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EC number: 205-153-9 | CAS number: 134-71-4
- 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
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
Additional information
Two articles are available on the metabolism of the test substance.
In the article by Feller et al. (1977) investigations were carried out with radiolabeled D(-)-ephedrine and L(+)-ephedrine to establish whether differences exist in their metabolic fate in the rabbit, in vivo and in vitro. In liver microsomal preparations, D(-)-ephedrine was metabolized at a faster rate than L(+)-ephedrine, benzoic acid was formed from D(-)-ephedrine at a rate about three times greater than from the L(+)-isomer, and the relative amounts of norephedrine and 1-phenyl-1,2-propranediol formed from both ephedrine isomers were nearly identical throughout the entire incubation period. In vivo, both ephedrine isomers were extensively metabolized and the majority of total radioactivity(71-91%) was excreted within 24 hr. 47-50% of the urinary 14C was attributable to hippuric acid and benzoic acid from L(+)- and D(-)-ephedrine, from 4 to 16% of the total 14C obtained with both isomers was accountable as 1-phenyl-1,2-propanediol, either free or as a glucuronide conjugate, no appreciable quantities of sulfate or glucuronide conjugates of p-hydroxylated metabolites of ephedrine or norephedrine was detectable, and small amounts (<4% of metabolites corresponding to unchanged ephedrine, norephedrine, or 1-hydroxy-l-phenyl-2- propanone were found in urine of animals given either isomer. These experiments indicate that the major pathway for the biotransformation of D(-)-ephedrine and L(+)-ephedrine involves N-demethylation and oxidative deamination of the side chain.
In the article by Inoue et al. (1990) urinary metabolites of methylephedrine and their excretion after oral administration to rat and human volunteers have been studied. The unchanged drug, ephedrine, norephedrine, their aromatic hydroxylated compounds and methylephedrine N-oxide were found in rat urine. The same metabolites, except the p-hydroxylated metabolites, were detected in human urine. The most abundant metabolite in rat urine was methylephedrine N-oxide, and in human urine was the unchanged drug. Metabolites excreted in three days after administration of the drug to rat amounted to about 54% of the dose and those after administration to man, 70-72%.
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