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EC number: 203-090-1 | CAS number: 103-23-1
- 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:
- key study
- Study period:
- 24 - 27 Oct 1989
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- other: DIN 38412, part 9
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A 500 mg/L stock solution was preparted using 200 mg/L Cremophor as dispersant. After stirring of 17h the test solution was still an emulsion. This emulsion was tested.
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): Cremophor
- Concentration of vehicle in test medium (stock solution and final test solution(s) including control(s)): 200 mg/L
- Evidence of undissolved material (e.g. precipitate, surface film, etc): Test solutions were emulsions. - Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISMS
- Strain: SAG 86.81
- Method of cultivation: temperature: 20°C, stock culture 10000 cells/mL, cultivation in 250 ml Erlenmeyer flasks, test volume 100 mL - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 20 °C
- pH:
- not specified
- Nominal and measured concentrations:
- Nominal: 7.812, 15.625, 31.25, 62.5, 125, 250 and 500 mg/L
- Details on test conditions:
- TEST SYSTEM
- Fill volume: 10 mL
- Initial cells density: 10000 cells/mL
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- No. of vessels per vehicle control (replicates): 4
GROWTH MEDIUM
- Standard medium used: yes (OECD medium)
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: not specified
- Culture medium different from test medium: no
EFFECT PARAMETERS MEASURED: Biomass was recorded after 0, 24, 48 and 72h exposure time.
- Determination of cell concentrations: fluorimeter - Reference substance (positive control):
- no
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 500 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EC20
- Effect conc.:
- 398.6 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 500 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test): no - Validity criteria fulfilled:
- yes
- Conclusions:
- A 72h acute toxicity test with Scenedesmus subspicatus revealed that DEHA is not acutely harmful to freshwater algae up to the saturation limit in water.
- Executive summary:
The study was performed according to DIN guideline 38412, part 9 using Scenedesmus subspicatus as test organism. A 500 mg/L stock solution was preparted using 200 mg/L Cremophor as dispersant. After stirring of 17h the test solution was still an emulsion. This emulsion was tested. Nominal test concentrations between 7.8 and 500 mg/L were tested. The 72h-EC50 value is determined to be > 500 mg/L. An 72h-EC20 value is determined to be 398.6 mg/L. Since the effect concentration is greater than the solubility of DEHA in the test medium, it can be concluded that DEHA is not harmful to freshwater algae up to the saturation limit in water.
- 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: Acceptable, well documented peer-reviewed publication, which meets basic scientific principles
- Qualifier:
- according to guideline
- Guideline:
- other: EPA-600/9-78-018
- GLP compliance:
- no
- Analytical monitoring:
- not specified
- Vehicle:
- no
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Duration:
- 96 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 78 mg/L
- Basis for effect:
- growth rate
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- > 0.78 mg/L
- Basis for effect:
- growth rate
- Validity criteria fulfilled:
- not specified
- Conclusions:
- A 96h acute toxicity test with Selenastrum capricornutum revealed that DEHA is not acutely harmful to freshwater algae up to the saturation limit in water.
- 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:
- other: Guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Version / remarks:
- Cited as Directive 92/69/EEC, C.3
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Vehicle:
- no
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1.4 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- > 1.4 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The concentration of 1.4 mg/L is well above water solubility. It can be concluded that the test substance is not acutely harmful to algae within its water solubility.
Referenceopen allclose all
Description of key information
No toxicity is observed within the limit of water solubility.
Key value for chemical safety assessment
Additional information
Three studies investigating the toxicity of DEHA to feshwater algae are available. The key study was performed according to DIN guideline 38412, part 9 using Scenedesmus subspicatus as test organism (BASF 1989). A 500 mg/L stock solution was preparted using 200 mg/L Cremophor RH40 as dispersant. After stirring of 17h the test solution was still an emulsion. This emulsion was tested. Nominal test concentrations between 7.8 and 500 mg/L were tested. The 72h-EC50 value is determined to be > 500 mg/L. An 72h-EC20 value is determined to be 398.6 mg/L. Since the effect concentration is greater than the solubility of DEHA in the test medium, it can be concluded that DEHA is not harmful to freshwater algae up to the saturation limit in water.
Result and conclusion is confirmed by two supporting studies, which assessed the acute toxicity of DEHA to Selenastrum capricornutum (Felder et al. 1989) and Scenedesmus subspicatus (Hüls 1996), respectively.
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