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EC number: 201-116-6 | CAS number: 78-42-2
- 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:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: No OECD guideline or GLP defined.
Data source
Reference
- Reference Type:
- publication
- Title:
- Toxicological Studies on Tri-(2-Ethylhexyl)-Phosphate
- Author:
- MacFarland H.N.; Punte C.L.
- Year:
- 1 966
- Bibliographic source:
- Archives of Environmental Health Vol. 13, pp.13-20
Materials and methods
- Objective of study:
- metabolism
- Principles of method if other than guideline:
- other: Radiotracer Inhalation Study
- GLP compliance:
- no
Test material
- Reference substance name:
- Tris(2-ethylhexyl) phosphate
- EC Number:
- 201-116-6
- EC Name:
- Tris(2-ethylhexyl) phosphate
- Cas Number:
- 78-42-2
- Molecular formula:
- C24H51O4P
- IUPAC Name:
- tris(2-ethylhexyl) phosphate
- Details on test material:
- Mol wt: 434.6;
Sp g: 0.925 at 20 C;
n25D: 1.4473;
Surface tension: 31 dynes/sq cm;
Viscosity: 10.2 cp;
Vap press: 2 mm Hg at 200 C
particle diameter of 4 µ
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- 32P radiolabel (for metabolism study only)
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- All species were adapted to laboratory conditions prior to use for one to two weeks. Animals were housed in cages with screen bottoms elevated above the droppings.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- not specified
- Details on exposure:
- Radiotracer study- in rats (inhalation)
Nine rats were subjected to a single exposure of radioactive TOF, disseminated as an aerosol from a Laskin generator 7 into a tubular exposure apparatus. The median particle size produced was approximately 4 um. The exposure tube, constructed of clear plastic, measured 3 X 3 X 30 inches long and was provided with four ports through which the animals' heads protruded into the lumen. The outlet of the tube led to an absorption train consisting of three gas washing bottles charged with trichlorethylene, a rotameter, and exhaust pump. A filter paper sampling holder was arranged in parallel and could be substituted for the absorption train by manipulation of stopcocks. After exposure, the rats were maintained in metabolism cages and then sacrificed by exsanguination at various time intervals. - Duration and frequency of treatment / exposure:
- sinlge exposure of radiolabelled TEHP for 20 mins (aerosol).
Doses / concentrations
- Remarks:
- Doses / Concentrations:
nominal air flow concentration was 1.45 mg/L- actual determined to be 0.72 - 0.91 mg/L.
Mean recoveries of radioactiviy from rat tissues suggest that each rat retained ca 1.13 mg
- No. of animals per sex per dose / concentration:
- various- see exposure section
- Control animals:
- no
- Positive control reference chemical:
- no
- Details on study design:
- Radiotrace inhalation study
- Details on dosing and sampling:
- rats were sacrificied by exsanguination after the following time intervals post exposure: 5 minutes, 30 minutes, 1, 4, 17, 18, 24, 48, and 70 hours. The brain, lungs, liver, spleen, kidneys, stomach and stomach contents, fat, muscle, bone, urine, blood, and feces were analyzed for radioactivity. The head skin was also removed and examined for surface radioactivity.
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- the test substance is well absorbed after 20-minute inhalation exposure
- Details on distribution in tissues:
- the test substance is rapidly distributed in tissues, mainly in the lung, liver and brain
Transfer into organs
- Observation:
- other: the test substance is rapidly distributed in tissues, mainly in the lung, liver and brain
- Details on excretion:
- fecal excretion high
Toxicokinetic parameters
- Toxicokinetic parameters:
- other: maximum retention in tissue after the first few hours
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- In studying the excretion of radioactive test substance or its metabolites, urine and feces samples from the rat sacrificed at 48 hours were utilized.
Any other information on results incl. tables
RM-Freetext:
Radiotracer inhalation study with rats: 9 male rats, single
head exposure, 20 minutes, aerosol, sacrifice after 5 min,
30 min, 1, 4, 17, 18, 24, 48, or 70 h:analytcal
concentration 0.72 to 0.91 mg/l, maximum retention in tissue
after the first few hours, fecal excretion high.
Applicant's summary and conclusion
- Executive summary:
In an old and limited documented radiotracer inhalation study nine male rats received a single head exposure of an aerosol of [32P] labeled test substance (median particle size 4 nm) for 20 minutes. The animals were sacrificed by exsanguinisation after the following intervals post exposure: 5 minutes, 30 minutes, 1, 4, 17, 18, 24, 48, and 70 hours. The brain, lungs, liver, spleen, kidneys, stomach and stomach contents, fat, muscle, bone, urine, blood, and feces were analyzed for radioactivity. The head skin was also removed and examined for surface radioactivity. Analytical concentrations, obtained from the analysis of filter paper samples, revealed that the nominal concentration of the test substance levels ranged between 0.72 and 0.91 mg/liter. An estimate of the total amount of radioactive test substance in the rat sacrificed five minutes after exposure, obtained by summing all tissue radioactivities, came to 1.13 mg. On analysis for radioactivity, it was found that most tissues exhibited a maximum retention in the first few hours, followed by a progressive decay. Thus, the lungs retained a peak of 13% of the total radioactivity in the animal at five minutes, with a subsequent gradual decline. Peak activity was seen in the brain and liver at 30 minutes and corresponded to retentions of 9% and 16%, respectively. Other organs and tissues (i.e., spleen, kidneys, bone, muscle, and fat) retained less than 2% of the radioactivity at any time. A high level of radioactivity, representing 50% to 64% retention, was found during the first hour in the stomach contents, but this declined rapidly thereafter. Urinary and fecal excretions, first determined at the 17-hour point, were moderately high, 7%, and then declined steadily. Finally, carcass radioactivity increased to a peak corresponding to 81% retention at 48 hours post exposure, followed by a progressive decrease. In studying the excretion of radioactive test substance or its metabolites, urine and feces samples from the rat sacrificed at 48 hours were utilized. Ascending chromatography of filter paper strips 54 cm long for 48 hours was performed. The strip was cut into segments and these were counted for three minutes. The fecal sample exhibited very high activity but only slight activity was detectable in the urine sample. The results obtained with the isopropyl ether-formic acid solvent system was the only solvent that yielded evidence of excretion of a metabolite product of the test substance.
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