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EC number: 271-968-1 | CAS number: 68647-71-2
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Remarks:
- by HPLC-MS
- Details on sampling:
- Samples were taken from the control and each test group at 0 hours and from the pooled replicates at 72 hours for quantitative analysis. All samples were taken for immediate analysis. A set of duplicate (reserve) samples was taken at 0 and 72 hours occasion from the additional flasks and stored frozen for further analysis if necessary.
- Vehicle:
- yes
- Remarks:
- water
- Details on test solutions:
- Nominal amounts of test item (5.0, 16, 50, 160 and 500 mg) were each separately added to the surface of 5 liters of culture medium to give the 1.0, 3.2, 10, 32 and 100 mg/L loading rates respectively. After the addition of the test item, the culture medium was stirred by magnetic stirrer using a stirring rate such that a vortex was formed to give a dimple at the water surface. The stirring was stopped after 23 hours and the mixtures allowed to stand for 1 hour. Microscopic observations made on the WAFs indicated that a significant amount of dispersed test item was present in the water column and hence it was considered justifiable to remove the dispersed material by filtering the WAFs through a glass wool plug (2 to 4 cm in length) and one piece of filter paper. A wide bore glass tube, covered at one end with Nescofilm was submerged into the vessel, sealed end down, to a depth of approximately 5 cm from the bottom of the vessel. A length of Tygon tubing was inserted into the glass tube and pushed through the Nescofilm seal. A glass wool plug was inserted into the opposite end of the tubing and the Water Soluble Fraction (WSF)∗ removed by mid-depth siphoning (the first 75 to 100 mL discarded) before passing through a filter paper to give the 1.0, 3.2, 10, 32 and 100 mg/L loading rate WSF. Microscopic observations of the WSFs were performed after filtering and showed no micro-dispersions of test item to be present.
An aliquot (1000 mL) of each of the loading rate WSFs was separately inoculated with algal suspension (7.0 mL) to give the required test concentrations of 1.0, 3.2, 10, 32 and 100 mg/L loading rate WSF. Each test concentration was inverted several times to ensure the algal suspension was fully mixed before dispensing into test vessels. - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- The test was carried out using Pseudokirchneriella subcapitata strain CCAP 278/4. Liquid cultures of Pseudokirchneriella subcapitata were obtained from the Culture Collection of Algae and Protozoa (CCAP), SAMS Research Services Ltd, Scottish Marine Institute, Oban, Argyll, Scotland. Master cultures were maintained in the laboratory by the periodic replenishment of culture medium
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 24 ±1ºC
- pH:
- 7.5 to 8.8
- Nominal and measured concentrations:
- Nominal: 0, 1, 3.2, 10, 32 and 100 mg/L
Measured: 0, 0.527, 1.37, 4.33, 10.9 and 33.1 mg/L - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EL50
- Effect conc.:
- 76 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.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Validity criteria fulfilled:
- yes
- Conclusions:
- Under the conditions of this study, the EL50 and NOEL for growth rate were determined to be 76 mg/L and 10 mg/L loading rate WAF.
- Executive summary:
The effect of the test substance on the growth of the alga Pseudokirchneriella subcapitata was assessed according to OECD Guideline 201 and EU Method C.3 under GLP conditions. Due to the low aqueous solubility and complex nature of the test substance, the test medium was prepared as a water accommodated fraction (WAF). The algal cells were exposed to WAFs of the test substance over a range of nominal loading rates of 0, 1, 3.2, 10, 32 and 100 mg/L (three replicate flasks per concentration) for 72 hours, under constant illumination and shaking at a temperature of 25 ± 2°C. Analysis of the test concentrations at the start revealed measured test concentrations to range from 0.28 and 38 mg/L which varied up to 0.53 to 33 mg/L at 72 hours. Under the conditions of this study, the EL50 and NOEL for growth rate were determined to be 76 mg/L and 10 mg/L loading rate WAF (Hull, 2019).
Reference
Description of key information
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 76 mg/L
- EC10 or NOEC for freshwater algae:
- 10 mg/L
Additional information
The effect of the test substance on the growth of the alga Pseudokirchneriella subcapitata was assessed according to OECD Guideline 201 and EU Method C.3 under GLP conditions. Due to the low aqueous solubility and complex nature of the test substance, the test medium was prepared as a water accommodated fraction (WAF). The algal cells were exposed to WAFs of the test substance over a range of nominal loading rates of 0, 1, 3.2, 10, 32 and 100 mg/L (three replicate flasks per concentration) for 72 hours, under constant illumination and shaking at a temperature of 25 ± 2°C. Analysis of the test concentrations at the start revealed measured test concentrations to range from 0.28 and 38 mg/L which varied up to 0.53 to 33 mg/L at 72 hours. Under the conditions of this study, the EL50 and NOEL for growth rate were determined to be 76 mg/L and 10 mg/L loading rate WAF (Hull, 2019).
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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