Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 406-700-6 | CAS number: 78531-61-0
- 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:
- from 1996-10-15 to 1996-10-18
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Version / remarks:
- 1992
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Details on sampling:
- - No concentrations were measured
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The test was performed with an aqueous extract (eluate) of the test substance. A defined amount of the substance was weighed out and suspended in demineralized water by stirring for about 20 h (Ikamag RCT basic, step 8, at 22 ± 1 °C). Undissolved test substance was removed by filtration with a paper filter, followed by a passage through a membrane filter with a pore diameter of 0.45 µm. The test was performed with the filtrate (eluate).
- Controls: Blank control performed without test substance.
- Evidence of undissolved material: no - Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Common name: algae
- Strain: No. CHODAT SAG 86.81
- Source: Collection of algae cultures, Plant Physiological Institute of the University of Gottingen (Germany)
ACCLIMATION
- Culturing media and conditions: same as the test
- Any deformed or abnormal cells observed: no - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
- Test temperature:
- 23 °C ± 2 °C
- pH:
- - in uninoculated solution: 8
- in inoculated solution: 9.4 - 9.7 - Nominal and measured concentrations:
- - Nominal concentration: 0 (control) and 100 mg/L (Limit test)
- Measured concentrations: No concentrations were measured - Details on test conditions:
- TEST SYSTEM
- Test vessel: Erlenmeyer flask (nominal volume 250 mL) with gas-permeable silicone sponge caps
- Volume: 250 mL
- Initial cells density: 10 000 cells/mL
- No. of vessels per concentration (replicates): 6
- No. of vessels per control (replicates): 3
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: according to OECD guideline
- Culture medium different from test medium: no
- Intervals of water quality measurement: The pH-values were measured after 0 and 72 h in an uninoculated replicate per concentration and after 72 h in an inoculated replicate per concentration. The temperatur was measured continuously.
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: continuous illumination
- Light intensity and quality: approx. 120 µE/(m2-s) in the wavelength range 400 - 700 nm
EFFECT PARAMETERS MEASURED: The purpose of this aquatic toxicity study was to evaluate the inhibitory effect of the test material on the growth of the freshwater green algae species, Desmodesmus subspicatus. The inhibition of the growth in relation to a control was determined over a period of 72 hours.
- Determination of cell concentrations: The algae cell densities were determined after 72 h in a counting chamber (Neubauer improved) in replicate 1 of the inoculated control.
- Chlorophyll measurement: yes. The in vivo Chlorophyll-a fluorescence was measured through pulsed excitation with light flashes having a wavelength of 435 nm after 0, 24, 48, 72 h in an EOS Filterfluorometer FL 2.
TEST CONCENTRATIONS
- Range finding study: not performed - Reference substance (positive control):
- no
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Details on results:
- - Exponential growth in the control: yes
- Observation of abnormalities: no
- Unusual cell shape: not observed
- Colour differences: not observed
- Flocculation: not observed
- Adherence to test vessels: not observed
- Aggregation of algal cells: not observed
- Any stimulation of growth found in any treatment: no
- Any observations that might cause a difference between measured and nominal values: no
- Effect concentrations exceeding solubility of substance in test medium: no - Results with reference substance (positive control):
- No test with reference substance was performed.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The test substance was tested to Desmodesmus subspicatus in a static test system according to OECD 201 (1984). Under the given conditions of this study the 72 h ErC50 value and the NOEC were determined to be > 100 mg/L.
- Executive summary:
The influence of the test material on the growth and growth rate of the green algae species Desmodesmus subspicatus was tested according to OECD 201 (1984) under static and GLP conditions. The algae were exposed to different concentrations of test material and the growth was calculated after 0, 24, 48 and 72 hours of exposure in the test media. The study with the test substance was performed with nominal concentrations of 0 (control) and 100 mg test material/L (limit test) in reconstituted water. Because of the poor water solubility of the test substance no analytics were performed. The study design included three replicates per test material concentration, each containing about 100 mL test medium and 10,000 cells/mL at the start of the experimental phase and a control without algae. A blank control without test substance was performed. No test with reference substance was performed. Under the given conditions of this study the 72 h ErC50 and the NOEC were determined to be > 100 mg/L.
Reference
Table 1: Cell density of the algae, measured via the parameter Chlorophyll-a fluorescence. Means of the relative fluorometer units.
Concentration [mg/L] |
0 h |
24 h |
48 h |
72 h |
Cell density after 72 h [% of the control] |
0 (control) |
40 |
125 |
657 |
2382 |
100 |
100 |
39 |
132 |
796 |
2697 |
113 |
Table 2: Inhibition of the algal growth rates after 72 hours
Concentration [mg/L] |
Biomass |
Growth Rate |
||
|
absolute |
Inhibition [% of the control] |
absolute |
Inhibition [% of the control] |
0 (control) |
1833 |
0.0 |
0.057 |
0.0 |
100 |
2140 |
-16.7 |
0.059 |
-3.7 |
Table 3: pH-values at the start (t = 0 h) and at the end (t = 72 h) of the test
Concentration [mg/L] |
|
48 h 72 h |
Cell density after 72 h [% of the control] |
0 (control) |
8.0 |
8.0 |
9.4 |
100 |
8.0 |
8.0 |
9.7 |
Description of key information
The test substance was tested to Desmodesmus subspicatus in a static test system according to OECD 201 (1984). Under the given conditions of this study (reference 6.1.5-1) the 72 h ErC50 value and the NOEC were determined to be < 100 mg/L.
Key value for chemical safety assessment
Additional information
The influence of the test material on the growth and growth rate of the green algae species Desmodesmus subspicatus was tested according to OECD 201 (1984) under static and GLP conditions. The algae were exposed to different concentrations of test material and the growth was calculated after 0, 24, 48 and 72 hours of exposure in the test media. The study with the test substance was performed with nominal concentrations of 0 (control) and 100 mg test material/L (limit test) in reconstituted water. Because of the poor water solubility of the test substance no analytics were performed. The study design included three replicates per test material concentration, each containing about 100 mL test medium and 10,000 cells/mL at the start of the experimental phase and a control without algae. A blank control without test substance was performed. No test with reference substance was performed. Under the given conditions of this study the 72 h ErC50 and the NOEC were determined to be > 100 mg/L.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
