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EC number: 206-056-4 | CAS number: 298-07-7
- 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
The most reliable experimentally determined 96h-LC50 value of bis(2-ethylhexyl) hydrogen phosphate was 30 mg/L on Salmo gairdneri.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 30 mg/L
Additional information
Three studies are available with regard to the acute toxicity of bis(2-ethylhexyl) hydrogen phosphate to fish.
Despite the fact that these studies are not documented satisfyingly, their scientific value appears sufficient for assessment. Especially since the toxicity data of all three studies reveal very similar 96h LC50 values lying within the same order of magnitude.
The most reliable study is a toxicity test performed with Salmo gairdneri (now Oncorhynchus mykiss) in a static test system at 15°C and 20°C. Although there was no guideline stated, the tests were performed under generally accepted scientific principles. Experiments were conducted with 10 animals at each concentration tested.
The pH was initially adjusted to 7.9. At 20°C a 96h-LC50 of 20 mg/l was obtained and at 15°C a 96h-LC50 of 30 mg/L was observed, both related to nominal concentrations. The recommended temperature for rainbow trout is 15°C according to OECD TG 203, therefore the 96h-LC50 value at 15°C is the preferred value for assessment. Effects resulting from the exposure conditions at 20°C cannot be excluded. Although no details on the amount of test concentrations were reported the study is considered as reliable and was therefore chosen as key study.
In another study, toxicity of bis(2-ethylhexyl) hydrogen phosphate towards fish was assessed in a toxicity range finding test under static conditions. Salmo gairdneri was exposed to several concentrations at 15°C for 96 h of exposure, which is in accordance with OECD TG 203. Due to the large size (15 - 25 g) of fish, only 4 fish were used at each test concentration. Analysis of test substance was carried out by spectrophotometric determinations of the total phosphorus content. A 96h-LC50 of 48–54mg/L based on measured concentrations was obtained in this test. Since this value lies well within the order of magnitude of the key study (30 mg/L) the study is considered as useful for assessment. However, based on methodological deficiencies (only 40% of the required number of test fish are used) the study was only used as supporting study.
Following the procedure of ISO/TC 147/SC5/WG3 (France: acute toxicity test; static) with 2 exceptions, the toxicity of bis(2-ethylhexyl) hydrogen phosphate towards Danio rerio was assessed. Only 5 juvenile zebrafish were exposed to bis(2-ethylhexyl) hydrogen phosphate at a temperature of 25°C and the exposure time was extended to 144h (6 days). Appropriate amounts (0-5.6 mL) of substance stock solutions were made up in acetone.
After evaporation of acetone just to dryness at room temperature, premade aerated Standard Reference Water was added to each flask. A solvent control (maximal amount of acetone evaporated just to dryness) and an ordinary control were included in the test procedure. A 144h-LC50 and a 96h-LC50 of > 56 mg/l were reported. The LC50 was above the highest concentration tested. Based on methodological deficiencies (only 50% of the required numbers of test fish are used) the study is scored as reliable with restrictions and is considered to be useful for assessment. The study is therefore used as a supporting study.
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