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EC number: 240-367-6 | CAS number: 16260-09-6
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 11 May 2020 - 17 Feb 2023
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 305 (Bioaccumulation in Fish: Aqueous and Dietary Exposure) -III: Dietary Exposure Bioaccumulation Fish Test
- Version / remarks:
- 2 October 2012
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Radiolabelling:
- yes
- Details on sampling:
- - Sampling intervals/frequency for test organisms: day 0, 14 (uptake phase), 15, 18, 21, 28, 35, 42 (depuration phase)
- Sampling intervals/frequency for test medium samples: day 0, 14 (uptake phase)
- Sample storage conditions before analysis: chilled conditions
- Details on sampling and analysis of test organisms and test media samples: Food samples: extraction with tetrahydrofuran, vortex mixing for 1 min, sonication for 15 min, centrifugation at 3000 rpm for 15 min. Fish samples: homogenization by mincing with scissors, extraction with tetrahydrofuran by mixing with a blender for 5 min, sonication for 5 min. centrifugation at 2500 rpm for 15 min. - Vehicle:
- yes
- Remarks:
- corn oil
- Details on preparation of test solutions, spiked fish food or sediment:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: evaporation to dryness and solution in corn oil
- Controls: corn oil without test substance
- Concentration of vehicle in test medium: Test substance: 2.49 mL corn oil in 120.06 g food; Control: 2.4 mL corn oil in 120.16 g food
- Evidence of undissolved material: none reported
PREPARATION OF SPIKED FISH FOOD
- Details on fish food: Inicio 917 1.1 mm trout pellets (Biomar, Denmark) (50% protein and 16% fat content)
- Details of spiking: test substance dissolved in corn oil
- Quantity of corn oil vehicle per unit mass of fish food: Test substance: 2.49 mL corn oil in 120.06 g food; Control: 2.4 mL corn oil in 120.16 g food
- Method of mixing: manual shaking followed by rotational agitation for 5 min - Test organisms (species):
- Oncorhynchus mykiss (previous name: Salmo gairdneri)
- Details on test organisms:
- TEST ORGANISM
- Common name: rain bow trout
- Source: Commcercial supplier, UK
- Length at study initiation: mean 8.13 cm
- Weight at study initiation: mean 5.37 g
- Weight at termination (mean and range, SD): 5.28 - 9.66 g
- Lipid content at test initiation: 4.26% (tissue weight)
- Health status: no abnormalities reported
- Description of housing/holding area: same as test, acclimatization for at least 2 weeks
- Feeding during test
- Food type: Inicio 917 1.1 mm trout pellets (Biomar, Denmark)
- Amount: 2% of body weight (on day 27 2.7% were fed in error)
- Frequency: daily
ACCLIMATION
- Acclimation period: at least 2 weeks
- Acclimation conditions: same as test
- Type and amount of food: Inicio 917 1.1 mm trout pellets (Biomar, Denmark)
- Feeding frequency: daily
- Health during acclimation: no mortality reported - Route of exposure:
- feed
- Justification for method:
- dietary exposure method used because stable, measurable water concentrations cannot be maintained
- Test type:
- flow-through
- Water / sediment media type:
- natural water: freshwater
- Total exposure / uptake duration:
- 14 d
- Total depuration duration:
- 28 d
- Hardness:
- 174 - 176 mg CaCO3
- Test temperature:
- 13.9 - 14.3°C
- pH:
- 7.6 - 8.1
- Dissolved oxygen:
- 72 - 95% air saturation
- TOC:
- <1.0 - 1.3 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: aquaria
- Material, fill volume: glass, 100 L
- Aeration: continuous aeration
- Renewal rate of test solution: nominal 800 mL/min equal to approximately 1152 L per d
- No. of organisms per vessel: 50
- No. of vessels per concentration: 1
- No. of vessels per control / vehicle control: 1
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: tap water, dechlorinated by activated carbon, softened to the desired water hardness
- Metals: none
- Pesticides: none
- Chlorine: none
- Holding medium different from test medium: no
- Intervals of water quality measurement: pH, oxygen, temperature daily
OTHER TEST CONDITIONS
- Photoperiod: 16 h light/ 8 h dark, with 20 min dawn and dusk transition periods
- Overall daily feeding rate used in the study: 2 % body weight, adjusted after every sampling interval (on day 27 erroneously 2.7% was fed)
- Number of feeds per day: 1
RANGE-FINDING / PRELIMINARY STUDY
The solubility in the vehicle corn oil was determined with nominal test substance concentrations of 10, 100, 1000 µg/g. The 1000 µg/g concentration contained undissolved material, while the lower concentrations were observed to be clear.
The homogeneity of the test substance on food was tested with the concentrations 10, 100 µg/g. The test substance dissolved in corn oil was administered to fish food same as in the test five times. The test substance concentrations were in the range of ±15%.
The palability of treated food was determined for 7 days. The feeding was considered to be normal. With a test substance concentration of 100 µg/g, radioactivity in fish was in the range of 1.05 - 1.91 µg equivalents/g after 7 d. This was determined to be sufficient for measuring a 95% reduction in body burden. Therefore, the concentration of 100 µg/g food was chosen for the test. - Nominal and measured concentrations:
- Nominal 0 (control), 100 µg test substance/g food
Measured at d0: 0 (control), 112 µg/g
Measured at d14: 0 (control), 104 µg/g - Reference substance (positive control):
- no
- Lipid content:
- 5.33 %
- Time point:
- other: end of depuration
- Lipid content:
- 4.65 %
- Time point:
- end of exposure
- Remarks on result:
- other: end of uptake/start of depuration
- Lipid content:
- 4.26 %
- Time point:
- start of exposure
- Conc. / dose:
- 100 µg/g food
- Type:
- BMF
- Value:
- 0.386 dimensionless
- Basis:
- whole body w.w.
- Calculation basis:
- kinetic
- Conc. / dose:
- 100 µg/g food
- Type:
- BMF
- Value:
- 0.582 dimensionless
- Basis:
- whole body w.w.
- Calculation basis:
- other: Lipid normalized
- Conc. / dose:
- 100 µg/g food
- Type:
- BMF
- Value:
- 0.15 dimensionless
- Basis:
- whole body w.w.
- Calculation basis:
- kinetic, corrected for growth
- Elimination:
- yes
- Parameter:
- DT50
- Depuration time (DT):
- 7 d
- Rate constant:
- growth-corrected depuration rate constant (d-1)
- Value:
- 0.012
- Rate constant:
- growth-corrected half-life (d)
- Value:
- 59.2
- Details on kinetic parameters:
- - Uptake rate constant k(f): 0.00176 kg food / kg fish / day
- Depuration rate constant k(e): 0.0455
- Indication of bi- or multiphasic kinetics: none - Metabolites:
- 2 metabolites could be identified:
M1: Palmitic acid, C16H32O2
M2: C32H63O3N - Details on results:
- - Mortality of test organisms: None
- Behavioural abnormalities: None
- Observations on feeding behavior: Normal feeding bevaior
- Observations on body length and weight: No abnormalities
- Mortality and/or behavioural abnormalities of control: None
- Loss of test substance during test period: None - Reported statistics:
- Data was analysed using GraphPad Prism (ver. 9.0.1) and R software with package OECD-TG305 bcmfR (v0.4-18). Three optimization models were tested against the data. Linear regression, a Box-Cox transformation and a Natural Log transformation. Box-Cox showed optimum results and was ultimately used for evaluation.
- Validity criteria fulfilled:
- yes
- Remarks:
- see Table 1 in "Any other information on results incl. tables" for further details
Reference
Table 1: Validity criteria for OECD 305-III
Criterion from the guideline | Outcome | Validity criterion fulfilled |
The temperature variation is less than ± 2 °C | 13.9 – 14.3°C | yes |
The concentration of dissolved oxygen does not fall below 60% saturation | ≥72% | yes |
The concentration of the test substance in fish food before and at the end of the uptake phase is within a range of ± 20% (based on at least three samples at both time points) | 104 – 112 % recovery | yes |
The homogeneity of test item in feed is confirmed to be less than ±15 % from the mean (by analysis at least triplicate portions) | 109% | yes |
Concentrations of test substance are not detected, or are present only at typical trace levels, in un-spiked food or control fish tissues relative to treated samples | No test substance in untreated food or control fish reported | yes |
The mortality or other adverse effects/disease in both control and treated fish is less than 10% at the end of the test; where the test is extended over several weeks or months, death or other adverse effects in both sets of fish should be less than 5% per month and not exceed 30% in all. | No mortality or adverse effects reported | yes |
Description of key information
BMF: 0.582 kg food / kg fish (lipid normalised, OECD 305, dietary exposure)
Key value for chemical safety assessment
Additional information
Experimental data on bioaccumulation of (Z)-N-Octadec-9-enylhexadecan-1-amide (CAS No. 16260-09-6) is available from an OECD 305 GLP-study by dietary route.
Radio-labeled substance was administered to rainbow trout (Oncorhynchus mykiss) via food over a period of 14 days, followed by a 24 days depuration phase. The concentration of the test substance in food during the uptake phase was 100 µg/g.
The mean concentration of total radioactivity in fish tissue was 2.54 µg equivalents/g after 14 days of exposure, but declined to 0.514 µg equivalents/g. C hromatographic analysis of the extracts showed that the test substance had been metabolized, accounting for 42.0% sample radioactivity (1.07 µg/g) after 14 days of exposure. After 28 days depuration, crodamide 203 accounted for 5.8% sample radioactivity (0.03 µg/g).
The test substance was metabolized to palmitic acid (≤22.6% sample radioactivity), Met 5 (≤14.3%), Met 7 (≤56.8%), polar material (≤3.3%) and up to eight low level, unidentified metabolites (each comprising ≤4.5% sample radioactivity).
The calculation of effect levels and kinetic parameters showed a BMF of 0.582 kg food/kg fish (lipid normalized) and a growth corrected half-life of 59.2 d.
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