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Diss Factsheets
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EC number: 233-912-4 | CAS number: 10431-98-8
- 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
Endpoint summary
Administrative data
Link to relevant study record(s)
- Endpoint:
- basic toxicokinetics in vivo
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Reference
Description of key information
Based on considerations of the physicochemical properties and the toxicologically insignificant gross pathological findings following acute exposure 2-ethyl-2-oxazoline would be expected to be absorbed following oral, dermal and inhalation exposure. Conservative absorption rates for this substance are set at 100% for all routes of exposure.
Gross pathological observations and the physicochemical properties of the substance suggest that there will be distribution of the substance throughout the body. The substance is expected to rapidly transform via hydrolysis and metabolism to its aliphatic amine and corresponding fatty acid components. Ultimately the majority of excretion is expected to be urinary but might also be faecal following oral dosing. Based on the available data, in particular the log P value of 0.198, the water solubility of >97.87 g/L, the substance is expected to have a no potential to bioaccumulate.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
- Absorption rate - oral (%):
- 100
- Absorption rate - dermal (%):
- 100
- Absorption rate - inhalation (%):
- 100
Additional information
To date, no relevant analytical toxicokinetic testing data has been generated for 2-ethyl-2-oxazoline. However, toxicological information following oral, dermal, and inhalation exposure of 2-ethyl-2-oxazoline and information on the physicochemical properties can be used as a basis for the assessment of toxicokinetics.
Absorption
The diffusion of a substance across biological membranes in a test species is governed by the physicochemical properties of the substance, particularly its molecular size, Log P, and water solubility (ECHA, 2017).
Oral
Due to its small molecular size of 99 g/mol, very hydrophilic nature with a water solubility of >97.87 g/L and a Log P of 0.198 there is the possibility of passive absorption of 2-ethyl-2-oxazoline following oral exposure through aqueous pores or through the epithelial barrier by bulk transport of water. Following oral exposure, 2-ethyl-2-oxazoline is expected to undergo hydrolysis to 2 -aminoethanol and propionic acid; as these products of hydrolysis are smaller molecules, have similar water solubility and Log P values, they too are anticipated to be passively absorbed.
There are two acute oral studies included within this REACH dossier. Both indicate the substance may be harmful is swallowed (LD50 > 2000 mg/kg bw and less than 5000 mg/kg bw). While no toxicologically significant effects were reported during the gross pathological investigations, one study reported pale kidneys and the other pale livers in the mid to high dose level groups. These pathological findings suggest systemic absorption followed oral exposure. Based on a consideration of the substance’s physicochemical properties and the available oral toxicity studies, a conservative default value for oral absorption of the substance is set as 100%.
Inhalation
The low measured vapour pressure (1.31 kPa at 37.8°C) and measured boiling point (131°C) of the substance would suggest it possesses moderate to low volatility and thus likely not readily available for inhalation as a vapour. However, the hydrophilic nature of the substance (low Log P value, high water solubility) would suggest it is favourable for absorption directly across the respiratory tract epithelium by passive diffusion. 2-Ethyl-2-oxazoline is expected to undergo hydrolysis to 2-aminoethanol and propionic acid; as these products of hydrolysis are smaller molecules, have similar water solubility and Log P values, they too are anticipated to be passively absorbed.
While the available acute inhalation toxicity study in rats indicated a low acute vapour inhalation toxicity value (7h LC50 > 635 ppm) and no toxicologically significant gross pathological findings were report, the kidneys were described as pale. These pathological findings suggest systemic absorption followed inhalation exposure. Based on a consideration of the physicochemical properties and the available oral and inhalation toxicity studies, a conservative default value for inhalation absorption of the substance is set as 100%.
Dermal
The very hydrophilic nature of the substance would suggest that 2-ethyl-2-oxazoline would not cross the lipid rich environment of the stratum corneum. However, 2-ethyl-2-oxazoline is CLP classified as a Category 1B Skin Corrosive substance. Dermal exposure to the substance could damage the lipid rich stratum corneum allowing for passive diffusion directly through the epidermis.
An acute dermal toxicity study with a 10% aqueous solution of 2-ethyl-2-oxazoline supports the assumption of passive diffusion through damaged skin as deaths were reported in following exposure of animals with abraded skin while no deaths were reported following exposure of animals with unabraded skin. Based on a consideration of the substance’s physicochemical properties and the results of the available skin toxicity study, a conservative value of 100% skin absorption is chosen.
Distribution
As 2-ethyl-2-oxazoline is a small water-soluble molecule it is anticipated to diffuse through the aqueous channels and pores of cellular membranes following absorption. While there were no toxicologically significant gross pathological findings following oral and inhalation exposure; the reports of pale liver and/or kidneys support distribution throughout the animal system. No significant signs of systemic toxicity were reported following dermal exposure with animals with unabraded skin while deaths were reported in animals with abraded skin. The findings reported following acute exposure suggest that the substance dose distribute in animal systems.
Metabolism
The substance is expected to undergo initial hydrolysis into its secondary amide which will then be metabolized by amidase enzymes such as fatty acid amide hydrolase (FAAH) [Fiume, et al., 2015] into its aliphatic amine (ethanolamine) and corresponding fatty acid (propionic acid) components. FAAH, an enzyme responsible for the hydrolysis of a number of primary and secondary fatty acid amides, is widely distributed throughout the human body.
Excretion
Following metabolism to the aliphatic amine and corresponding fatty acid, ultimate excretion is expected to be primarily urinary, although a minor amount of faecal excretion may also occur following oral dosing.
Based on the available data, in particular the log P value and high water solubility the substance is expected to have a no potential to bioaccumulate in animals and humans.
References
ECHA (2017). Guidance on information requirements and chemical safety assessment. Chapter R.7c: Endpoint specific guidance. Volume 3.0, July 2017. Available at:https://echa.europa.eu/documents/10162/13632/information_requirements_r7c_en.pdf/e2e23a98-adb2-4573-b450 -cc0dfa7988e5
Fiume, M.M., Heldreth, B.A., Bergfeld, W.F., Belsito, D.V., Hill, R.A., Klaassen, C.D., Liebler, D.C., Marks Jr, J.G., Shank, R.C., Slaga, T.J. and Snyder, P.W., 2015. Safety Assessment of Ethanolamides as Used in Cosmetics. International journal of toxicology, 34(1_suppl), pp.18S-34S.
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