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Diss Factsheets
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EC number: 201-074-9 | CAS number: 77-99-6
- 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, other
- Type of information:
- other: estimation
- Adequacy of study:
- other information
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: estimation of toxicokinetic and metabolism of trimethylolpropane based on information given by the experimental animal data
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
- Principles of method if other than guideline:
- assumtions based on the available experimental data with amimals and physico-chemical data
- GLP compliance:
- no
Test material
- Reference substance name:
- Propylidynetrimethanol
- EC Number:
- 201-074-9
- EC Name:
- Propylidynetrimethanol
- Cas Number:
- 77-99-6
- Molecular formula:
- C6H14O3
- IUPAC Name:
- 2-ethyl-2-(hydroxymethyl)propane-1,3-diol
- Details on test material:
- as described in the respective tests
Constituent 1
- Radiolabelling:
- no
Administration / exposure
- Route of administration:
- other: assumtions based on the available experimental data with amimals and physico-chemical data
- Vehicle:
- other: assumtions based on the available experimental data with amimals and physico-chemical data
- Duration and frequency of treatment / exposure:
- assumtions based on the available experimental data with amimals and physico-chemical data
Doses / concentrations
- Remarks:
- Doses / Concentrations:
assumtions based on the available experimental data with amimals and physico-chemical data
- No. of animals per sex per dose / concentration:
- assumtions based on the available experimental data with amimals and physico-chemical data
Results and discussion
Any other information on results incl. tables
The following remarks on the toxicokinetics of trimethylolpropane are based on the available studies which were recorded within the process of registration according to the Regulation (EC) No. 1907/2006 (REACH). Experimental toxicokinetic studies were not available.
Trimethylolpropane (TMP, Molecular weight 134.18) is a white, crystalline, hygroscopic solid with a meltingpoint of 58°C at 25 °C, a vapour pressure of 0.0062 Pa at 25°C and log Pow of - 0.47 at room temperature.TMP dissolves readily in water(>100 g/L at room temperature), glycerol, ethanol and other low-molecular alcohols, but is somewhat less soluble in acetone, ethyl acetate and benzene and virtually insoluble in aliphatic, aromatic and chlorinated hydrocarbons (Criteria Group for Occup Standards 1995).
ABSORPTION
The physico-chemical characteristics of TMP (readily soluble in water,log Pow-0.47) and the molecular mass are in a range suggestive of absorption from the gastro-intestinal tract subsequent to oral ingestion. This assumption of an oral absorption is confirmed by the data on acute and subchronic oral toxicity. 1-2 hours following single oral administration of 1000, 2150, 4640, 10000 or21500 mg/kg bw, rats appeared depressed, exhibited lacrimation, slow and labored respiration from 2150 mg/kg bw onwards and mortality occurred at 21500 mg/kg bw. Gross autopsy of the dead animals showed pathological changes in lungs, stomach, intestine. Changes in the kidneys were seen in surviving rats dosed with 4640 and 10000 mg/kg bw (Celanese Corp. 1956). Repeated application of up to and including 1 % TMP in the diet (corresponding to max 667 mg/kg bw/d) for 90 days led to changes in red blood parameters and effects on liver, spleen and kidneys(de Knecht van Eekelen 1969). All these findings indicate absorption from gastrointestinal tract and systemic availability after oral application.
Water solubility, n-octanol/water partition coefficient and molecular weight of TMP are in ranges which favor dermal absorption. However, applied to the shaved back of rabbits in doses up to 10000 mg TMP/kg bw as paste for 24 hours followed by a 7 days post exposure observation, only mild irritational effects and no deaths were reported and at autopsy effects only on the kidneys were reported (Celanese Corp 1956). In acute skin and eye irritating studies in rabbits no systemic intolerance reactions have been reported (Bayer 1979) and no sensitizing effect has been identified in the Local Lymph Node Assay (Bayer AG 2010).
Water solubility and low molecular weight are suggestive for inhalation absorption but due to the vapour pressure of 0.02 Pa it is unlikely to occur at workplace. In animal experiments, acute exposure did not lead to signs of intoxication and/or mortality. In an early study, at autopsy following repeated exposure up to 1800 mg/m³ daily for 4 hours over a period of 3.5 months, there is some evidence of absorption shown in only slight disturbance of blood circulation, slight disturbance of the permeability of the vessel walls, interstitialpneumonia, focal emphysema in lungs and parenchymatous degeneration of the liver but individual animal data were not shown (Stankevich 1967).
DISTRIBUTION and METABOLISM
As a small molecule with the given water solubility a wide distribution is expected. This assumption is confirmed by the changes shown in the repeated dose toxicity studies following oral application or inhalation exposure (see section Absorption). However, histopathological changes in spleen and liver only at the highest test doses in the 90-day feeding study (de Knecht-van Eekelen 1969) reveal limited distribution into cells.
Based on the results of the in vitro genotoxicity tests (Ames test, with and without metabolic activation, MHLW ) and HPRT test with and without S9 -mix (Harlann CCR 2010) and
Chromosome Aberration tests with and without metabolic activation (MHLW ) it is concluded that DNA-reactive metabolites of TMP will most probably not be generated in mammals in the course of hepatic biotransformation. The polar structure of TMP suggests that it will preferably be either directly conjugated in a phase-II reaction or undergoes further oxidation in the alcohol moieties of the molecule.
ELIMINATION
The n-Octanol/water partitition coefficient (log Pow of 0.47) is not suggestive of accumulation of unchanged TMP in fatty tissues subsequent to absorption from GI tract or from lungs. On the basis of the molecular structure, the molecular size and the water solubility excretion into urine in the unchanged form and/or as glucuronide/sulfate is assumed to be a preferred route of elimination
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.
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