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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: 208-144-8 | CAS number: 512-56-1
- 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
Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.141 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 12.5
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 1.8 mg/m³
- Explanation for the modification of the dose descriptor starting point:
The starting point was corrected according to Figure R.8-3 in chapter R.8 in the ECHA guidance document (version 2.1, November 2012). NOAEL(oral, rat) = 1 mg/kg bw/day => NOAEC(corrected, inhalation) = NOAEL(oral, rat) x 1/(0.38 m3/kg bw/day) x 6.7 m3/10 m3 x 0.5 = 1.8 mg/m3
- AF for dose response relationship:
- 1
- Justification:
- Default value (ECHA)
- AF for differences in duration of exposure:
- 1
- Justification:
- Default value (ECHA)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Default value (ECHA)
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value (ECHA)
- AF for intraspecies differences:
- 5
- Justification:
- Default value (ECHA)
- AF for the quality of the whole database:
- 1
- Justification:
- Default value (ECHA)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- skin irritation/corrosion
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- skin irritation/corrosion
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.2 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 50
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 10 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
In an acute dermal toxicity study with New Zealand White rabbits the LD50 was determined to be 3388 mg/kg Trimethyl Phosphate. Due to the low dermal toxicity, it appears that Trimethyl Phosphate is absorbed more rapidly through the gastrointestinal tract than the skin. According to QSAR DERMWIN the calculated dermal absorption is 10 %. Therefore, the starting point was corrected according to the slower absorption through skin.
- AF for dose response relationship:
- 1
- Justification:
- Default value (ECHA)
- AF for differences in duration of exposure:
- 1
- Justification:
- Default value (ECHA)
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default value (ECHA)
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value (ECHA)
- AF for intraspecies differences:
- 5
- Justification:
- Default value (ECHA)
- AF for the quality of the whole database:
- 1
- Justification:
- Default value (ECHA)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- skin irritation/corrosion
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - workers
As trimethyl phosphate is manufactured in a closed system, exposure during synthesis may be excluded. Since this chemical is used as a polymerization catalyst, the possibility of workplace exposure through dermal route is possible when the product is filled into barrels. Dermal uptake at work place is considered to be the main exposure route while inhalation plays a minor role. However workers wear personal protective equipment (e.g. chemical cartridge respirator with an organic vapour cartridge, safety glasses and protective suits) during the filling process. Therefore, the exposure at work place is considered to be very low.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- skin irritation/corrosion
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- skin irritation/corrosion
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 25 µg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 40
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
Bioavailability in humans versus rat concerning oral route: no data are available for humans (rat: nearly complete absorption) but the same bioavailability is assumed, no correction.
Same route of exposure, no correction.
- AF for dose response relationship:
- 1
- Justification:
- Default (DNEL calculator)
- AF for differences in duration of exposure:
- 1
- Justification:
- Default (DNEL calculator)
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default (DNEL calculator)
- AF for other interspecies differences:
- 1
- Justification:
- Default (DNEL calculator)
- AF for intraspecies differences:
- 10
- Justification:
- Default (DNEL calculator)
- AF for the quality of the whole database:
- 1
- Justification:
- Default (DNEL calculator)
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
The highest exposure to the general population via the environment would be expected through drinking water processed from surface water. Based on the physical chemical properties of trimethyl phosphate, a significant removal of during processing is not expected. Although PECglobal cannot be estimated, the concentration in drinking water is assumed to be less than 1.5 x 10-4 mg/l. Assuming a consumption of drinking water of 2 L/day and an average body weight of 60 kg, a daily intake of 5.0 x 10-6 mg/kg/day can be estimated. The margin of safety is very large.
The exposure through food is estimated to be negligible as the substance has a low bioaccumulation potential.
Therefore, health risk through the environment, in general, is considered to be low due to its use pattern and exposure situation.
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.