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EC number: 201-956-3 | CAS number: 89-98-5
- 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:
- key study
- Study period:
- year of publication: 1988
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Sufficently documented literature data
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Percutaneous absorption of 14C-labelled 2-chlorobenzaldehyde in rats. Metabolism and toxicokinetics.
- Author:
- Rietveld EC, Hoet RMA, Seutter-Berlage F, van Rossum JM
- Year:
- 1 988
- Bibliographic source:
- European Journal of Drug Metabolism and Pharmacokinetics 13: 231-240
Materials and methods
- Objective of study:
- metabolism
- Principles of method if other than guideline:
- investigation of metabolism in vivo
- GLP compliance:
- not specified
Test material
- Reference substance name:
- 2-chlorobenzaldehyde
- EC Number:
- 201-956-3
- EC Name:
- 2-chlorobenzaldehyde
- Cas Number:
- 89-98-5
- Molecular formula:
- C7H5ClO
- IUPAC Name:
- 2-chlorobenzaldehyde
- Details on test material:
- - Name of test material (as cited in study report): 2-chlorobenzaldehyde
- Radiochemical purity (if radiolabelling): at least 98%
- Specific activity (if radiolabelling): 20 mCi/mmol; reduced to 0.275 mCi/mmol by addition of pure unlabelled material
- Locations of the label (if radiolabelling): carbonyl-group
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- 2-Chloro(carbonyl-14C)benzaldehyde
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- - Source: TNO, Zeist (The Netherlands)
- Age at study initiation: about 6 weeks
- Individual metabolism cages: yes
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: at least three days prior to experiments rats were housed in individual glass metabolism cages
- Air was drawn through the metabolism cage (volume 24 l) at a rate of 400 ml/min; pressure inside the cage was somewhat lower than outside
- polyethylene catheters (I.D. 0.4 mmmm; O.D. 0.8 mm) were placed into the femoral artery and the jugular vein and led subcutaneously to the nuchal area where they went out of the body
Administration / exposure
- Route of administration:
- other: dermal, intravenous, intraperitoneal
- Vehicle:
- water
- Details on exposure:
- DERMAL EXPOSURE:
Preparation of dose:
- radiolabelled substance was pipetted undiluted in the cup, which was closed immediatly afterwards with a glass cover using the cyanoacrylate adhesive
TEST SITE
- Preparation of test site: shaved, 16 hours before application
- Area of exposure: right dorsal skin,
- Type of cover: with a glass cup (I.D. 16 mm, O.D. 24 mm, height: 10 mm) which was fixed to the skin with cyanoacrylate adhesive; the cup was glued in such a way that no contact between the glass or the adhesive with the treated skin was possible.
SITE PROTECTION / USE OF RESTRAINERS FOR PREVENTING INGESTION: yes: glass cup
REMOVAL OF TEST SUBSTANCE
- Washing procedures and type of cleansing agent: the glass was rinsed with methanol
- exposed skin was widely excised, cut into small pieces and solubilized bevor counting of radioactivity
SAMPLE COLLECTION
- Collection of blood: from femural artery
- Collection of urine and faeces: urine was colleted for 72 hours after the administration; faeces was collected at daily intervals
INTRAVENOUS AND INTRAPERITONEAL EXPOSURE:
25 µl/kg bw of the radiolabelled test substance (specific radioactivity 1.83 mCi/ml dissolved in 1 ml of 2% aqueous solution of Tween-60) were injected into the jugular vein catheter, duration about 4 minutes; 37.5 µl/kg were applied intraperitoneally. - Duration and frequency of treatment / exposure:
- 72 hours (dermal application)
single exposure (i.v. and i.p. application)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
75 µl/kg (dermal application)
25 µl/kg (i.v. application)
37.5 µl/kg (i.p. application)
- No. of animals per sex per dose / concentration:
- 8 (dermal application),
6 (i.v. application),
2 (i.p application) - Control animals:
- no
- Positive control reference chemical:
- none
- Details on dosing and sampling:
-
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine
- Time and frequency of sampling: dermal application: 0-12 h, 12-24 h, 24-48 h, 48-72 h; i.v. and i.p. application: 0-6 h, 6-24 h
- From how many animals: no data
- Method type(s) for identification: thin layer chromatography
- Limits of detection and quantification: no data
Results and discussion
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- More than 95% of the radioactivity in the urine was ethyl acetate extractable. Metabolic patterns of urinary excreted metabolites of the test item were quite similar after dermal, i.v. and i.p. application, apart from some quantitative differences. None 14C-2-chlorobenzaldehyde was identified in the urine. 2-Chlorohippuric acid was the main metabolite excreted (about 65% to 75% depending on the application route). Additionally, 2-chlorobenzylmercapturic acid, 2-chlorobenzoic acid and 2-chlorobenzyl alcohol were identified as urinary metabolites. 14C-2-chlorobenzyl alcohol was mostly excreted in the urine collected on the second day (24-48 h) of cutaneously treated rats. This metabolite was found in much smaller amounts in the urin of rats which were treated i.v. or i.p. 2-Chlorobenzyl alcohol and 2-chlorobenzoic acid accounted for abour 15% of the total urinary radioactivity.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results concluded by supplier
2-Chlorobenzaldehyde is extensively metabolised in rats. 2-Chlorohippuric acid is the main metabolite. 2-Chlorobenzyl alcohol, 2-chlorbenzoic acid and 2-chlorobenzylmercapturic acid were identified as further metabolites. No unchanged compound was identified in the urine. - Executive summary:
Urinary metabolites of 14C-2-chlorobenzaldehyde were identified in rats treated percutaneously, intravenously or intraperitoneally. The principal metabolite in rat urine was 2-chlorohippuric acid. Additionally, 2-chlorobenzyl alcohol, 2-chlorobenzoic acid, which accounted for about 15% of urinary radioactivity, and 2-chlorobenzylmercapturic acid were identified in the urine by means of thin layer chromatography. No unchanged compound was detected in the urine.
The study has been judged to be reliable with restrictions (RL2). It was selected as key study.
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