oxo-N-phenylbutanamide)
CAS no: 6358-85-6
EC no: 228-787-8
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Details on species / strain selection:
- No data
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River
Breeding Laboratories, Wilmington, Massachusetts
- Age at study initiation: 7 weeks old
- Weight at study initiation:
- Fasting period before study:
- Housing: Rats were housed five per cage by sex. During quarantine and for the first 6 weeks of study, they were kept in galvanized-steel wire-mesh cages suspended above newspapers. Newspapers were replaced daily, and cages and racks washed weekly. From week 6 rats were kept in suspended polycarbonate cages equipped with disposable nonwoven filter sheets. Clean bedding and cages were provided twice weekly.
Hardwood chips (Ab-sorb-dri® Wilner Wood Products Co.) were used through the first 3 months of study, then corncob bedding (SAN-I-CEL®, Paxten Processing Co.) for the next 12 months. and then another type of corncob bedding (Bed-o'CobS®, The Anderson's Cob Division) for the remainder of the bioassay.
- Diet (e.g. ad libitum): Wayne Lab-Blox® ad libitum
- Water (e.g. ad libitum): Water ad libitum
- Acclimation period: 2 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 23° to 34°C
- Humidity (%): 10-85%
- Air changes (per hr): Incoming air was filtered through Tri-Dek® 15/40 denier Dacron® filters providing six changes of room air per hour.
- Photoperiod (hrs dark / hrs light): 12-hour-daily cycle
IN-LIFE DATES: From: To:
Administration / exposure
- Route of administration:
- oral: feed
- Details on route of administration:
- No data
- Vehicle:
- other: Feed
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS: The test chemical was administered to treated animals as a component of feed. The test chemical was mixed with feed in a 6 Kg Patterson-Kelly standard model stainless steel twin-shell V blender. After 20 mins of blending, the mixtures were placed in double plastic bags and stored at 4˚C in dark.
DIET PREPARATION
- Rate of preparation of diet (frequency): Weekly
- Mixing appropriate amounts with (Type of food): Wayne Lab-Blox®
- Storage temperature of food: at 4˚ for no longer than 2 weeks
VEHICLE
- Justification for use and choice of vehicle (if other than water): Wayne Lab-Blox®
- Concentration in vehicle: 0, 1250 or 2500 mg/Kg/day
- Amount of vehicle (if gavage): No data
- Lot/batch no. (if required): No data
- Purity: No data - Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- No data
- Duration of treatment / exposure:
- 78 weeks
- Frequency of treatment:
- Daily
Doses / concentrations
- Remarks:
- 0, 2.5 or 5.0% (0, 1250 or 2500 mg/Kg/day)
- No. of animals per sex per dose:
- Total: 150 males and 150 females
0 mg/Kg/day: 50 males and 50 females
1250 mg/Kg/day: 50 males and 50 females
2500 mg/Kg/day: 50 males and 50 females - Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: In order to establish the maximum tolerated concentrations of diarylanilide yellow for dministration to treated animals in the chronic studies, subchronic toxicity tests was conducted. Diarylanilide yellow was incorporated into the basal laboratory diet and fed ad libitum to four of the five rat groups in a dose range of 0.1, 0.3, 1.0, and 3.0 percent. The remaining group of each species served as a control group, receiving only the basal laboratory diet. The dosed dietary preparations were administered for a period of 8 weeks. A dosage inducing no mortality or body weight gain retardation in either sex was to be selected as the initial high dose in the chronic bioassay. No decreases in food consumption or significant weight depression relative to controls were observed in any group. All animals survived until necropsy (week 8). Although the external surfaces of all animals at all concentrations were bright yellow, gross necropsy revealed no abnormalities or organ discoloration other than the mucosal surfaces of the intestinal tract, which appeared bright yellow due to direct contact with the test compound.
In the Guidelines for Carcinogen Bioassay in Small Rodents it is indicated that a chronic dietary concentration of 5 percent (50,000 ppm) should not be exceeded. This applies even if the compound causes no toxicity during subchronic testing. An exception can be made under special circumstances. E.g. if the chemical is a major component of the human diet. Because no toxic symptoms or gross abnormalities were observed clinically or at necropsy- in animals receiving the tested concentrations, 5.0 percent was selected as the concentration to be administered to the high dose groups during the chronic bioassay.
- Rationale for animal assignment (if not random): Animals were assigned to groups and distributed among cages so that average body weight per cage was approximately equal for a given sex
- Rationale for selecting satellite groups: No data
- Post-exposure recovery period in satellite groups: No data
- Section schedule rationale (if not random): No data - Positive control:
- No data
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Twice daily
- Cage side observations checked in table [No.?] were included. Mortality
DETAILED CLINICAL OBSERVATIONS: Yes / No / No data
- Time schedule:
BODY WEIGHT: Yes
- Time schedule for examinations: Animals were weighed immediately prior to initiation of the experiment. Body weights were recorded twice weekly for
the first 12 weeks of the study and at monthly intervals thereafter.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes, Food consumption was monitored for seven consecutive days once a month for the first nine months of the bioassay and for three consecutive days each month thereafter.
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes
FOOD 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: No data
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes / No / No data
- Time schedule for examinations:
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: No data
- Dose groups that were examined: No data
HAEMATOLOGY: No data
- Time schedule for collection of blood: No data
- Anaesthetic used for blood collection: No data
- Animals fasted: No data
- How many animals: No data
- Parameters checked in table [No.?] were examined. No data
CLINICAL CHEMISTRY: No data
- Time schedule for collection of blood: No data
- Animals fasted: No data
- How many animals: No data
- Parameters checked in table [No.?] were examined. No data
URINALYSIS: No data
- Time schedule for collection of urine: No data
- Metabolism cages used for collection of urine: No data
- Animals fasted: No data - Parameters checked in table [No.?] were examined. No data
NEUROBEHAVIOURAL EXAMINATION: No data
- Time schedule for examinations: No data
- Dose groups that were examined: No data
- Battery of functions tested: sensory activity / grip strength / motor activity / other: No data
OTHER: No data - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes, The animals were euthanized by carbon dioxide inhalation, and were immediately necropsied. The presence of tissue masses and lesions was determined by monthly.
HISTOPATHOLOGY: Yes, The histopathologic examination consisted of gross and microscopic examination of major tissues, organs, or gross lesions taken from sacrificed animals and, whenever possible, from animals found dead.
Slides were prepared from the following tissues: skin, subcutaneous tissue, lungs and bronchi, trachea, bone marrow, spleen, lymph / nodes, thymus, heart, salivary gland, liver and bile duct, pancreas, esophagus, stomach, small intestine,large intestine, kidney, urinary bladder, pituitary, adrenal, thyroid, parathyroid, pancreatic islets, testis, prostate, brain, uterus, mammary gland, and ovary. - Other examinations:
- No data
- Statistics:
- Refer below section
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- All the treated rats, both male and female, appeared bright yellow in color. The only other clinical sign recorded for male or female rats vas a hard crusted lesion on the back of one male control animal.
- Mortality:
- no mortality observed
- Description (incidence):
- In the males survival was quite high, as 74 percent of the high dose, 84 percent of the low dose, and 64 percent of the control rats survived until the end of the study despite the sacrifice of five high dose and five control rats in week 78. In the females, 66 percent of the high dose, 80 percent of the low dose, and 72 percent of the control rats survived until the end of the study, despite the sacrifice of five high dose and five control rats in week 78.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- The body weight patterns for control and treated rat groups of both sexes were generally equivalent throughout the treatment period
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- no effects observed
- Description (incidence and severity):
- In addition, the conjunctivas were faintly yellow as were most organs and internal mucosal surfaces.
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- not specified
- Neuropathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- With a few exceptions, the same variety of neoplasms occurred sporadically and randomly in the chemically treated and control groups. No particular organ or system seemed to be the target of this chemical. Sporadic and unusual neoplasms that occurred in the treated but rot in control animals were as follows: a metastatic chordoma of unknown origin occurred in the lung of 1/49 of the low dose males. and 1/49 of the low dose females had an osteogenic sarcoma.
- Histopathological findings: neoplastic:
- no effects observed
- Description (incidence and severity):
- The incidence-and variety of nonneoplastic degenerative, proliferative, and inflammatory lesions were similar in the control and the chemically treated rats, except for treatment-related basophilic /cytoplasm changes in hepatocytes of treated males and females.
- Other effects:
- not specified
- Details on results:
- No data
Effect levels
- Dose descriptor:
- NOAEL
- Effect level:
- 2 500 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No significant effects were noted at the mentioned dose level
- Remarks on result:
- other: No toxic effects were observed
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- The No Observed Adverse Effect level (NOAEL) for test chemical was considered to be 2500 mg/Kg/day.
- Executive summary:
Combined repeated dose – carcinogenicity assay was performed to determine the toxic nature of test chemical upon repeated exposure by oral route. The study was performed using male and female F344 rats. The test chemical was mixed with feed and used at dose level of 0, 1250 or 2500 mg/Kg/day (0, 2.5 or 5.0%) for 109 weeks including 28 weeks of observation period. The animals were observed for clinical signs, mortality, changes in body weight and food consumption, opthalmology. The animals were subjected to gross pathology and histopathology. All the treated rats, both male and female, appeared bright yellow in color. The only other clinical sign recorded for male or female rats was a hard crusted lesion on the back of one male control animal. No statistically significant positive association was noted in the dosage and mortality. The body weight patterns for control and treated rat groups of both sexes were generally equivalent throughout the treatment period. In addition, the conjunctivas were faintly yellow as were most organs and internal mucosal surfaces. With a few exceptions, the same variety of neoplasms occurred sporadically and randomly in the chemically treated and control groups. No particular organ or system seemed to be the target of this chemical. Sporadic and unusual neoplasms that occurred in the treated but rot in control animals were as follows: a metastatic chordoma of unknown origin occurred in the lung of 1/49 of the low dose males and 1/49 of the low dose females had an osteogenic sarcoma. The incidence-and variety of nonneoplastic degenerative, proliferative, and inflammatory lesions were similar in the control and the chemically treated rats, except for treatment-related basophilic/cytoplasm changes in hepatocytes of treated males and females. Based on the observations made, the No Observed Adverse Effect level (NOAEL) for test chemical is considered to be 2500 mg/Kg/day.
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