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EC number: 216-913-4 | CAS number: 1696-20-4
- 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)
Description of key information
High oral and inhalation absorption is assumed. Dermal absorption is suspected to be low, but was conservatively assumed to be half of the oral/inhalation absorption. A wide distribution throughout the body is likely. An accumulation potential is not expected. Metabolism might play a minor role. Renal excretion is considered as most relevant.
Key value for chemical safety assessment
Additional information
Phys-chem properties relevant for toxicokinetic assessment
The non-aromatic O-heterocyclic compound 4-acetylmorpholine (CAS-No. 1696-20-4, MW 129.16 g/mol) is a colourless to yellowish, slightly odoured organic liquid. 4-Acetylmorpholine is completely water soluble and has a partition coefficient Log Pow of -0.81 (24°C). 4-acetylmorpholine has a vapor pressure of 0.022 hPa at 20°C. Exposure to 4-acetylmorpholine may occur through inhalation and dermal contact at workplaces where 4-acetylmorpholine is produced or used.
Toxicokinetic Analysis of 4 -acetylmorpholine
Oral absorption
Administered orally it can be assumed that the test item is well absorbed in the gastrointestinal (GI) tract after dissolving in GI fluids due to its low molecular weight, the high water solubility, the low Log Pow of -0.81 and the absence of ionisable groups in the 4-acetylmorpholine molecule at pH values of small intestine. These substance characteristics favour the absorption via passive diffusion, e.g. by passage through aqueous pores or carriage through the epithelial barrier with the bulk passage of water. The systemic effects seen after oral administration demonstrate that the test item is absorbed from the GI tract.
Dermal absorption
As 4-acetylmorpholine is a liquid which completely dissolves in water and has a Log Pow of -0.81, it can be assumed that dermal absorption is significantly lower than oral absorption. This is also indicated by a very low percutaneous permeability coefficient Kp of 0.0000855 cm/hr (calculated with Epi Suite, Dermwin). Conservatively, dermal absorption is assumed to be 50% of the oral absorption.
Respiratory absorption
The test item is a liquid exhibiting low volatility due to a low vapor pressure (< 0.5 kPa) and a high boiling point (> 150°C). Therefore only a minimal amount of the substance is available for inhalation. Based on the aforementioned physico-chemical properties (see “oral absorption”), an absorption rate similar to the oral absorption is expected.
Distribution and metabolism
Since the 4-acetylmorpholine molecule is relative small, completely water soluble and has a negative Log Pow value, a wide distribution throughout the body is likely to occur after absorption. Based on the physico-chemical characteristics, particularly the high water solubility and Log Pow value below 0, long biological half-life of 4-acetylmorpholine in tissues can not be expected, thus it has no accumulation potential. The metabolism itself is determined by physico-chemical factors like electronic and steric effects within the molecule (Karcher W & Devillers J, 1990). Since 4 -acetylmorpholine is already highly water soluble, metabolism might play a minor role. This is supported by metabolism data on morpholine, which showed that Morpholine is eliminated mainly in a non-metabolized form in the urine of the rat, mouse, hamster and rabbit (Griffiths, 1968; Tanaka et al., 1978; Van Stee et al., 1981; Sohn et al., 1982).
Excretion
The high water solubility and low molecular weight (< 400) indicate that renal excretion is the most relevant route of systemically available 4-acetylmorpholine.
References
Karcher W & Devillers J (eds.) (1990): Practical Applications of Quantitative Structure-Activity Relationships (QSAR) in Environmental Chemistry and Toxicology.Chemical and Environmental Science Series, Vol. 1.
Griffiths MH (1968). The metabolism of N-triphenylmethylmorpholine in the dog and rat. Biochem. J., 108: 731-740.
Tanaka A et al. (1978). Excretion and Distribution of Morpholine Salts in Rats. J. Food Hygienic Soc. 19: 329-334.
Van Stee EW, Wynns PC and Moorman MP (1981). Distribution and disposition of Morpholine in the rabbit. Toxicology 20: 53-60.
Sohn OS et al.(1982). Metabolism and Disposition of Morpholine in the Rat, Hamster and Guinea Pig. Toxicol. Appl. Pharmacol. 64: 486-491.
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