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EC number: 943-303-1 | CAS number: -
- 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 aquatic algae and cyanobacteria
Administrative data
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 017
- Report date:
- 2017
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- Reaction products of diphenyl ether and 9-methylene nonadecane
- EC Number:
- 943-303-1
- Molecular formula:
- Variable, substance is a UVCB
- IUPAC Name:
- Reaction products of diphenyl ether and 9-methylene nonadecane
- Test material form:
- liquid
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 100 mg/L (nominal)
- Sampling method: Samples were taken at 0, 24, 48 and 72 hours after exposure and analysed by GC-MS.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- Test solutions were prepared as Water Accommodated Fractions (WAFs) and Water Soluble Fractions (WSFs). Initially amounts of test substance were weighed and added directly to aspirators where they were stirred for 48 hours. The resulting WAF was then filtered using a 5 µm filter paper. The resulting solutions were then used on study. This procedure was confirmed as a result of the range finding phase.
Test organisms
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Pseudokirchneriella Subcapitata
- Strain: ATCC22662
- Source (laboratory, culture collection): American Type Culture Collection
- Method of cultivation: Maintained by periodic subculture using Gorham medium. Algae are kept under sterile conditions.
ACCLIMATION
- Acclimation period: 4 days
- Any deformed or abnormal cells observed: No
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
Test conditions
- Hardness:
- No details
- Test temperature:
- 21.5 to 22.3°C throughout the test
- pH:
- 7.7 to 7.8 throughout the test
- Dissolved oxygen:
- No details
- Nominal and measured concentrations:
- Nominal: 100 mg/L (loading rate)
Measured: 1.16 mg/L (TWA) - Details on test conditions:
- TEST SYSTEM
- Test vessel: 300 mL Erlenmeyer flask with aluminium cap
- Type: open
- Material, size, headspace, fill volume: 100 mL
- Aeration: No
- Initial cells density: 5 x 10^3
- No. of vessels per concentration (replicates): 6
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: yes (OECD medium as detailed in the respective guideline)
OTHER TEST CONDITIONS
- Sterile test conditions: Yes
- Adjustment of pH: No
- Photoperiod: Continious
- Light intensity and quality: 68 to 74 µE/m2/s
EFFECT PARAMETERS MEASURED:
- Determination of cell concentrations: cells/mL (biomass) and growth rate
TEST CONCENTRATIONS
- Range finding study: Control, 10 and 100 mg/L
- Test concentrations: Limit test at 100 mg/L
- Results used to determine the conditions for the definitive study: No effects in range finding phase at limit dose. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 72 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1.16 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: exceeds limit of aqueous solubility
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1.16 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: exceeds limit of aqueous solubility
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test): No
- Unusual cell shape: No
- Colour differences: No
- Flocculation: No
- Adherence to test vessels: No
- Aggregation of algal cells: No
- Any stimulation of growth found in any treatment: No
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: None
- Effect concentrations exceeding solubility of substance in test medium: Yes (no effects observed at limit dose). - Results with reference substance (positive control):
- Growth inhibition tests with a reference reagent potassium dichromate are conducted every 6 months. The ErC50 values obtained in the most recent test were within historical ranges for tests conducted at the laboratory.
- Reported statistics and error estimates:
- The NOEL/NOEC values were determined using a Student's t-test subsequent to a test for homogeneity of variances. No statistical analysis was performed to determine the EC50/EL50 values as no effects were observed.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- Validity criteria on test fulfilled
- Conclusions:
- The effect concentrations to algae exceeded the aqueous solubility of the test substance when performing a limit test at a loading rate of 100 mg/L. The water solubility of the test substance in the aqueous media was determined to be low.
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