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Diss Factsheets
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EC number: 203-049-8 | CAS number: 102-71-6
- 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: Basic data given acceptable for assessment
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2004
- Reference Type:
- secondary source
- Title:
- Unnamed
- Year:
- 2 004
Materials and methods
- Principles of method if other than guideline:
- Groups of four female mice received a single intravenous dose of 3 mg/kg [14C]-triethanolamine. Expired radioactivity was trapped and quantitated and urine and feces were collected from all B6C3F1 mice dosed intravenously up to 72 hours after dosing. Tissue samples at 72 hours after dosing were also examined.
- GLP compliance:
- no
Test material
- Reference substance name:
- 2,2',2''-nitrilotriethanol
- EC Number:
- 203-049-8
- EC Name:
- 2,2',2''-nitrilotriethanol
- Cas Number:
- 102-71-6
- Molecular formula:
- C6H15NO3
- IUPAC Name:
- 2-[bis(2-hydroxyethyl)amino]ethan-1-ol
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- 14C
Test animals
- Species:
- mouse
- Strain:
- B6C3F1
- Sex:
- female
Administration / exposure
- Route of administration:
- intravenous
- Vehicle:
- acetone
- Details on exposure:
- Single intravenous doses contained approximately 6 μCi radiolabel for mice, an appropriate amount of nonradiolabeled triethanolamine, and isotonic saline as a vehicle that delivered a total dosing volume of 2 mL/kg to mice. Intravenous doses were drawn into a syringe equipped with a Teflon®-tipped plunger (Hamilton) and a 30 gauge hypodermic needle. Excess dose formulation was wiped off the needle before weighing the filled dosing syringe. Intravenous doses were injected into one lateral tail vein. After dosing, the needle was wiped clean with a Kimwipe®, and the empty syringe was reweighed. The Kimwipe® was placed into a vial containing 2 mL ethanol and analyzed by liquid scintillation spectrometry. Each dose was calculated as the difference between the weights of the filled and empty dosing apparatus less the amount found in the Kimwipe®. To determine the concentration of [14C]-triethanolamine in the dose formulation, two weighed aliquots were taken before, two after, and one during dosing.
- Duration and frequency of treatment / exposure:
- 72 hrs
Doses / concentrations
- Dose / conc.:
- 3 other: mg/kg bw
- No. of animals per sex per dose / concentration:
- 4
- Control animals:
- no
- Positive control reference chemical:
- not done
- Details on dosing and sampling:
- METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine, faeces, tissues, cage washes, CO2
- Time and frequency of sampling: 24, 48, 72 hrs
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on distribution in tissues:
- The distribution of radioactivity present in tissue samples from female mice showed that the heart, kidney, liver, lung, and spleen contained higher concentrations of triethanolamine equivalent relative to blood.
- Details on excretion:
- 26% of the dose was recovered in the urine within 24 hours.
An average of 62% of the dose was recovered in the urine within 72 hours after dosing, and 27.6% was recovered in the feces during this time.
Metabolite characterisation studies
- Details on metabolites:
- Urine collected 6 to 24 hours after intravenous dosing contained more than 95% radiolabeled components that coeluted with unchanged triethanolamine, with minor components eluting the same fractions in mice as those in rats.
Any other information on results incl. tables
With only 40% of the dose excreted within 24 hours, mice appeared to excrete intravenously administered triethanolamine much slower than did rats. Considerably more of the dose was recovered in the feces of mice (28 %) than in rats (0.6 %). However, it is common for mice to shred and powder their food pellets, and the feces collections are often contaminated with urine-soaked solids and their associated radiochemical equivalents. Less than 0.5 % of the dose was recovered in carbon dioxide traps, and less than 0.1 % was recovered in volatiles traps. The distribution of radioactivity present in tissue samples from female mice showed that, as with rats, the heart, kidney, liver, lung, and spleen contained higher concentrations of triethanolamine equivalent relative to blood.
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.