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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
Long-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
For bis(2-ethylhexyl) hydrogen phosphate in an Embryo-larval toxicity test a 48d-NOEC of 20.6 mg/L was obtained for Salmo gairdneri under semi-static conditions. A further test with the same test design revealed a 10d-NOEC of 21 mg/L for Brachydanio rerio.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 20.6 mg/L
Additional information
The toxicity of bis(2-ethylhexyl) hydrogen phosphate was investigated in embryos and larvae of rainbow trout (Salmo gairdneri) and zebrafish (Danio rerio) following the procedure for the embryo-larval toxicity test by American scientists (the U.S. EPA procedure) with deviations. The three main differences are (1) that a static renewal instead of a flow-through procedure was used, (2) that no food was offered during the test, which accordingly cannot be extended as long as the EPA procedure and, (3) that the results are based on nominal values instead on measured values. The studies were valuated as long-term toxicity as the fish were exposed at the most sensitive developmental stages.
In the experiments, stock solutions of bis(2-ethylhexyl) hydrogen phosphate were made up with acetone. A defined amount of the stock solutions was used to achieve the desired test concentrations. Acetone was evaporated to dryness at room temperature. After addition of water to the vessels, and equilibration during the night embryos or larvae of rainbow trout were introduced. In the study with zebrafish, acetone was also evaporated to dryness at room temperature and after addition of water to the petri-dishes 10–15 viable fertilized eggs of zebrafish were introduced. Control vessels are prepared in each test in the same manner. Rainbow trout embryos and larvae were exposed to bis(2-ethylhexyl) hydrogen phosphate at 8 +/- 1°C and a 12 h light-dark photoperiod. No feeding of the test animals took place during the experiment, which was terminated 48 days after hatching. Renewal of test solutions was every third to fourth day at the beginning and every week at the end of test. Fertilized eggs (5 h after fertilization) of zebrafish were exposed to bis(2-ethylhexyl) hydrogen phosphate at 25°C and a 12 h light-dark photoperiod. No feeding of the test animals took place during the experiment, which was terminated after 10 days. Renewal of test solutions was every second day by transferring survivors to new dishes. Mortality was recorded daily. Dead eggs got an opaque white to yellowish colour and the larvae were defined as dead if they did not respond to mechanical stimulation. For rainbow trout a result of 20.6 mg/l is reported and for zebrafish a result of 21 mg/l is reported. Both values are given as threshold concentration and in combination with a presented graph, each value is interpreted as NOEC.
Despite no details on amount of test concentrations were reported the studies were considered as reliable and useful for assessment.
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