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EC number: 431-480-3 | 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
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 09 Mar 2018 - 06 Apr 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Version / remarks:
- Adopted March 23, 2006; Annex 5 corrected 28 July 2011 and • Guidance document on aquatic toxicity testing of difficult substances and mixtures, OECD series on testing and assessment number 23, 2000
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Test material form:
- solid: particulate/powder
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
- Remarks:
- No analytical monitoring was carried out due to the low solubility of the test item .
- Details on sampling:
- - Concentrations:
Solutions containing 1.0, 10 and 100% of the SS prepared at a loading rate of 100 mg/L.
3 replicates of each test concentration,
6 replicates of the control and limit concentration,
1 extra replicate of each test group for sampling purposes after 24 hours of exposure,
1 or 2 replicates of each test concentration without algae
At the end of the exposure period, the replicates with algae were pooled at each concentration before sampling.
- Sampling method:
Samples for possible analysis were taken from all test concentrations and the control.
In addition, the filter containing the undissolved residue was kept for possible analysis.
Frequency at t=0 h, t=24 h and t=72 h
Volume 2.0 mL from the approximate centre of the test vessels.
- Sample storage conditions before analysis:
Samples were stored in a freezer (≤-15°C) until analysis at the analytical laboratory of the Test Facility.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- The substance tested was a slight yellow powder with a purity of 98% which was not completely soluble in test medium at the loading rate initially prepared.
No correction was made for the purity/composition of the test item.
Preparation of test solutions started with a loading rate of 100 mg/L applying an overnight period of magnetic stirring to ensure maximum dissolution of the test item in medium.
Thereafter, the aqueous Saturated Solution (SS) was collected by filtration through a 0.45 µm membrane filter (RC55, Whatman) and used as the highest test concentration. Lower test concentrations were prepared by subsequent dilutions of the SS in test medium. All test solutions were clear and colorless at the end of the preparation procedure.
After preparation, volumes of 50 mL were added to each replicate of the respective test concentration. Subsequently, 1 mL of an algal suspension was added to each replicate providing a cell density of 104 cells/mL.
Any residual volumes were discarded.
Test organisms
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Raphidocelis subcapitata (formerly known as Pseudokirchneriella subcapitata)
- Strain: strain: NIVA CHL 1
- Source: In-house laboratory culture.
- Age of inoculum (at test initiation): 4 days
- Method of cultivation: Algae stock cultures were started by inoculating growth medium with algal cells from a pure culture on agar. The suspensions were continuously aerated and exposed to light in a climate room at a temperature of 21-24°C.
ACCLIMATION
- Acclimation period: 4 days before the start of the test, cells from the algal stock culture were inoculated in culture medium at a cell density of 1 x 10E4 cells/mL. The pre-culture was maintained under the same conditions as used in the test. The cell density was measured immediately before use.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
Test conditions
- Hardness:
- Hardness (Ca+Mg) 0.24 mmol/L (24 mg CaCO3/L)
- Test temperature:
- 21-24°C.
- pH:
- 8.1 -8.3
- Nominal and measured concentrations:
- Solutions containing 1.0, 10 and 100% of the SS prepared at a loading rate of 100 mg/L.
Samples taken from the undiluted SS were analysed. Test item concentrations were below the Limit of Quantification (LOQ), i.e. 0.008 mg/L, throughout the test. Nevertheless, it can be stated that testing was ultimately performed at the maximum soluble concentration of test item in test medium. Analysis of the filter residue demonstrated the use of the test item during preparation of test solutions. - Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 mL, all-glass, containing 50 mL of test solution
- Static
- Aeration: continuous
- Initial cells density: An initial cell density of 1 x 10E4 cells/mL.
- Control end cells density: In the control, cell density increased by an average factor of at least 16 within the exposure period (i.e. 130).
- No. of organisms per vessel: 1 x 10E4 cells/mL.
- No. of vessels per concentration (replicates): 3 x 104 cells/mL for each test concentration / 6 x 10E4 cells/mL for limit concentration
- No. of vessels per control (replicates): 6 x 10E4 cells/mL.
GROWTH MEDIUM
- Standard medium used: yes
Stock culture medium
M1; according to the NPR 6505 (“Nederlandse Praktijk Richtlijn no. 6505”) formulated using Milli-RO water (tap-water purified by reverse osmosis; Millipore Corp., Bedford, Mass., USA)
NaNO3 500 mg/L
K2HPO4.3H2O 52 mg/L
MgSO4.7H2O 75 mg/L
Na2CO3.10H2O 54 mg/L
C6H8O7.H2O 6 mg/L
NH4NO3 330 mg/L
CaCl2.2H2O 35 mg/L
C6H5FeO7.xH2O 6 mg/L
H3BO3 2.9 mg/L
MnCl2.4H2O 1.81 mg/L
ZnCl2 0.11 mg/L
CuSO4.5H2O 0.08 mg/L
(NH4)6Mo7O24.4H2O 0.018 mg/L
TEST MEDIUM / WATER PARAMETERS
Pre-culture medium M2; according to the OECD 201 Guideline, formulated using Milli-RO water and with the following composition:
NH4Cl 15 mg/L
MgCl2.6H2O 12 mg/L
CaCl2.2H2O 18 mg/L
MgSO4.7H2O 15 mg/L
KH2PO4 1.6 mg/L
FeCl3.6H2O 64 µg/L
Na2EDTA.2H2O 100 µg/L
H3BO3 185 µg/L
MnCl2.4H2O 415 µg/L
ZnCl2 3 µg/L
CoCl2.6H2O 1.5 µg/L
CuCl2.2H2O 0.01 µg/L
Na2MoO4.2H2O 7 µg/L
NaHCO3 50 mg/L
Hardness (Ca+Mg) 0.24 mmol/L (24 mg CaCO3/L)
pH 8.1 ± 0.2
- Source/preparation of dilution water: MMilli-RO water (tap-water purified by reverse osmosis; Millipore Corp., Bedford, Mass., USA)
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 24h (Continuously using TLD-lamps with a light intensity within the range of 68 to 73 µE.m-2.s-1.)
- Light intensity and quality: 60 to 120 µE/m2/s when measured in the photosynthetically effective wavelength range of 400 to 700 nm
- Incubation: Capped vessels were distributed at random in the incubator and daily repositioned. During incubation the algal cells were kept in suspension by continuous shaking.
EFFECT PARAMETERS MEASURED
- pH recorded at the beginning and the end of the test
- The temperature measured in the incubator was maintained between 21 and 22°C.
- Appearance of the cells:
At the end of the final test microscopic observations were performed on the limit concentration to observe for any abnormal appearance of the algae compared to the control.
- Determination of cell concentrations:
At the beginning of the test, cells were counted using a microscope and a counting chamber. Thereafter, cell densities were determined by spectrophotometric measurement of samples at 680 nm using a spectrophotometer with immersion probe (path length =10 mm). Algal medium was used as blank and the extra replicates, without algae, as background for the treated solutions.
Cell densities were recorded at 24-hour intervals in the control and the limit concentration. Intermediate concentrations were measured only at the end of the exposure period.
TEST CONCENTRATIONS
Test item Solutions containing 1.0, 10 and 100% of the SS prepared at a loading rate of 100 mg/L.
Control Test medium without test item or other additives.
Replicates 3 replicates of each test concentration,
6 replicates of the control and limit concentration,
1 extra replicate of each test group for sampling purposes after 24 hours of exposure,
1 or 2 replicates of each test concentration without algae.
A Saturated Solution (SS) was prepared at a loading rate of 100 mg/L and used as the highest test concentration. Lower concentrations were prepared by diluting the highest test concentration in test medium.
A combined limit/range-finding test was performed. Six exponentially growing algal cultures per group were exposed to an untreated control and to an undiluted SS prepared at a loading rate of 100 mg/L in the limit test. In addition, three replicates per group were exposed to solutions containing 1.0 and 10% of the SS in a combined range-finding test. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EL50
- 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:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- No significant differences were recorded between the values for growth rate or yield at any of the test concentrations when compared to the control group.
Microscopic observations at the end of the test revealed a normal and healthy appearance of the algal cells exposed to the limit concentration when compared to the control. - Results with reference substance (positive control):
- - Results with reference substance valid? yes
The EC50 for growth rate inhibition (72h-ERC50) was 1.6 mg/L with a 95% confidence interval ranging from 1.5 to 1.6 mg/L. The historical ranges for growth rate inhibition lie between 0.82 and 2.3 mg/L. Hence, the 72h-ERC50 for the algal culture tested corresponds with this range.
The EC50 for yield inhibition (72h-EYC50) was 0.50 mg/L with a 95% confidence interval ranging from 0.48 to 0.52 mg/L. The historical ranges for yield inhibition lie between 0.43 and 1.1 mg/L. Hence, the 72h-EYC50 for the algal culture tested corresponds with this range.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- In conclusion, under the conditions of the present study with Raphidocelis subcapitata (formerly known as Pseudokirchneriella subcapitata), no inhibition of growth rate and yield was recorded at any of the concentrations of the tested substance.
The EL50 for growth rate (72h-ERL50) and yield (72h-EYL50) inhibition was beyond the range of concentrations tested, i.e. exceeded a loading rate of 100 mg/L.
The 72h-NOEL for growth rate inhibition and yield inhibition was at 100 mg/L. - Executive summary:
The objective of the study was to evaluate test item for its ability to generate toxic effects inRaphidocelis subcapitata(formerly known as Pseudokirchneriella subcapitata)during an exposure period of 72 hours and, if possible, to determine the NOEL, EL10and EL50for both inhibition of growth rate and inhibition of yield.
The study procedures described in this report were based on the OECD guideline No. 201, 2006; Annex 5 corrected 28 July 2011. In addition, procedures were based on the test methods described in the OECD series on testing and assessment number 23, 2000.
The batch of test item tested was a slight yellow powder with a purity of 98% which was not completely soluble in test medium at the loading rate initially prepared.A SaturatedSolution (SS) was prepared at a loading rate of 100 mg/L and used as the highest test concentration. Lower concentrations were prepared by diluting the highest test concentration in test medium.
A combined limit/range-finding test was performed. Six exponentially growing algal cultures per group were exposed to an untreated control and to an undiluted SS prepared at a loading rate of 100 mg/L in the limit test. In addition, three replicates per group were exposed to solutions containing 1.0 and 10% of the SS in a combined range-finding test. The initial algal cell density was 1 x 104cells/mL.The total exposure period was 72 hours and samples for analytical confirmation of actual exposure concentrations were taken at the start, after 24 and 72 hours of exposure.
No significant differences were recorded between the values for growth rate or yield at any of the test concentrations when compared to the control group.
Samples taken from the undiluted SS were analysed. Test item concentrations were below the Limit of Quantification (LOQ), i.e. 0.008 mg/L, throughout the test. Nevertheless, it can be stated that testing was ultimately performed at the maximum soluble concentration of test item in test medium. Analysis of the filter residue demonstrated the use of the test item during preparation of test solutions.
The study met the acceptability criteria prescribed by the study plan and was considered valid.
The effect parameters obtained in this study are summarized in the table below.
Parameter (mg/L)
NOEL
EL10
EL50
Growth rate
100
>100
>100
Yield
100
>100
>100
Due to the very low solubility of test item in water, concentration levels that might be toxic for algae could not be reached.
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