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EC number: 201-114-5 | CAS number: 78-40-0
- 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

Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
A number of published and proprietary studies are available.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 2 100 mg/L
Additional information
Ewell et al (1986) describe the development of a test system designed to simultaneously assess the aquatic toxicity of chemicals to seven species, including six invertebrate species. Under the conditions of this study, the 96 -hour LC50 of triethyl phosphate in the invertebrate species tested [Asellus intermedius (pillbug), Daphnia magna (water flea), Dugesia tigrina (flatworm), Gammarus fasciatus (sideswimmer), Helisoma trivolvis (snail) and Lumbriculus variegatus (segmented worm)] and in the fathead minnow were all reported to be >100 mg/L.
The acute toxicity of triethylphosphate was investigated in the bleak (Alburnus alburnus). The 96 -hour LC50 value of the substance was calculated to be 2100 -2400 mg/L (Linden et al, 1978).
The acute aquatic toxicity was investigated in Oryzias latipes. The 48 -hour LC50 of the substance is reported to be >500 mg/L (CITI, 1992).
The acute toxicity of triethyl phosphate was investiagted in Leuciscus idus. The 48 -hour LC0, LC50 and LC100 values were found to be 1926 mg/L, 2140 mg/L and 2500 mg/L under the conditions of this study (Knie et al, 1983).
The acute toxicity of triethylphosphate was investigated in Danio rerio. No deaths occurred at concentrations of up to and including the highest tested concentration of 100 mg/L. The 96 -hour LC50 of triethylphosphate in Danio rerio is therefore >100 mg/L (Bayer, 1985a). The acute toxicity of triethylphosphate was also investigated in Leuciscus idus. 50% mortality was seen in an initial study performed at 100 mg/L, however no effects were seen in subsequent experiments at 133 or 100 mg/L. The LC50 is therefore considered to be >= 100 mg/L (Bayer, 1985b).
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