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EC number: 500-209-1 | CAS number: 68412-54-4 1 - 2.5 moles ethoxylated
- 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
Studies were conducted to evaluate the acute toxicity of NP, NPE-1 and NPE-2 to fathead minnow (Pimephales promelas) under flow-through conditions in freshwater. The procedures followed EPA guidelines. Under the test conditions, the 96 h LC50 values were 0.136, 0.218 and 0.323 mg/L, respectively. The data suggests that the acute toxicity to fish decreases as ethoxylation grade increases, as would be expected based on water solubility. The 96 h LC50 of 0.218 mg/L for Pimephales promelas exposed to NPE-1 was selected as being representative for NPEO (which contains > 30 - <50% NPE-1).
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 0.218 mg/L
Additional information
A study was conducted to evaluate the acute toxicity of pure NPE-2 to fathead minnow (Pimephales promelas) under flow-through conditions in dechlorinated freshwater. The procedures followed the EPA Guideline OPP 72-1. After an acclimatisation period of 24 h, less than 4 day old fish larvae were exposed at the measured concentrations of <12 (control),99.4 ± 37.2, 129 ± 43, 188 ± 47, 287 ± 75 and 630 ± 150µg/L for 96 h. Four replicates were used for each dose group. Test substance concentrations were verified analytically using HPLC on water samples collected from the middle of the exposure tanks at 0 and 96 h and from half of the tanks at 24, 48 and 72 h. The animals were not fed during the test and were observed daily for mortality. Corresponding potassium chloride reference tests were conducted and found to be within acceptable limits. Survival in the controls for all of the replicates was >95% and the guideline water quality criteria were met. Under the study conditions, the 96 h LC50 for Pimephales promelas was 323 µg (0.323 mg)/L (TenEyck MC and Markee TP, 2007).
In the same study, the authors also tested pure NPE-1 and NP under similar conditions.
NPE-1 measured concentrations were equivalent to <10.4 (control), 39.4 ± 15.3, 51.4 ±15.3, 88.7 ± 22.8, 164 ± 31 and 338 ± 10 µg/L. The 96 h LC50 was 218 µg (0.218 mg)/L.
NP measured concentrations were <3.1 (control), 19.3 ± 3.1, 24.9 ± 6.3, 36.5 ± 7.3, 88.7 ± 5.7 and 229 ± 19 µg/L. The 96 h LC50 was 136 µg (0.136 mg)/L.
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