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EC number: 232-730-2 | CAS number: 9012-33-3
- 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:
- key study
- Study period:
- 20 July 2020 to 08 February 2021
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Version / remarks:
- Please provide version.
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Remarks:
- Only the highest concentration could be measured, as the other concentrations fell below the assay detection limit. Therefore, nominal concentrations were used.
- Details on sampling:
- Only the highest concentration could be measured, as the other concentrations fell below the assay detection limit. Therefore, nominal concentrations were used. Samples were prepared in the presence and absence of algae.
- Concentrations: 260 mg enzyme contrate dry matter/L (equivalent to 100 mg active enzyme protein/L)
- Sample storage conditions before analysis: During the duration of the test, the samples were treated the same as the test concentrations. Thereafter, the samples were stored frozen until analysis. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: Dilution in medium
- Controls: ASTM medium - Test organisms (species):
- Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Raphidocelis subcapitata
- Strain: CCAP 278/4.
- Source (laboratory, culture collection): Original cultures obtained from the Culture Collection of Algae and Protozoa (CCAP), SAMS Research Services Ltd, Scottish Marine Institute, Oban, Argyll, Scotland.
ACCLIMATION
- Acclimation period: Approximately 3 to 4 days before the start of the test, inoculum cultures of algae were set up at an initial cell density of approximately 10^3 cells/mL.
- Culturing media and conditions (same as test or not): Same as test
- Any deformed or abnormal cells observed: No - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Hardness:
- ASTM medium
- Test temperature:
- 23-24⁰C
- pH:
- 7.7-8.6 in control,
7.3-8.6 in test concentrations - Details on test conditions:
- TEST SYSTEM
- Test vessels: 250 ml conical flasks containing 100 ml test solution and loosely stoppered.
- Type: Polyurethane foam bungs.
- Aeration: None. Gaseous exchange and suspension of algal cells maintained by orbital shaker.
- Initial cells density: 5*10^3 cells/mL
- Control end cells density: 5.79*10^5 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- Method of initiation: Serial dilutions with the test substance were prepared and inoculated with algae suspension to achieve the desired concentration.
GROWTH MEDIUM
- Standard medium used: ASTM medium
OTHER TEST CONDITIONS
- Sterile test conditions: No
- Photoperiod: Continuous (approximately 7000 lux).
- Adjustment of pH: No
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: Light microscope. It was not possible to monitor algal cells using a Coulter® Multisizer Particle Counter due to dispersed material interfering with the Coulter counts.
TEST CONCENTRATIONS
- Concentrations: 16.3, 32.6, 65.2 130.4 and 260.7 mg enzyme concentrate dry matter/L.
Medium renewal: None.
Duration of exposure: 72 hours.
Measurement of growth: Light microscope. It was not possible to monitor algal cells using a Coulter® Multisizer Particle Counter due to dispersed material interfering with the Coulter counts. - Reference substance (positive control):
- no
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 50 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: enzyme concentrate dry matter
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 101.7 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: enyzme concentrate dry matter
- Basis for effect:
- yield
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 260.7 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- other: enzyme concentrate dry matter
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 65.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: enyzme concentrate dry matter
- Basis for effect:
- growth rate
- Details on results:
- Mean cell density of control @ 0 h: 0.5 x 10^3 cells/mL
Mean cell density of control @ 72 h: 5.79*10^5 cells/mL
- Exponential growth in the control: yes
- Observation of abnormalities:
- Unusual cell shape: No
- Color differences: No
- Flocculation: No
- Adherence to test vessels: no
- Aggregation of algal cells: Cell clumping was observed to be present in the test cultures at 32.6, 65.2, 130.4 and 260.7 mg enzyme concentrate dry matter/L.
- Any stimulation of growth found in any treatment: Stimulation was observed at the two lowest concentrations 16.3, 32.6 mg enzyme concentrate dry matter/L. - Validity criteria fulfilled:
- yes
- Conclusions:
- Exposure of Raphidocelis subcapitata to beta-N-acetylhexosaminidase revealed an ErC50 > 260.7 mg enzyme concentrate dry matter/L (equivalent to 100 mg active enzyme protein/L). NOEC for both growth rate and yield was 65.2 mg enzyme concentrate dry matter/L and LOEC was 130.4 mg enzyme concentrate dry matter/L. Yield EbC50 was 101.7 mg enzyme concentrate dry matter/L.
- Executive summary:
A study was performed to assess the effect of beta-N-acetylhexosaminidase on the growth of the green algae Raphidocelis subcapitata (formerly known as Pseudokirchneriella subcapitata). The method followed was designed to be compatible with the OECD Guidelines for Testing of Chemicals (2006) No 201, "Freshwater Alga and Cyanobacteria, Growth Inhibition Test" and Method C.3 of Commission Regulation (EC) No 761/2009.
At the request of the Sponsor, Raphidocelis subcapitata was exposed to aqueous dispersions of the test item at nominal concentrations of 16.3, 32.6, 65.2, 130.4 and 260.7 mg enzyme concentrate dry matter/L (three replicate flasks per concentration) for 72 hours, under constant illumination and shaking at temperature of 24 ± 1 °C.
Samples of the algal populations were removed daily and cell concentrations determined for each control and treatment group, using a hemocytometer and light microscope.Analysis of the test preparations was conducted by the Sponsor. Only the highest concentration could be measured, as the other concentrations fell below the assay detection limit. Therefore, nominal concentrations were used in this study. The results for the highest concentration were within 20% of the nominal concentrations. Similar results were seen for samples with and without algae for the highest concentration.
Exposure of Raphidocelis subcapitata to beta-N-acetylhexosaminidase revealed an ErC50 > 260.7 mg enzyme concentrate dry matter/L (equivalent to 100 mg active enzyme protein/L). NOEC for both growth rate and yield was 65.2 mg enzyme concentrate dry matter/L and LOEC was 130.4 mg enzyme concentrate dry matter/L. Yield EbC50 was 101.7 mg enzyme concentrate dry matter/L.
Reference
Description of key information
Exposure of Raphidocelis subcapitata to beta-N-acetylhexosaminidase revealed an ErC50 > 260.7 mg enzyme concentrate dry matter/L (equivalent to 100 mg active enzyme protein/L). NOEC for both growth rate and yield was 65.2 mg enzyme concentrate dry matter/L and LOEC was 130.4 mg enzyme concentrate dry matter/L. Yield EbC50 was 101.7 mg enzyme concentrate dry matter/L.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 260.7 mg/L
- EC10 or NOEC for freshwater algae:
- 62.5
Additional information
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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