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EC number: 266-096-3 | CAS number: 66063-05-6
- 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

Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 1982-02-03
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 982
- Report date:
- 1982
Materials and methods
- Objective of study:
- absorption
- distribution
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- Deviations:
- yes
- Remarks:
- See "Overall remarks" for more information
- GLP compliance:
- no
- Remarks:
- Older study, predates mandatory GLP
Test material
- Reference substance name:
- 1-[(4-chlorophenyl)methyl]-1-cyclopentyl-3-phenylurea
- EC Number:
- 266-096-3
- EC Name:
- 1-[(4-chlorophenyl)methyl]-1-cyclopentyl-3-phenylurea
- Cas Number:
- 66063-05-6
- Molecular formula:
- C19H21ClN2O
- IUPAC Name:
- 1-[(4-chlorophenyl)methyl]-1-cyclopentyl-3-phenylurea
Constituent 1
- Radiolabelling:
- yes
Test animals
- Species:
- other: rat and mouse
- Strain:
- other: rat: Fisher, and mouse: CD-1 (males only)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Weight at study initiation:
Rats: ca. 150g (male) and ca. 125 g (female).
Mice (only males): ca. 25 g.
- Diet: ad libitum.
- Water: ad libitum.
ENVIRONMENTAL CONDITIONS
- Temperature: 24±2°C
- Fasting period: 16 hr
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- other: N,N-dimethylformamide in polyethylene glycol 400 (1:9 v/v)
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Phenyl labeled 14C-pencycuron or carbonyl labeled 14C-pencycuron dissolved in 0.5 ml of N,N-dimethylformamide was diluted with 4.5 ml of polyethylene glycol 400 and a 5 ml of mixture solution per kilogram body weight (200 µCi/kg). - Duration and frequency of treatment / exposure:
- Single dose
Doses / concentrations
- Dose / conc.:
- 40 mg/kg bw (total dose)
- No. of animals per sex per dose / concentration:
- 3/sex/dose/time point
- Control animals:
- no
- Details on dosing and sampling:
- TOXICOKINETIC / PHARMACOKINETIC STUDY (Absorption, distribution)
- Tissues and body fluids sampled:
* Rats: liver, kidney, heart, lung, brain, spleen, pancreas, adrenal, thymus, right femoral muscle, abdominal fat and sexual organs (male: testis, female: uterus and ovary), and blood.
* Mice: blood cell, plasma, liver, kidney, lung, heart, brain, spleen, pancreas, adrenal, gall-bladder, muscle, adipose and testis.
- Time and frequency of sampling:
* Rats: 1, 3, 8, 24, 48, 72 and 144 or 168 hr after the oral administration.
* Mice: 2, 8, 24 and 72 hr after the oral administration.
- Analysis of tissues:
*Rats:
Blood was collected in a 10 ml glass centrifuge tube containing heparin and centrifuged at 2,000 xg for 5 min for separation of plasma and blood cell. The precipitate was washed with 0.9% sodium chloride centrifugally and the washing supernatant was combined with plasma. The total radiocarbon in tissues and blood preparations was analyzed by LSC after the combustion with a sample oxidizer of 100 to 500 mg homogenized tissue sample in triplicate. Digestive organs of stomach, small intestine and large intestine were collected from each animal.
Each digestive organs in rats were homogenized in a Waring blender with five volume of methanol. The methanol extracts after concentration were analyzed directly by Isc and remaining organs samples were analyzed by LSC after oxygen combustion.
*Mice:
The total radiocarbon in tissues of male mice were analyzed by LSC after the combustion with a sample oxidizer of 50 to 400 mg homogenized tissue samples in triplicate.
Results and discussion
Main ADME results
- Type:
- distribution
- Results:
- In rats, excluding the gastro-intestinal tract, concentration of radiolabel at any time-point was highest in the liver. As mice, in contrast to rats, do have a gall-bladder this organ was also included. It
showed by far the highest concentration.
Toxicokinetic / pharmacokinetic studies
- Details on distribution in tissues:
- In male rats administered [14C-phenyl]pencycuron, total radiolabel in tissues and organs, excluding the gastro-intestinal tract, peaked three hours after administration at 1.8% of the administered radiolabel. Thereafter, it steadily declined to 0.09% seven days after administration. No such data were presented for other treated groups. No remarkable differences in distribution of radiolabel in male rats were found between administration 14C-phenyl- and 14C-carbonyl labelled pencycuron. For female rats only results of administration of 14C-carbonyl-labelled pencycuron were presented. Both in male and female rats the concentration of radiolabel in tissues and organs, excluding the gastro-intestinal tract, peaked between 3 to 8 hours after administration. Thereafter levels steadily declined. In rats, excluding the gastro-intestinal tract, concentration of radiolabel at any time-point was highest in the liver. For example, three days after administration, concentration of radioactivity in the liver was ca. 1.3 mg eq./kg, while in the other tissue, excluding the gastro-intestinal tract, concentrations were at least 2 times lower. Male mice showed similar patterns after oral administration of 14C-phenyl-labelled pencycuron. As mice, in contrast to rats, do have a gall-bladder this organ was also included. It showed by far the highest concentration of all tissues, with a residual peak 8 h after administration when it was ca. 85 times higher than in the liver.
Metabolite characterisation studies
- Metabolites identified:
- no
Applicant's summary and conclusion
- Conclusions:
- Administration of carbonyl labeled 14C-pencycuron observed the excretion patterns approximately similar to those obtained with phenyl labeled chemical. Significant difference in the residual concentration of radiocarbon was not observed between male and female rats. No accumulation of 14C-pencycuron in the specific tissues of rat and mouse were presumed.
- Executive summary:
Male and female rats and male mice were administered orally with phenyl labeled 14C-pencycuron [1-(p chlorobenzyl)-1-cyclopentyl-3-phenyl urea] at the dosage level of 40 mg/Kg and the absorption, the distribution and the residue levels in the tissues and organs studied. The administered 14C-pencycuron was readily absorbed and distributed into various tissues. The radiocarbon in tissues was found shortly after the administration; liver, kidney, lung, adrenal and adipose contain large amount of radiocarbon, while brain, muscle and testis might contain less amount of radiocarbon. The half lives of animal body were in order of 13-27 hr (rat) and 6-16 hr (mouse). In addition, administration of carbonyl labeled 14C-pencycuron observed the excretion patterns approximately similar to those obtained with phenyl labeled chemical. Significant difference in the residual concentration of radiocarbon was not observed between male and female rats. No accumulation of 14C-pencycuron in the specific tissues of rat and mouse were presumed. The high residue concentration observed in the gall-bladder of mouse was suggested to be due to active biliary excretion.
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