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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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 10 Sep - 11 Sep 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Version / remarks:
- adopted 2010
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- The Department of Health of the Government of the United Kingdom
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Amounts of test item (5, 50 and 500 mg) were each separately dispersed in approx. 200 mL of deionized reverse osmosis water and subjected to ultrasonication for approx. 15 min followed by magnetic stirring for 24 h in order to maximize the dissolved test item concentration. All test vessels were shielded from the light during mixing. Synthetic sewage (16 mL), activated sewage sludge (250 mL) and water were added to a final volume of 500 mL to give the required concentrations of 10, 100 and 1000 mg/L. - Test organisms (species):
- activated sludge, domestic
- Details on inoculum:
- - Source of inoculum: A mixed population of activated sewage sludge micro-organisms was obtained on 10 Sep 2012 from the aeration stage of the Severn Trent Water Plc sewage treatment plant at Loughborough, UK, which treats predominantly domestic sewage.
- Method of cultivation: The activated sewage sludge sample was maintained on continuous aeration in the laboratory at a temperature of approx. 21 °C overnight prior to the test. On the day of collection the sludge (8 L) was fed synthetic sewage sludge (400 mL).
- Initial suspended solids concentration: 3.0 g/L prior to use - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Test temperature:
- 20 ± 2 °C
- pH:
- 7.8 - 7.9 at test start
8.3 - 8.5 at test end - Dissolved oxygen:
- 5.3 - 5.9 (controls), 4.1 - 6.8 mg/L (test flasks), 5.5 - 7.5 (reference flasks)
- Nominal and measured concentrations:
- Nominal: 0, 10, 100 and 1000 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 500 mL conical flasks containing 500 mL of test culture for incubation; 250 mL darkened glass BOD bottles for respiration rate measurements
- Aeration: yes, with clean, oil-free air at 0.5 - 1 L/min
- No. of vessels per concentration (replicates): 10 and 100 mg/L 1 flask, 1000 mg/L 3 flasks
- No. of vessels per control (replicates): 1
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Deionised reverse osmosis water containing < 1 mg/L dissolved organic carbon (DOC) was used in the test.
- Intervals of water quality measurement: Observations were made on the test preparations throughout the test period. The pH of all vessels was measured at 0 and 3 h, the oxygen concentrations in all vessels were measured after 30 min of contact time.
OTHER TEST CONDITIONS
- Light intensity: normal laboratory lighting
EFFECT PARAMETERS MEASURED (with observation intervals if applicable):
- After 3 h of contact time, an aliquot from each conical flask was poured into a BOD bottle and the rate of respiration measured over the linear portion of the oxygen consumption trace. The contents of the BOD bottles were stirred constantly by magnetic stirrer. The respiration rates were determined over periods of 4 - 10 min.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 10 - Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- - All validation criteria were fulfilled.
- No statistically significant toxic effects of the test item were shown at all of the test concentrations employed. The inhibition of respiration ranged from -3% to +1% for the test item and from 24% to 78% for 3,5-dichlorophenol.
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: All flasks contained pale/dark brown dispersions. In the test cultures test item was visible floating on the surface. In the reference control cultures no undissolved reference item was visible. - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- EC50 (3 h) = 10 mg/L, 95% CL = 8 - 13mg/L
Reference
Description of key information
EC50 (3 h) > 1000 mg/L (OECD 209)
Key value for chemical safety assessment
- EC50 for microorganisms:
- 1 000 mg/L
- EC10 or NOEC for microorganisms:
- 1 000 mg/L
Additional information
The toxicity of (Z)-N-Octadec-9-enylhexadecan-1-amide (CAS No. 16260-09-6) to aquatic microorganisms was investigated in one respiration inhibition test according to OECD guideline 209 under GLP conditions (Harlan, 2012). Predominantly domestic activated sludge was incubated with test item concentrations of 10, 100 and 1000 mg/L. The highest test concentration was prepared in triplicate while the two lower concentrations were single preparations. No statistically significant toxic effects of the test item were shown at all test concentrations employed. Therefore, an EC50 (3 h) > 1000 mg/L and a NOEC ≥ 1000 mg/L were assumed.
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