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EC number: 200-578-6 | CAS number: 64-17-5
- 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

Respiratory sensitisation
Administrative data
- Endpoint:
- respiratory sensitisation: in vivo
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Published study that contains sufficient details to judge it reliable with restrictions.
Data source
Reference
- Reference Type:
- publication
- Title:
- Impact of emerging pollutants on pulmonary inflammation in asthmatic rats: ethanol vapors and agglomerated TiO2 nanoparticles.
- Author:
- Scarino A, Noël A, Renzi PM, Cloutier Y, Vincent R, Truchon G, Tardif R, Charbonneau M.
- Year:
- 2 012
- Bibliographic source:
- Inhalation Toxicol. 24(8): 528–538
Materials and methods
- Principles of method if other than guideline:
- To investigate if exposure to inhaled ethanol vapors can modulate the rat pulmonary inflammatory response resulting from an allergic asthmatic reaction in Brown Norway rats.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Ethanol
- EC Number:
- 200-578-6
- EC Name:
- Ethanol
- Cas Number:
- 64-17-5
- Molecular formula:
- C2H6O
- IUPAC Name:
- ethanol
- Test material form:
- liquid
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Brown Norway
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 6-8 weeks.
- Housing: Individually during exposure.
- No food or drink during exposure.
ENVIRONMENTAL CONDITIONS
- Photoperiod (hrs dark / hrs light): 12/12
Test system
- Route of induction exposure:
- inhalation
- Route of challenge exposure:
- inhalation
- Vehicle:
- unchanged (no vehicle)
- Concentration:
- 3000ppm
- No. of animals per dose:
- 8
- Details on study design:
- Chicken egg ovalbumin (OVA) was used to induce allergic asthma in two phases, i.e. sensitization and challenge. Animals were sensitized by s.c. injection of 1 mL solution containing 0.9% saline (w/v), 1 mg ovalbumin, and 3.5 mg aluminum hydroxide (adjuvant). Fourteen days later, animals were challenged for 15 min by inhalation with a freshly prepared 0.9% saline solution containing a specific OVA concentration. A compressor was used to vaporize OVA solution from the nebulizer to the cage (2 rats/exposure). OVA concentrations were selected to cause 30–40% of maximal pulmonary inflammation to leave sufficient capacity for enhancement of the effect in the presence of ethanol.
A. INDUCTION EXPOSURE
- No. of exposures:1
- Site: sub cutaneous
Ethanol exposure:
- Whole body inhalation exposure, 500L chamber. Concentration monitored (GC) every 10 mins.
- 6hrs/day for at least 22 days.
B. CHALLENGE EXPOSURE
- No. of exposures: 1
- Day(s) of challenge: 14
- Site: inhalation
- Bronchiolar lavage was performed in different groups of rats at 6, 24, 36, 48, and 72 h following OVA challenge, always immediately after the last ethanol exposure. Fixed white blood cells (WBC) were mixed 1:1 with methylene blue and then counted using a hemacytometer. The plasma concentrations of seven cytokines relevant to asthma inflammation (MCP-1, IL-1β, IL-4, IL-6, IL-10, INF-γ, and TNF-α)were measured using a cytokine kit). Lung histology was performed.
Results and discussion
- Results:
- Exposure to ethanol did not significantly affect leukocytes present in bronchiolar lavage after OVA challenge.
Applicant's summary and conclusion
- Interpretation of results:
- not sensitising
- Executive summary:
A study was carried out to investigate if exposure to inhaled ethanol can modulate the rat pulmonary inflammatory response resulting from an allergic asthmatic reaction. Brown Norway rats were sensitized and challenged (15 min inhalation, 14 days later) with chicken egg ovalbumin (OVA). Leukocytes were counted in bronchoalveolar lavages (BAL) performed at 6, 24, 36, 48 and 72 h following the challenge and after ethanol exposures (3000 ppm, 6 h/day, daily). Exposure to ethanol did not significantly affect BAL leukocytes after OVA challenge leading to the conclusion that allergic pulmonary inflammation is not up-regulated by inhalation of ethanol.
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