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Diss Factsheets
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EC number: 231-209-7 | CAS number: 7446-81-3
- 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 in vivo
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 995
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 993
- Report date:
- 1993
Materials and methods
- Objective of study:
- toxicokinetics
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Disposition and metabolism of Acrylic acid (AA) in C3H mice after single cutaneous administration.
- GLP compliance:
- yes
Test material
- Reference substance name:
- Acrylic acid
- EC Number:
- 201-177-9
- EC Name:
- Acrylic acid
- Cas Number:
- 79-10-7
- Molecular formula:
- C3H4O2
- IUPAC Name:
- acrylic acid
- Details on test material:
- - Name of test material (as cited in study report): Acrylic acid
- Analytical purity: > 98 % (unlabeled AA)
- Supplier: Union Carbide Corporation
- Radiochemical purity (if radiolabelling): >= 98.6 %
- Specific activity (if radiolabelling): 0.14 - 0.4 mCi/mmol
- Locations of the label (if radiolabelling): [1-14C]AA
- Supplier: Sigma Chemical Co. (St. Louis, Mo.)
Constituent 1
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): Acrylic acid
- Analytical purity: > 98 % (unlabeled AA)
- Supplier: Union Carbide Corporation
- Radiochemical purity (if radiolabelling): >= 98.6 %
- Specific activity (if radiolabelling): 0.14 - 0.4 mCi/mmol
- Locations of the label (if radiolabelling): [1-14C]AA
- Supplier: Sigma Chemical Co. (St. Louis, Mo.) - Radiolabelling:
- yes
Test animals
- Species:
- mouse
- Strain:
- C3H
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories (Kingston, NY)
- Substrain: C3H/HeNCrlBR
- Age at study initiation: approx. 35 d old
- Weight at study initiation: 21 g
- Diet (ad libitum): Agway Prolab Diet Mouse, Agway Inc., Syracuse, NY
- Water (ad libitum)
Administration / exposure
- Route of administration:
- dermal
- Vehicle:
- acetone
- Details on exposure:
- TEST SITE
- Area of exposure: 1.0 X 1.0 cm
- Type of wrap if used: nonocclusive dose containment devices constructed from Stomahesive and cemented to the skin with Skin-Bond
- Time intervals for shavings or clipplings: prior to application
REMOVAL OF TEST SUBSTANCE
- Washing (if done): at the end of experiment to remove the unabsorbed portion of the dose
TEST MATERIAL
- concentration (if solution): 1 mL test AA/100 mL acetone
VEHICLE
- Amount(s) applied (volume or weight with unit): 0.95 and 3.8 mL/kg bw, respectively - Duration and frequency of treatment / exposure:
- 72 hrs
Doses / concentrationsopen allclose all
- Dose / conc.:
- 10 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 40 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose / concentration:
- 15
- Control animals:
- no
- Details on study design:
- - Dose selection rationale: The cutaneous dose levels were selected based on previous work on the cutaneous toxicity of AA in several strains of mice (DePass et al. 1984, Tegeris et al. 1988).
- Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: urine, faeces, blood, plasma, stomach contents (after sacrifice)
- Time and frequency of sampling: Urine was collected under dry ice and faeces were collected at room temperature at 8, 24, 48, and 72 h. At 1 and 8 hrs, 5 animals from ech group were sacrificed and blood samples collected. Tissues were sampled at termination (liver, kidney, fat, stomach).
- Traps for volatile compounds:
Room air was drawn through the metabolism cages at a rate of approximately 350 mL/min. Expired 14CO2 was collected in traps containing a solution of 2-methoxyethanol : ethanolamine (7:3, v/v), which was replaced with fresh solution at regular intervals. Other exhaled volatile 14C-labeled organic compounds were collected onto activated charcoal traps (approximately 4 g) placed in series ahead of the 14CO2 traps. In addition to the in-line volatile organics trap, the dose-containment device was modified by cementing activated charcoal-impregnated filter paper sheets to the top of the frame in order to trap the volatile fraction of the applied dose at the dosing site.
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- After cutaneous administration of single doses (40 or 10 mg/kg bw) to C3H mice, the processes of AA absorption and elimination were rapid and nearly complete within 8 h. Evaporation from the dosing site accounted for the largest fraction of the applied dose, although total recovery of the dose was variable. After 40 mg/kg bw, 11.4 ± 1.7% (mean t ± SD, n= 5) of the dose was absorbed (sum of cumulative proportions exhaled as 14CO2 or excreted in urine or faeces and the proportions found in dosing site skin, tissues, and carcass at 72 h), and after 10 mg/kg bw, 12.4 ± 3.3% was absorbed. Metabolism to 14CO2 was the major route of elimination, accounting for 83.5 ± 8.4% and 77.7 ± 10.4% of the absorbed dose after the high and low dose, respectively. Elimination via other routes was minor.
- Details on distribution in tissues:
- At the end of the experiment, 0.2-1.5% of the dose was found in the dosing site skin, and about 1% was found in tissues and carcass. Exhalation of volatile organic compounds other than 14CO2 was not quantified separately but was presumed to be negligible based on the results from orally dosed animals. Elimination of radioactivity from the dosing site skin, plasma, liver, and kidney was rapid. The concentration of radioactivity found in fat at 72 h was greater than that found at 1 or 8 h.
Metabolite characterisation studies
- Metabolites identified:
- no
- Details on metabolites:
- Neither AA nor its metabolites were detected in livers from mice at any time after cutaneous administration of 40 mg/kg bw.
Any other information on results incl. tables
Disposition of radioactivity in C3H mice after cutaneous administration of [1 -14C]AA:
Dose |
||
40 mg/kg bw |
10 mg/kg bw |
|
14CO2 |
9.6 ± 2.2 |
9.3 ± 1.2 |
Volatilized dose |
49.9 ± 12.6 |
70.9 ± 9.6 |
Urine |
0.4 ± 0.1 |
0.3 ± 0.1 |
Faeces |
0.2 ± 0.1 |
0.4 ± 0.1 |
Cage wash |
0.2 ± 0.1 |
0.2 ± 0.1 |
Tissues |
0.0 ± 0.0 |
0.2 ± 0.1 |
Carcass |
0.8 ± 0.8 |
0.5 ± 0.1 |
Dosing-site skin |
0.2 ± 0.1 |
1.5 ± 2.3 |
Skin rinse |
0.2 ± 0.1 |
0.6 ± 0.3 |
Total recovery |
61.5 ± 14.0 |
84.0 ± 10.5 |
The less than complete recovery of the administered doses is probably explained by the volatile nature of acrylic acid and its propensity to bind to materials such as plastic and glass, properties that may also be shared by some of the metabolites of acrylic acid.
Applicant's summary and conclusion
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.
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