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EC number: 701-219-0 | CAS number: 15174-47-7
- 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
In a key read-acros Guideline (OECD 203) fish toxicity study, the 96-hour LC50 of Hexylcinnamaldehyde (CAS# 101-86-0) on the fathead minnow (Pimephales promelas) was determined to be 1.7 mg/L, with 95% confidence limits of 0.93 and 2.3 mg/L. When adjusted for the molecular weight of the test material, an LC50 of 1.2mg/L is achieved. The no-mortality concentration and the NOEC were both determined to be 0.93 mg/L.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Dose descriptor:
- LC50
- Effect concentration:
- 1.2 mg/L
Additional information
In a key read-acros Guideline (OECD 203) fish toxicity study (Wildlife International Ltd., 2010a), the acute effects of the test material (Hexylcinnamaldehyde; CAS# 101-86-0) on the fathead minnow (Pimephales promelas) were evaluated during a 96-hour exposure period under flow-through test conditions.
Fathead minnows were exposed to a geometric series of five test concentrations, a negativecontrol (dilution water), a solvent control (0.1 mL/L dimethylformamide) and a stabilizer control(0.01 mg/L stabilizer mix) for 96 hours under flow-through conditions. Two replicate test chambers were maintained in each treatment and control group, with 10 fish in each test chamber, for a total of 20 fish per concentration. Nominal test concentrations selected were 0.19, 0.38, 0.75, 1.5 and 3.0 mg/L. The concentration of the stabilizer mixture in the stabilizer control was equal to the concentration of stabilizer mixture in the highest treatment concentration. Mean measured test concentrations were determined from samples of test water collected from each treatment and control group at the beginning, the approximate mid-point and the end of the test.Delivery of the test substance to the test chambers was initiated four days prior to the introductionof the fathead minnows to the test water in order to achieve equilibrium of the test substance in the test chambers. The fish were impartially assigned to exposure chambers at test initiation. Observations of mortality and other signs of toxicity were made approximately 1, 24, 48, 72 and 96 hours after test initiation. Cumulative percent mortality observed in the treatment groups was used to determine LC50 values at 24, 48, 72 and 96 hours. The no-mortality concentration and the no-observed-effect concentration (NOEC) were determined by visual interpretation of the mortality and biological observation data.
When measured concentrations of the samples collected during the test were averaged, the mean measured test concentrations for this study were 0.12, 0.27, 0.61, 0.93 and 2.3 mg/L, representing 63, 71, 81, 62 and 77% of nominal concentrations, respectively.
All fish in the negative, solvent and stabilizer control groups appeared normal throughout the test. All fathead minnows in the 0.12, 0.27, 0.61 and 0.93 mg/L treatment groups also appeared normalthroughout the test, with no mortalities or overt signs of toxicity observed. Percent mortality in the2.3 mg/L treatment group at test termination was 80%. Signs of toxicity observed among fish in the2.3 mg/L treatment group were lethargy and lying on the bottom of the test chamber.
Based on the results observed, the 96-hour LC50 was determined to be 1.7 mg/L, with 95% confidence limits of 0.93 and 2.3 mg/L. When adjusted for the molecular weight of the test material, an LC50 of 1.2mg/L is achieved. The no-mortality concentration and the NOEC were both determined to be 0.93 mg/L.
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