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EC number: 201-174-2 | CAS number: 79-07-2
- 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
Dermal absorption
Administrative data
- Endpoint:
- dermal absorption in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1985
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The dermal route is relevant for human exposure; current study can add valuable information on absorption, distribution and excretion.
Cross-reference
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 985
- Report date:
- 1985
Materials and methods
- Principles of method if other than guideline:
- 14C analysis: absorption, elimination, residues of 14C-chloroacetamide following dermal application
Test material
- Reference substance name:
- 2-chloroacetamide
- EC Number:
- 201-174-2
- EC Name:
- 2-chloroacetamide
- Cas Number:
- 79-07-2
- Molecular formula:
- C2H4ClNO
- IUPAC Name:
- 2-chloroacetamide
- Details on test material:
- Own synthesis of lots RCL-No. 12059 I, 4.5 GBq/g (121 mCi/g) & No. 12059 II, 1.7 GBq/g (46.6 mCi/g); melting points 120°C.
Identity established by IR spectra in comparison to unlabelled standard.
Radiochemical purity >= 98% established by TLC & radioactivity scans.
Synthesis based on Ba 14C-Carbonat using a Grignard reaction to form 14C-acetic acid, chlorination, methylation & preparative
GLC to obtain 14C- methyl monochloroacetate, amidation to 14C-chloroacetamide,
purification by sublimation under reduced pressure.
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- 1C-C14
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Healthy male SPF-Wistar rats (stock: Winkelmann, Kirchborchen, Germany)
weight range: 190 – 280 g
Temperature 21+- 1 °C, relative humidity 45-55 %; single cages (excretions, autoradiography) or cages for two animals (blood
levels, exhalation) with separation devices for urine and faces collection. Feed (Altromin(R) 1324, milled, from Altrogge,
Lage/Lippe, Germany) & drinking water ad libitum.
Administration / exposure
- Type of coverage:
- occlusive
- Vehicle:
- water
- Duration of exposure:
- 6 h
- Doses:
- 2.9 or 6.2 mg/mL solution - 2 mg/kg bw
- No. of animals per group:
- 5
- Details on study design:
- A 1 mL tuberculin syringe was used. The calculated application volume was given dropwise to & distributed evenly on the shaven skin area.
After 6 h, the application area was cleaned several times with a wet swap. The latter had been wettened with tap water & some drops of a tenside .(pricol(R), Henkel, Düsseldorf, Germany).
Results and discussion
- Signs and symptoms of toxicity:
- not examined
- Dermal irritation:
- not examined
- Total recovery:
- 77.5 +- 5.0 %
Percutaneous absorption
- Parameter:
- percentage
- Absorption:
- 14 - 39 %
- Remarks on result:
- other: 6 h p.appl
Any other information on results incl. tables
Max. blood concentrations of 0.58 +- 0.22 µg equivalent/ml between 2 and 6 h ( 4.4 +- 1.7 h) p. appl.
2-phase elimination from the blood with half-lives of 5.7+-2.1 h (2-8h p. appl.) and 180+-35 h (up to 5 d p. appl.)
Applicant's summary and conclusion
- Conclusions:
- After dermal administration, maximal plasma levels were observed between 2 and 6 hrs after application. Two elimination half-lives of approximately 6 and 180 hrs were determined for blood. Within 24 hrs, 43% of the administered radioactivity was excreted via
urine, whereas 0.7% of the administered radioactivity was excreted via faeces. At study termination after 24 hrs radioactivity (33% of the applied amount) was still present in organs, tissues, site of application and remaining body. Autoradiography revealed that radioactivity was present in blood, liver, kidneys and also in skin areas that had not been treated. At study termination, 43.4% and 0.68% of the applied radioactivity had been excreted via urine and faeces, respectively. 11.8% of the applied radioactivity was determined in tissues and body compartments excluding treated skin areas, 21.1% of the applied radioactivity was detected in skin of the application site. In total, 77.5% of the applied radioactivity was recovered. Thus, from the percentages of radioactivity excreted and radioactivity present in body compartments different from the application site, 56% of the applied radioactivity is taken as amount absorbed. - Executive summary:
Groups of animals received single doses of (1-14C)-chloroacteamide by the dermal pathway (onto shaved skin of the back; oral intake from treated skin was prevented by fixing a vessel onto the treated skin area). Treated skin areas were washed of 6 hrs after substance administration. Parameters studied were absorption (blood analysis), tissue distribution and excretion in urine and faeces. Termination was after 24 hrs for dermal application. Radioactivity was determined by liquid scintillation and whole-body autoradiography.
After dermal administration, maximal plasma levels were observed between 2 and 6 hrs after application. Two elimination half-lives of approximately 6 and 180 hrs were determined for blood. Within 24 hrs, 43% of the administered radioactivity was excreted via urine, whereas 0.7% of the administered radioactivity was excreted via faeces. At study termination after 24 hrs radioactivity (33% of the applied amount) was still present in organs, tissues, site of application and remaining body. Autoradiography revealed that radioactivity was present in blood, liver, kidneys and also in skin areas that had not been treated. However, at 6 hours there was also clear radioactivity in urinary tract, testes, lung and spleen. At study termination, 43.4% and 0.68% of the applied radioactivity had been excreted via urine and faeces, respectively. 11.8% of the applied radioactivity was determined in tissues and body compartments excluding treated skin areas, 21.1% of the applied radioactivity was detected in skin of the application site. In total, 77.5% of the applied radioactivity was recovered. Thus, from the percentages of radioactivity excreted and radioactivity present in body compartments different from the application site, 56% of the applied radioactivity is taken as amount absorbed.
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