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EC number: 209-940-8 | CAS number: 598-56-1
- 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:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Effect of dietary intake of trimethylamine on human metabolism of the industrial catalyst dimethylethylamine
- Author:
- Lundh T, Akesson B, Skerfving S
- Year:
- 1 995
- Bibliographic source:
- Occup Environ Med. 52(7):478-83.
Materials and methods
- Objective of study:
- metabolism
- Principles of method if other than guideline:
- metabolism of dimethylethylamine (DMEA) in human
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Ethyldimethylamine
- EC Number:
- 209-940-8
- EC Name:
- Ethyldimethylamine
- Cas Number:
- 598-56-1
- Molecular formula:
- C4H11N
- IUPAC Name:
- ethyldimethylamine
- Details on test material:
- - Name of test material (as cited in study report): DMEA
- Supplier: Janssen Chemical, Geel, Belgium
Constituent 1
- Radiolabelling:
- no
Test animals
- Species:
- human
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- The participants were five healthy male volunteers (subjects A, B, C, D, and E), mean age 40 (range 25-55) years, body weight 81 (70-88) kg, and height 1.81 (1.75-1.91) m, all non-smokers. They were instructed not to eat fish or drink alcohol during the 24 hour period preceding the experiments, and to fast overnight (> 8 hours) before being given the amines.
The study design was approved by the ethics committee of Lund University, and all five subjects gave their informed consent to participate in the study.
Administration / exposure
- Route of administration:
- oral: drinking water
- Vehicle:
- water
- Duration and frequency of treatment / exposure:
- once a week for six weeks
Doses / concentrations
- Remarks:
- Doses / Concentrations:
25 mg, pH adjusted to 7
- No. of animals per sex per dose / concentration:
- 5 volunteers
- Control animals:
- no
- Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: blood samples (20 ml) were collected by venepuncture,
- Time and frequency of sampling: before and one hour after the doses of amines
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine was collected in polyethylene bottles,
- Time and frequency of sampling: before the start of the experiments, and 2, 4, 6, 8, and 24 hours after the doses of amines
- From how many persons: 5
- Method type(s) for identification: GC
Results and discussion
- Preliminary studies:
- Before amines were given, the median plasma concentrations of TMA and TMAO were 11 and 32 µmol/l, respectively. There were only minor
variations within and between the volunteers in the TMA concentrations (range 6-15 µmol/l). The range of TMAO concen trations was wider, 4-97 µmol/l, corresponding to TMAO fractions of 20% to 91% (median 72%). In all experiments the plasma DMA concentration was below the detection limit of our method (0·6 µmol/l). Neither DMEA nor DMEAO were found in plasma or in urine collected before the experiments, or in the
experiments where no DMEA was given. One hour after the start of control experiments without amines, the median plasma concentrations of TMA and TMAO were about the same as the baseline values (11 and 9 µmol/l, respectively; table 1). The median TMAO fraction was 50%. Median 24 hour urinary excretions of TMA and TMAO were 3·4 and 390 µmol, respectively, the TMAO fraction being 99%. There were only minor variations within and between the volunteers in urinary excretion of TMA and TMAO during the four two-hour periods with standardised diet and in the eight to 24 hour period (table 1).
Main ADME resultsopen allclose all
- Type:
- distribution
- Results:
- The median plasma DMEAO concentration was 1 µmol/l, and the DMEAO fraction 100%.
- Type:
- excretion
- Results:
- Median urinary excretion (0-24 hours) of DMEA was 1 0 µmol and that of DMEAO 275 µmol/l. 81% of the dose was excreted in urine
- Type:
- excretion
- Results:
- During the period, two to eight hours after the dose of DMEA, the half lives were 1.2-2.0 hours for DMEA, and 2.7-3.5 hours for DMEAO
- Type:
- excretion
- Results:
- Urinary DMA excretion to have increased during the first two-hour period after the dose from 0.7 to 5.6 µmol for 25 mg of DMEA
Toxicokinetic / pharmacokinetic studies
- Details on distribution in tissues:
- In only one subject (A), did the plasma DMEA concentration at one hour after the dose of DMEA exceed the detection limit of 0.04 µmol/l (table 1). The median plasma DMEAO concentration was 11 µmol/l and the DMEAO fraction 100%.
- Details on excretion:
- Median urinary excretion (0-24 hours) of DMEA was 1.0 µmol and that of DMEAO 275 µmol. The median Sum-DMEA value represented 81% of the DMEA dose given (table 2). The DMEAO fraction was 100% in all cases except subject A, where it was 1-2% lower.
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- Dimethylethylamineoxide (DMEAO)
Applicant's summary and conclusion
- Executive summary:
DMEA (0/25 mg) was given once weekly for six weeks to five healthy volunteers. Plasma was collected before and one hour after the doses, and urine 0-2, 2-4, 4-6, 6-8, and 8-24 hours after the doses. Specimens were analysed by gas chromatography with a nitrogen sensitive detector. DMEA was readily absorbed from the gastrointestinal tract and excreted in urine within 24 hours (81%) (Lundh et al., 1995).
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