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EC number: 688-269-6 | CAS number: 641571-11-1
- 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
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 07 March - 25 March 2005
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 005
- Report date:
- 2005
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 641571-1 1-1
- IUPAC Name:
- 641571-1 1-1
- Details on test material:
- - Name of test material (as cited in study report):AMN 107 B6
- - Physical state:solid
- Analytical purity:100.3 %
-- Lot/batch No.:CHAD0409
- Expiration date of the lot/batch:30 June 2005
- - Stability under test conditions:Stable
- Storage condition of test material:At room temperature in the dark
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
Test solutions
- Vehicle:
- no
Test organisms
- Test organisms (species):
- Scenedesmus capricornutum
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 7.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- dissolved
- Basis for effect:
- cell number
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 24 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- dissolved
- Basis for effect:
- growth rate
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Under the conditions of the present study with Selenastrum capricornutum, AMN107 B6
reduced growth rate of this fresh water algae species significantly at 4.6 mgll and higher.
The ECSOfo r cell growth inhibition (EBCS00:- 72h) was 7.2 mg/l with a 95% confidence interval
ranging from 4.1 to 13 mg/l.
As growth rate is derived from the slope under the growth curve in a logarithmic plot, the
measure of the specific growth rate is preferable aver biomass following from the mathematical
nature of exponential growth.
The EC50 for growth rate reduction (ERCSO0:- 72h) was 24 mgll with a 95% confidence interval
ranging from '1 3 to 45 mgll.
The NOEC for cell growth inhibition was 1.0 mgll, the NOEC for growth rate reduction was 2.2 mg/l. - Executive summary:
Selenastrum capricornutum, Fresh Water Algal Growth Inhibition Test with AMN 107 B6. The study procedures described in this report were based on the IS0 International Standard 8692, 1989. In addition, the procedures were designed to meet the test methods and validity criteria of the EEC directive 92/69, Part C.3, 1992, the OECD guideline No. 201, 1984 and the OECD series on testing and assessment number 23,2000. The batch of AMN 107 B6 was a faintly beige powder with a purity of 100.3%. Analytical results confirmed that AMNI 07 B6 was completely soluble in test medium at the concentrations tested. The project started with a range-finding test exposing exponentially growing algal cultures to a blank-control and a range of AMN 107 B6 concentrations between 0.1 and 100 mg/l increasing by a factor of 10. The results showed that the expected EC, for cell growth inhibition was between 1.0 and 10 mg/l. The expected EC, for growth rate reduction was between 10 and ,100 mg/l. The analytical results showed that the measured concentration in samples taken from an AMN107 B6 concentration of 1.0 mg/l was in agreement with nominal and stable under test conditions for at least 72 hours. The project was continued with a final test exposing exponentially growing algal cultures to a blank-control, a 0.45 pm filtered solution prepared at nominally 46 mg/l and dilutions of the filtrate representing nominal concentrations of 1 .O, 2.2, 4.6, 10 and 22 mg/l. The initial algal cell density was 1 o4 cells/ml and the total test period was 72 hours. Samples for analytical confirmation of actual exposure concentrations were taken from all test concentrations at the start and the end of the test period. Analyses of the samples taken during the final test showed that measured concentrations were in agreement with nominal throughout the 72-hour test period (84-98%). Hence, all results were based on nominal concentrations. Thus, it can be concluded that the observed undissolved material before filtration did not originate from the test substance itself. The study met the acceptability criteria prescribed by the protocol and was considered valid. AMN 107 B6 reduced growth rate of this fresh water algae species significantly at 4.6 mgll and higher. The EC, for cell growth inhibition (EBC5,: Q-72h) was 7.2 mg/l with a 95% confidence interval ranging from 4.1 to '1 3 mg/l. As growth rate is derived from the slope under the growth curve in a logarithmic plot, the measure of the specific growth rate is preferable over biomass following from the mathematical nature of exponential growth. The EC5, for growth rate reduction (ERC5,: 0-72h) was 24 mg/l with a 95% confidence interval ranging from 13 to 45 mg/l. The NOEC for cell growth inhibition was 1.0 mg/l, the NOEC for growth rate reduction was 2.2 mg/l.
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