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EC number: 203-468-6 | CAS number: 107-15-3
- 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
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- documentation insufficient for assessment
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Deviations:
- yes
- Remarks:
- minor differnce in medium composition
- GLP compliance:
- not specified
- Analytical monitoring:
- not specified
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- Strain ATCC 2262
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Test temperature:
- 22°C
- Nominal and measured concentrations:
- Three replicate sat each concentration, but no data on concentration interval.
- Details on test conditions:
- The culture medium was modified in that the concentration of KH2PO4 was increased from 1.6 to 160 mg/L and for NaHCO3 from 50 to 100 mg/L to improve buffer capacity of the medium.
- Duration:
- 96 h
- Dose descriptor:
- EC50
- Effect conc.:
- 151 mg/L
- Basis for effect:
- growth rate
- Remarks on result:
- other: standard deviation of mean 21.4
- Validity criteria fulfilled:
- not specified
- Conclusions:
- 96 h EC50 for inhibition of algae growth rate was 150 mg/L.
- Executive summary:
A study was conducted to determine the toxicity potential of the test substance to Selenastrum capricornutum, according to EU Method C.3. The growth inhibition of S. capricornutum has been assessed over an exposure period of 96 hours. No details of methods used and analytical monitoring were reported in the study. Under the study conditions, the 96 h EC50 was determined to be 150 mg/L (van Wijk, 1993).
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- Note, no analytical monitoring of the test substance concentrations were performed.
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Version / remarks:
- including updates published 1988
- Deviations:
- yes
- Remarks:
- Slight change in mineral medium, preliminary study performed but not included in report
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Details on test solutions:
- A stock solution of 10 g Ethylene diamine /L in deionized water was titrated to neutral pH. Test solutions were prepared by dilution with test medium.
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- Selenastrum capricornutum ATCC 22662 was mantained on mineral salts agar slants in the light at room temperature.
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 72 h
- Test temperature:
- 22 - 24°C
- pH:
- pH 7 in fresh solutions, pH in 72 h test medium was 7.5 - 9.
- Nominal and measured concentrations:
- 0, 3.2, 10.2, 32.8, 104.9 and 335.5 mg/L nominal concentrations
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 mL Erlenmeyer flask containing 40 mL medium.
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: yes, with an increase of KH2PO4 and NaCO3 to 160 mg/L and 100 mg/L respectively to maintain a constant pH
OTHER TEST CONDITIONS
- Adjustment of pH: Yes, in stock solutions
- Photoperiod: Continuous
- Light intensity and quality: 6000 - 10000 lux
EFFECT PARAMETERS MEASURED:
- Determination of cell concentrations: spectrophotometer readings at 24 h intervals
TEST CONCENTRATIONS
- Range finding study was performed but not reported. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 71 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 645 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- ca. 3.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- - Exponential growth in the control : yes
- Observation of abnormalities: None - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- ErC50: 2.2 mg/L EbC50: 0.9 mg/L - Validity criteria fulfilled:
- yes
- Conclusions:
- The 72 h ErC50 for algae was 645 mg/L and the 72 h NOEC was 3.2 mg/L.
- Executive summary:
A static study was conducted to determine the toxicity of the test substance to Pseudokirchneriella subcapitata, according to EU Method C.3, in compliance with GLP. The exponentially growing P. subcapitata has been assessed over an exposure period of 72 h. In the definitive test the algae were exposed to the nominal concentrations of 0, 3.2, 10.2, 32.8, 104.9 and 335.5 mg/L. No analytical monitoring of the test substance concentrations were performed. Under the study conditions, the 72 h EbC50 and ErC50 of the test substance were determined to be 71 and 645 mg/L, respectively. The 72 h NOEC was determined to be 3.2 mg/L (van Ginkel, 1990).
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well documented study performed according to Industrial standard
- Qualifier:
- according to guideline
- Guideline:
- other: DIN 98 412, Part 9, 1988
- GLP compliance:
- not specified
- Analytical monitoring:
- no
- Details on test solutions:
- Stock solution prepared in double-distilled water. pH adjusted to 7. 7- 8.3
- Test organisms (species):
- Scenedesmus capricornutum
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 48 h
- Test temperature:
- 23- 25°C
- Nominal and measured concentrations:
- Dilution steps 1:2
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Basis for effect:
- growth rate
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The 48 h EC50 to Scenedesmus capricornutum was > 100 mg/L.
- Executive summary:
A static study was conducted to determine the toxicity of the test substance to Scenedesmus capricornutum according to DIN 98 412 (Part 9, 1988). The growth inhibition of S. capricornutum was assessed over an exposure period of 48 h. Details of method and analytical monitoring were not reported. Under the study conditions, the 48 h EC50 was determined to be > 100 mg/L (Kuhn, 1990).
Referenceopen allclose all
Description of key information
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 645 mg/L
- EC10 or NOEC for freshwater algae:
- 3.2 mg/L
Additional information
A static study was conducted to determine the toxicity of the test substance to Pseudokirchneriella subcapitata according to EU Method C.3, in compliance with GLP. The exponentially growing P. subcapitata were assessed over an exposure period of 72 h. In the definitive test, the algae were exposed to nominal concentrations of 0, 3.2, 10.2, 32.8, 104.9, and 335.5 mg/L. No analytical monitoring of the test substance concentrations was performed. Under the study conditions, the 72 h EbC50 and ErC50 of the test substance were determined to be 71 and 645 mg/L, respectively. The 72 h NOEC was 3.2 mg/L (van Ginkel, 1990).
A static study was conducted to determine the toxicity of the test substance to Scenedesmus capricornutum according to DIN 98 412 (Part 9, 1988). The growth inhibition of S. capricornutum was assessed over an exposure period of 48 h. Details of method and analytical monitoring were not reported. Under the study conditions, the 48 h EC50 was determined to be > 100 mg/L (Kuhn, 1990).
A study was conducted to determine the toxicity potential of the test substance to Selenastrum capricornutum according to EU Method C.3. The growth inhibition of S. capricornutum was assessed over an exposure period of 96 h. No details of methods used and analytical monitoring were reported. Under the study conditions, the 96 h EC50 was determined to be 150 mg/L (van Wijk, 1993).
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