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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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study was not conducted under GLP and limited information is provided on animals used and environmental conditions. This study was selected as the key study because the information provided for the hazard endpoint is sufficient for the purpose of classification and labeling and/or risk assessment.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 981
- Report date:
- 1981
Materials and methods
- Objective of study:
- excretion
- metabolism
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- Deviations:
- yes
- Remarks:
- One dose level, details on test animals and environmental conditions not complete.
- GLP compliance:
- not specified
Test material
- Details on test material:
- - Purity: > 99%
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- 14C-p-phenylenediamine
Test animals
- Species:
- rat
- Strain:
- not specified
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Not reported
- Age at study initiation: Not reported
- Weight at study initiation: 250 g
- Fasting period before study: Not reported
- Housing: Not reported
- Individual metabolism cages: yes
- Diet (e.g. ad libitum): Not reported
- Water (e.g. ad libitum): Not reported
- Acclimation period: Not reported
ENVIRONMENTAL CONDITIONS
- Temperature (°C): Not reported
- Humidity (%): Not reported
- Air changes (per hr): Airflow: 600-700 mL/min.
- Photoperiod (hrs dark / hrs light): Not reported
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- other: Tween 20: 1.15% saline (20:80)
- Details on exposure:
- Non-labeled test substance was recrystallized in methanol and stored in a freezer. The 14-C-labelled test substance was purified by HPLC. The dose was formulated in Tween 20:1.15% saline (20:80) immediately prior to dosing. Each 250 g male rat received a single 10 mg/kg ip dose. Each rat was administered approximately 2.42 µCi of 14C radioactivity.
- Duration and frequency of treatment / exposure:
- 72 hours
Doses / concentrations
- Remarks:
- Doses / Concentrations:
10 mg/kg in a 20 mL volume (2.42 µCi 14C radioactivity)
- No. of animals per sex per dose / concentration:
- 3/time point
- Control animals:
- no
- Details on study design:
- Immediately after dosing, each rat was housed individually in a glass metabolism unit. Urine and feces samples were collected separately at 6-, 24-, 48-, and 72-hour intervals after dosing. Samples were frozen and stored immediately after collection. Preliminary studies revealed no evolution of [14C]-CO2 following [14C]-PPD dosing; therefore, expired CO2 was not trapped. The rats were sacrificed 72 hours after dosing. Upon sacrifice blood was drawn and refrigerated in heparinized tubes. The heart, lungs, liver, spleen, kidney, G.I. tract, testes, brain, samples of fat, skin, and muscle were excised and weighed. The carcass was weighed, frozen, and stored with all excised tissues and organs. The metabolism units were rinsed with dilute detergent, water, and acetone into bottles, and refrigerated. Radioactivity in the urine and cage rinses was analyzed directly by liquid scintillation counting (LSC). Samples of feces, blood, tissues, and carcasses were analyzed for 14C by tissue oxidation using a tissue oxidizer.
Urine samples were examined for the distribution of [14C]-PPD metabolites. The quality of organo-soluble metabolites was determined by extraction with ethyl acetate. Urine was also subjected to enzymatic hydrolysis. Radioactivity levels in the organic phase were compared between non-hydrolyzed and enzymatically hydrolyzed urine. The organo-soluble radioactivity was analyzed by thin layer chromatography (TLC) and autoradiography. The organo-soluble extracts were also analyzed by HPLC using LSC analysis of eluant fractions. Procedures were also examined for preparing extracts that were relatively free of endogenous compounds. Column chromatography was examined. The purpose was to isolate fractions that were enriched with PPD metabolites and relatively free of urinary contaminants.
Metabolite fractions from column clean up procedures and organic solvent extractions were purified by HPLC. Fractions from the HPLC eluant were collected and analyzed for 14C content. The radioactive fractions containing the major metabolite were evaporated to dryness under N2. The purified metabolite was then analyzed by GC/Mass Spectrometry. Authentic standards of PPD, N-acetyl-PPD, and N,N'-diacetyl-PPD were also analyzed and compared to the metabolite. - Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: urine, faeces, blood, heart, lungs, liver, spleen, kidney, GI tract, testes, brain, fat, skin, and muscle.
- Time and frequency of sampling: Urine and faeces: 6, 24, 48, and 72 hours
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine
- Time and frequency of sampling: Total (72 h)
- Method type(s) for identification: HPLC, TLC, GC
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on distribution in tissues:
- 51.4% in urine, 35.3% in faeces, 3.3% in organs/tissues, and 3.2% in cage rinse
- Details on excretion:
- Approximately 50% of the dose was excreted in the urine and 35% in the faeces. The standard deviations revealed substantial animal variation in the distribution of excreted 14C activity. The urinary excretion for the first 24 hours represented over 40% of the original dose. Approximately 90% of the original dose was excreted in the urine and feces by 72 hours after dosing. Approximately 3-4% of the dose remained in the animal at the 72-hour sacrifice.
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- The solvent soluble metabolites were examined using TLC and HPLC. Both systems revealed the presence of 2 metabolites as monitored by 14C-containing zones. The ratio of the major to minor component was approximately 2:1. Non-labeled standards of potential test substance metabolites were also analyzed. In both the TLC and HPLC system, the major metabolite co-chromatographed with the N,N'-diacetyl-PPD standard. The project was halted before the hydrolysis, extractions, and derivatization procedures were satisfactorily refined.
Any other information on results incl. tables
Table 1: Disposition of 14C Activity 72 Hours After a Single 10 mg/kg Dose of [14C]PPD |
||
Sample |
µg±SD |
Percent of±SD |
Urine |
1286 ± 293 |
51.4 ±11.7 |
Feces |
886 ± 203 |
35.3 ± 8.1 |
Organs, Tissues |
82 ± 25 |
3.3 ± 1.0 |
Cage Rinse |
78 ± 31 |
3.2 ± 1.2 |
Table 2: Cumulative Percent Excretion of 14C Activity from Rats Dosed with 10 mg/kg [14C]PPD |
||
Sample |
Cumulative Percent Urinary Excretion |
Cumulative Percent Fecal Excretion |
6 h |
24.8 |
- |
24 h |
45.6 |
22.9 |
48 h |
50.5 |
32.8 |
72 h |
51.4 |
35.4 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): low bioaccumulation potential based on study results
This study and the conclusions which are drawn from it fulfill the quality criteria (validity, reliability, repeatability). In rats administered a single 10 mg/kg ip dose, approximately 50% of the dose was excreted in the urine and 35% in the afeces. The standard deviations reveal substantial animal variation in the distribution of excreted 14C activity. Approximately 3-4% of the dose remained in the animal at the 72-hour sacrifice. Two metabolites were detected. - Executive summary:
The excretion and distribution of 14C radioactivity in male rats were determined for a 72-hour period after the single 10 mg/kg i.p. dose. Approximately 50% of the dose was excreted in the urine and 35% in the faeces. The standard deviations reveal substantial animal variation in the distribution of excreted 14C activity. Approximately 3-4% of the dose remained in the animal at the 72-hour sacrifice. Sufficient quantities of 14C-labeled metabolites were excreted in the 6- and 24-hour urine samples to consider urinalysis as a plausible method for biological monitoring. The solvent soluble metabolites were examined using the TLC and HPLC. Both systems revealed the presence of 2 metabolites as monitored by 14C-containing zones. The ratio of the major to minor component was approximately 2:1. Non-labelled standards of potential test substance metabolites were also analyzed. In both the TLC and HPLC system, the major metabolite co-chromatographed with the N,N'-diacetyl-PPD standard. The project was halted before the hydrolysis, extractions, and derivatization procedures were satisfactorily refined.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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