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Diss Factsheets
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EC number: 918-811-1 | 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
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:
- 1993
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study was given a reliability rating of 1 because it followed a standard test guideline, which describes a procedure to evaluate this endpoint, and the results were reviewed for reliability and assessed as valid. The study was also conducted under GLP.
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Vehicle:
- no
- Details on test solutions:
- Individual treatment concentrations were prepared as water accommodated fractions (WAF). Control and dilution water were laboratory prepared algal nutrient medium. Test substance was mixed with dilution water in sealed vessels for approximately 24 hours, and the mixtures were allowed to settle for approximately 1 hour prior to drawing off the aqueous phase for testing.
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- Algal cells obtained from testing laboratory cultures. Original algal cultures obtained from American Type Culture Collection (ATCC 22662).
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- Temperature was 22 to 24 Deg C.
- pH:
- The pH ranged from 7.2 to 7.7 at test initiation and 7.2 to 10.2 at test termination.
- Dissolved oxygen:
- Not applicable
- Salinity:
- freshwater
- Nominal and measured concentrations:
- Nominal loading rates were 0.1, 0.4, 1.0, 3.0, and 10 mg/L. Only the 0 and 72 hours samples from the 3.0 and 10 mg/L treatments were analyzed yielding mean measured concentrations of 3.2 and 8.2 mg/L, respectively.
- Details on test conditions:
- Lighting was continuous at approximately 3000 lux.
Test vessels were sealed 300 ml conical flasks that were completely filled with test solution. The treatment and control flasks were inoculated with algal cells to yield initial concentrations ranging from 3200 to 5000 cells/ml. Uninoculated flasks were used to determine particle counts without algal cells. Biomass was calculated as area under the growth curve. - Reference substance (positive control):
- no
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 1 - < 3 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 1 - < 3 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- ca. 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- ca. 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- See Tables Below
- Reported statistics and error estimates:
- EL50 values estimated by visual inspection of data to determine range of loading rates, which bracketed a 50% reduction in biomass and growth rate. ANOVA and Williams test used to determine NOELs.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The hydrocarbons, C10, aromatics, >1% naphthalene, freshwater 72-hr EL50 value for Pseudokirchneriella subcapitata (formerly Selenastrum capricornutum) is 1.0 to 3.0 mg/l based on both growth rate and biomass. The hydrocarbons, C10, aromatics, >1% naphthalene, freshwater 72-hr NOELR (No Observed Effect Loading Rate) value for Pseudokirchneriella subcapitata is approximately 1.0 mg/l based on both growth rate and biomass.
- Executive summary:
The hydrocarbons, C10, aromatics, >1% naphthalene, freshwater 72-hr EL50 value for Pseudokirchneriella subcapitata (formerly Selenastrum capricornutum) is 1.0 to 3.0 mg/l based on both growth rate and biomass. The hydrocarbons, C10, aromatics, >1% naphthalene, freshwater 72-hr NOELR (No Observed Effect Loading Rate) value for Pseudokirchneriella subcapitata is approximately 1.0 mg/l based on both growth rate and biomass.
Reference
Nominal Loading | 72 h |
(mg/L) | % Inhibition |
Control | N/A |
0.1 | -14.0 |
0.4 | -27.0 |
1.0 | -8.0 |
3.0 | 97.0 |
10.0 | 100.0 |
Nominal Loading | Conc. | Conc. |
(mg/L) | 0 hr (cells/mL) | 72 hr (cells/mL) |
Control | 3.2xE3 | 3.7xE5 |
0.1 | 4.6xE3 | 4.2xE5 |
0.4 | 5.3xE3 | 4.7xE5 |
1.0 | 5.4xE3 | 4.0xE5 |
3.0 | 5.2xE3 | 9.3xE5 |
10.0 | 3.5xE3 | 0.0 |
Description of key information
There is no data available for Hydrocarbons, C10, aromatics, <1% naphthalene. However, data is available for a structural analogue, Hydrocarbons, C10 aromatics, >1% naphthalene andpresented in the dossier. This data is read across to based on analogue read across and a discussion and report on the read across strategy is provided as an attachment in IUCLID Section 13.
Water accommodated fractions of hydrocarbons, C10, aromatics, >1% naphthalene, produced a freshwater 72-hr EL50 value for Pseudokirchneriella subcapitata (formerly Selenastrum capricornutum) of 1.0 to 3.0 mg/L based on both growth rate and biomass. The 72-hr NOELR (No Observed Effect Loading Rate) value for Pseudokirchneriella subcapitata is approximately 1.0 mg/L based on both growth rate and biomass.
In a supporting study, water accommodated fractions of hydrocarbons, C10, aromatics, >1% naphthalene, produced a freshwater 72-hr EL50 value for Pseudokirchneriella subcapitata (formerly Selenastrum capricornutum) of 11 mg/L and 8.5 mg/L based on growth rate and biomass, respectively. The 72-hr NOELR (No Observed Effect Loading Rate) value for Pseudokirchneriella subcapitata is 2.5 mg/L based on both growth rate and biomass.
Key value for chemical safety assessment
Additional information
Water accommodated fractions of hydrocarbons, C10, aromatics, >1% naphthalene, produced a freshwater 72-hr EL50 value for Pseudokirchneriella subcapitata (formerly Selenastrum capricornutum) of 1.0 to 3.0 mg/L based on both growth rate and biomass. The 72-hr NOELR (No Observed Effect Loading Rate) value for Pseudokirchneriella subcapitata is approximately 1.0 mg/L based on both growth rate and biomass.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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