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EC number: 305-871-3 | CAS number: 95193-59-2
- 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
- Study period:
- 22/10/2013 - 25/10/2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Study according to international guideline (OECD guideline 201) under GLP. Validity criteria met, deviations from protocol did not adversely affect study integrity.
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- ISO 8692 (Water Quality - Fresh Water Algal Growth Inhibition Test with Scenedesmus subspicatus and Selenastrum capricornutum)
- Deviations:
- no
- Principles of method if other than guideline:
- Not relevant
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not relevant - Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: nominal WAFs of 10, 18, 32, 56 and 100 mg/l.
- Sampling method: 40 ml samples for analysis were taken from extra vessels containing test solutions incubated without algae after 0 and 72 hours. Additionally, reserve samples of 40 ml were taken from all test solutions for possible analysis. If not already used, these samples were stored in a refrigerator for a maximum of three months after delivery of the draft report, pending on the decision of the sponsor for additional analysis.
- Sample storage conditions before analysis: Samples were stored in a refrigerator until analysis. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: The standard test procedures required generation of test solutions, which contained completely dissolved test substance concentrations or stable and homogeneous mixtures or dispersions. The testing of concentrations that would disturb the test system was prevented as much as possible (e.g. film of the test substance on the water surface). No correction was made for the purity/composition of the test substance. The batch of Blown Linseed Oil tested was a hazy yellow to brown viscous liquid and an UVCB substance. The test substance was not completely soluble in test medium at the loading rates prepared.
Preparation started with individual loading rates ranging from 1.0 to 100 mg/l. A 2-day period of magnetic stirring was applied to accelerate the dissolving of the test substance in the test medium. The obtained mixtures were left for a period of 1 hour to stabilise. Subsequently, the aqueous Water Accommodated Fractions (WAFs) were siphoned off and used as test solutions. After preparation, volumes of 50 ml were added to each replicate of the respective test concentration.
- Controls: Yes, controls and blanks withut algae
- Evidence of undissolved material (e.g. precipitate, surface film, etc): The highest WAF in the final test was slightly hazy, whereas the remaining test solutions were all clear and colourless. - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Pseudokirchneriella subcapitata
- Strain: NIVA CHL 1
- Source (laboratory, culture collection): In-house laboratory culture
- 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. 3 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 10^4 cells/ml. The pre-culture was maintained under the same conditions as used in the test. The cell density was measured immediately before use.
ACCLIMATION
- Acclimation period: 3 days
- Culturing media and conditions (same as test or not): same - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Post exposure observation period:
- Not relevant
- Hardness:
- 24 mg/L CaCO3
- Test temperature:
- 22.5 - 23.3ºC
- pH:
- 7.4 - 8.1
- Dissolved oxygen:
- No data
- Salinity:
- Not relevant
- Nominal and measured concentrations:
- Nominal: 10, 18, 32, 56 and 100 mg/L WAF
Measured (t=0h, TOC, corrected for control): 0.5508, 1.2109, 2.7069, 4.0589 and 6.3469 mg/L
Measured (t=72h, TOC, corrected for control): 0.5281, 1.1415, 2.4805, 2.4995 and 5.9645 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: Vessel
- Type (delete if not applicable): closed
- Material, size, headspace, fill volume: Glass, 100 mL filled with 50 mL of test medium
- Aeration: None
- Initial cells density: 1.0 x 10^4 cells/mL
- Control end cells density: 53.6 x 10^4 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- No. of vessels per control (no algae): 2
GROWTH MEDIUM
- Standard medium used: yes, Elendt M1/M2 medium
- Detailed composition if non-standard medium was used:
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Milli-RO water
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
- Culture medium different from test medium: No
- Intervals of water quality measurement: pH at the beginning and end of the test, temperature was recorded continuously in a temperature control vessel
OTHER TEST CONDITIONS
- Photoperiod: Continuous
- Light intensity and quality: TLD-lamps with a light intensity within the range of 91 to 97 uE/m2^/s.
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- 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 720 nm using a spectrophotometer with immersion probe (pathlength =20 mm). Algal medium was used as blank and the extra replicates as background for the treated solutions.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.8
- Range finding study
- Test concentrations: 1, 10 amd 100 mg/L
- Results used to determine the conditions for the definitive study: Yes - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 56 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EL10
- Effect conc.:
- 61 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95%CL: 56 - 64 mg/L
- 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
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 32 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EL10
- Effect conc.:
- 41 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Remarks on result:
- other: 95%CL: 37 - 44 mg/L
- Duration:
- 72 h
- Dose descriptor:
- EL50
- Effect conc.:
- 75 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Remarks on result:
- other: 95%CL: 72 - 78 mg/L
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Observation of abnormalities: Microscopic observations at the end of the test revealed a normal and healthy appearance of the
exposed cells when compared to the control.
- Any stimulation of growth found in any treatment: Yes, in the 10, 18 and 32 mg/L treatments
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: The highest WAF in the final test was slightly hazy, whereas the remaining test solutions were all clear and colourless. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- EC50: 1.3 mg/L - Reported statistics and error estimates:
- For determination of the NOEL and the EL50 the approaches recommended in the OECD guideline 201 were used. An effect was considered to be significant if statistical analysis of the data obtained for the test concentrations compared with those obtained in the negative control revealed significant inhibition of growth rate or inhibition of yield (Williams Multiple Sequential t-test Procedure, α=0.05, one-sided, smaller). Additionally, the EL10 and EL20 were determined to meet the recommendations as put down in "A Review of Statistical Data Analysis and Experimental Design in OECD Aquatic Toxicology Test Guidelines" by S. Pack, August 1993. Calculation of the ELX values was based on probit analysis using linear max. likelihood regression with the percentages of growth rate inhibition and the percentages of yield inhibition versus the logarithms of the corresponding loading rate initially applied. The calculations were performed with ToxRat Professional v. 2.10.05 (ToxRat Solutions® GmbH, Germany).
- Validity criteria fulfilled:
- yes
- Remarks:
- > 16-fold increase in controls, coefficients of variation for section-by-section specific growth rates and average specific growth rates were 9.8 and 2.0% respectively
- Conclusions:
- The acute toxicity (72h-ELr50) of Blown linseed oil towards Pseudokirchneriella subcapitata is > 100 mg/L.
- Executive summary:
The acute toxicity of Blown linseed oil towards Pseudokirchnerialla subcapitata was investigated according to OECD guideline 201 under GLP. Algal cells were exposed to nominal WAFs of 10, 18, 32, 56 and 100 mg/L and were observed for 72 hours. Based on nominal loading rates the 72h-ErL10, 72h-EbL10, 72h-ErL50 and 72h-EbL50 were found to be 61, 41, >100 and 75 mg/L respectively.
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- See attached justification.
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 56 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EL10
- Effect conc.:
- 61 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95%CL: 56 - 64 mg/L
- 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
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 32 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EL10
- Effect conc.:
- 41 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Remarks on result:
- other: 95%CL: 37 - 44 mg/L
- Duration:
- 72 h
- Dose descriptor:
- EL50
- Effect conc.:
- 75 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Remarks on result:
- other: 95%CL: 72 - 78 mg/L
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Observation of abnormalities: Microscopic observations at the end of the test revealed a normal and healthy appearance of the
exposed cells when compared to the control.
- Any stimulation of growth found in any treatment: Yes, in the 10, 18 and 32 mg/L treatments
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: The highest WAF in the final test was slightly hazy, whereas the remaining test solutions were all clear and colourless. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- EC50: 1.3 mg/L - Reported statistics and error estimates:
- For determination of the NOEL and the EL50 the approaches recommended in the OECD guideline 201 were used. An effect was considered to be significant if statistical analysis of the data obtained for the test concentrations compared with those obtained in the negative control revealed significant inhibition of growth rate or inhibition of yield (Williams Multiple Sequential t-test Procedure, α=0.05, one-sided, smaller). Additionally, the EL10 and EL20 were determined to meet the recommendations as put down in "A Review of Statistical Data Analysis and Experimental Design in OECD Aquatic Toxicology Test Guidelines" by S. Pack, August 1993. Calculation of the ELX values was based on probit analysis using linear max. likelihood regression with the percentages of growth rate inhibition and the percentages of yield inhibition versus the logarithms of the corresponding loading rate initially applied. The calculations were performed with ToxRat Professional v. 2.10.05 (ToxRat Solutions® GmbH, Germany).
- Validity criteria fulfilled:
- yes
- Remarks:
- > 16-fold increase in controls, coefficients of variation for section-by-section specific growth rates and average specific growth rates were 9.8 and 2.0% respectively
- Conclusions:
- The acute toxicity (72h-ELr50) of Blown linseed oil towards Pseudokirchneriella subcapitata is > 100 mg/L.
- Executive summary:
The acute toxicity of Blown linseed oil towards Pseudokirchnerialla subcapitata was investigated according to OECD guideline 201 under GLP. Algal cells were exposed to nominal WAFs of 10, 18, 32, 56 and 100 mg/L and were observed for 72 hours. Based on nominal loading rates the 72h-ErL10, 72h-EbL10, 72h-ErL50 and 72h-EbL50 were found to be 61, 41, >100 and 75 mg/L respectively.
Referenceopen allclose all
Individual cell densities
Individual cell densities (x 10^4 cells/mL) | |||||||
WAF (mg/L) | |||||||
Time | Replicate | Control | 10 | 18 | 32 | 56 | 100 |
0h | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
2 | 1 | 1 | 1 | 1 | 1 | 1 | |
3 | 1 | 1 | 1 | 1 | 1 | 1 | |
4 | 1 | ||||||
5 | 1 | ||||||
6 | 1 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1 | 1 | 1 | 1 | 1 | 1 | |
St. Dev.: | 0 | 0 | 0 | 0 | 0 | 0 | |
CV: | 0 | 0 | 0 | 0 | 0 | 0 | |
24h | 1 | 4.151 | 4.260 | 3.766 | 3.696 | 3.333 | 2.388 |
2 | 4.083 | 3.445 | 3.749 | 3.575 | 3.083 | 2.351 | |
3 | 4.039 | 3.575 | 3.948 | 3.661 | 3.124 | 2.004 | |
4 | 4.208 | ||||||
5 | 4.168 | ||||||
6 | 4.377 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 4.2 | 3.8 | 3.8 | 3.6 | 3.2 | 2.2 | |
St. Dev.: | 0.1 | 0.4 | 0.1 | 0.1 | 0.1 | 0.2 | |
CV: | 2.8 | 11.6 | 2.9 | 1.7 | 4.2 | 9.4 | |
48h | 1 | 13.541 | 17.622 | 13.761 | 16.622 | 9.688 | 5.601 |
2 | 12.700 | 14.183 | 14.275 | 15.189 | 10.544 | 5.754 | |
3 | 12.632 | 15.508 | 17.171 | 17.360 | 9.019 | 5.361 | |
4 | 14.506 | ||||||
5 | 13.915 | ||||||
6 | 14.616 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 13.7 | 15.8 | 15.1 | 16.4 | 9.8 | 5.6 | |
St. Dev.: | 0.9 | 1.7 | 1.8 | 1.1 | 0.8 | 0.2 | |
CV: | 6.3 | 11 | 12.2 | 6.7 | 7.8 | 3.6 | |
72h | 1 | 55.207 | 77.040 | 55.616 | 69.421 | 38.076 | 14.146 |
2 | 45.952 | 60.703 | 54.419 | 61.237 | 42.250 | 17.598 | |
3 | 51.912 | 65.086 | 71.855 | 67.536 | 34.898 | 15.414 | |
4 | 56.225 | ||||||
5 | 54.715 | ||||||
6 | 57.483 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 53.6 | 67.8 | 60.6 | 66.1 | 38.4 | 15.7 | |
St. Dev.: | 4.2 | 8.8 | 9.7 | 4.3 | 3.7 | 1.7 | |
CV: | 7.8 | 13 | 16.1 | 6.5 | 9.6 | 11.1 |
Individual growth rates (day^-1)
WAF (mg/L) | |||||||
Time | Replicate | Control | 10 | 18 | 32 | 56 | 100 |
24h | 1 | 1.423 | 1.449 | 1.326 | 1.307 | 1.204 | 0.87 |
2 | 1.407 | 1.237 | 1.321 | 1.274 | 1.126 | 0.855 | |
3 | 1.396 | 1.274 | 1.373 | 1.298 | 1.139 | 0.695 | |
4 | 1.437 | ||||||
5 | 1.427 | ||||||
6 | 1.476 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.428 | 1.320 | 1.340 | 1.293 | 1.156 | 0.807 | |
St. Dev.: | 0.028 | 0.113 | 0.029 | 0.017 | 0.042 | 0.097 | |
CV: | 2.000 | 8.600 | 2.100 | 1.200 | 3.600 | 12.000 | |
48h | 1 | 1.303 | 1.435 | 1.311 | 1.405 | 1.135 | 0.861 |
2 | 1.271 | 1.326 | 1.329 | 1.360 | 1.178 | 0.875 | |
3 | 1.268 | 1.371 | 1.422 | 1.427 | 1.100 | 0.84 | |
4 | 1.337 | ||||||
5 | 1.316 | ||||||
6 | 1.341 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.306 | 1.377 | 1.354 | 1.398 | 1.138 | 0.859 | |
St. Dev.: | 0.032 | 0.055 | 0.059 | 0.034 | 0.039 | 0.018 | |
CV: | 2.400 | 4.000 | 4.400 | 2.400 | 3.400 | 2.100 | |
72h | 1 | 1.337 | 1.451 | 1.339 | 1.413 | 1.213 | 0.833 |
2 | 1.276 | 1.369 | 1.332 | 1.372 | 1.248 | 0.956 | |
3 | 1.317 | 1.392 | 1.425 | 1.404 | 1.184 | 0.912 | |
4 | 1.343 | ||||||
5 | 1.334 | ||||||
6 | 1.350 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.326 | 1.404 | 1.366 | 1.396 | 1.215 | 0.917 | |
St. Dev.: | 0.027 | 0.043 | 0.052 | 0.022 | 0.032 | 0.037 | |
CV: | 2.000 | 3.000 | 3.800 | 1.600 | 2.600 | 4.000 |
Section-by-section growth rate
WAF (mg/L) | |||||||
Time | Replicate | Control | 10 | 18 | 32 | 56 | 100 |
0 - 24h | 1 | 1.400 | 1.400 | 1.300 | 1.300 | 1.200 | 0.9 |
2 | 1.400 | 1.200 | 1.300 | 1.300 | 1.100 | 0.9 | |
3 | 1.400 | 1.300 | 1.400 | 1.300 | 1.100 | 0.7 | |
4 | 1.400 | ||||||
5 | 1.400 | ||||||
6 | 1.500 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.400 | 1.300 | 1.300 | 1.300 | 1.200 | 0.800 | |
St. Dev.: | 0.030 | 0.110 | 0.030 | 0.020 | 0.040 | 0.100 | |
CV: | 2.000 | 8.600 | 2.100 | 1.300 | 3.600 | 12.000 | |
24 - 48h | 1 | 1.200 | 1.400 | 1.300 | 1.500 | 1.100 | 0.900 |
2 | 1.100 | 1.400 | 1.300 | 1.400 | 1.200 | 0.900 | |
3 | 1.100 | 1.500 | 1.500 | 1.600 | 1.100 | 1.000 | |
4 | 1.200 | ||||||
5 | 1.200 | ||||||
6 | 1.200 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.200 | 1.400 | 1.400 | 1.500 | 1.100 | 0.900 | |
St. Dev.: | 0.040 | 0.030 | 0.090 | 0.050 | 0.100 | 0.070 | |
CV: | 3.400 | 2.000 | 6.700 | 3.700 | 8.600 | 7.400 | |
48 - 72h | 1 | 1.400 | 1.500 | 1.400 | 1.400 | 1.400 | 0.900 |
2 | 1.300 | 1.500 | 1.300 | 1.400 | 1.400 | 1.100 | |
3 | 1.400 | 1.400 | 1.400 | 1.400 | 1.400 | 1.100 | |
4 | 1.400 | ||||||
5 | 1.400 | ||||||
6 | 1.400 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.400 | 1.500 | 1.400 | 1.400 | 1.400 | 1.000 | |
St. Dev.: | 0.050 | 0.030 | 0.050 | 0.040 | 0.020 | 0.100 | |
CV: | 3.300 | 1.700 | 3.400 | 2.500 | 1.300 | 9.500 |
Individual yields
WAF (mg/L) | |||||||
Time | Replicate | Control | 10 | 18 | 32 | 56 | 100 |
24h | 1 | 3.151 | 3.260 | 2.766 | 2.696 | 2.333 | 1.388 |
2 | 3.083 | 2.445 | 2.749 | 2.575 | 2.083 | 1.351 | |
3 | 3.039 | 2.575 | 2.948 | 2.661 | 2.124 | 1.004 | |
4 | 3.208 | ||||||
5 | 3.168 | ||||||
6 | 3.377 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 3.171 | 2.760 | 2.821 | 2.644 | 2.180 | 1.248 | |
St. Dev.: | 0.118 | 0.438 | 0.11 | 0.062 | 0.134 | 0.212 | |
CV: | 3.700 | 15.900 | 3.900 | 2.400 | 6.200 | 17.000 | |
48h | 1 | 12.541 | 16.622 | 12.761 | 15.622 | 8.688 | 4.601 |
2 | 11.700 | 13.183 | 13.275 | 14.189 | 9.544 | 4.754 | |
3 | 11.632 | 14.508 | 16.171 | 16.360 | 8.019 | 4.361 | |
4 | 13.506 | ||||||
5 | 12.915 | ||||||
6 | 13.616 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 12.652 | 14.771 | 14.069 | 15.390 | 8.750 | 4.572 | |
St. Dev.: | 0.859 | 1.735 | 1.838 | 1.104 | 0.764 | 0.198 | |
CV: | 6.800 | 11.700 | 13.100 | 7.200 | 8.700 | 4.300 | |
72h | 1 | 54.207 | 76.740 | 54.616 | 68.421 | 37.076 | 13.146 |
2 | 44.952 | 59.703 | 53.419 | 60.237 | 41.250 | 16.598 | |
3 | 50.912 | 64.086 | 70.855 | 66.536 | 33.898 | 14.414 | |
4 | 55.225 | ||||||
5 | 53.715 | ||||||
6 | 56.483 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 52.582 | 66.843 | 59.630 | 65.065 | 37.408 | 14.719 | |
St. Dev.: | 4.175 | 8.847 | 9.740 | 4.286 | 3.687 | 1.746 | |
CV: | 7.900 | 13.200 | 16.300 | 6.600 | 9.900 | 11.900 |
Individual cell densities
Individual cell densities (x 10^4 cells/mL) | |||||||
WAF (mg/L) | |||||||
Time | Replicate | Control | 10 | 18 | 32 | 56 | 100 |
0h | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
2 | 1 | 1 | 1 | 1 | 1 | 1 | |
3 | 1 | 1 | 1 | 1 | 1 | 1 | |
4 | 1 | ||||||
5 | 1 | ||||||
6 | 1 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1 | 1 | 1 | 1 | 1 | 1 | |
St. Dev.: | 0 | 0 | 0 | 0 | 0 | 0 | |
CV: | 0 | 0 | 0 | 0 | 0 | 0 | |
24h | 1 | 4.151 | 4.260 | 3.766 | 3.696 | 3.333 | 2.388 |
2 | 4.083 | 3.445 | 3.749 | 3.575 | 3.083 | 2.351 | |
3 | 4.039 | 3.575 | 3.948 | 3.661 | 3.124 | 2.004 | |
4 | 4.208 | ||||||
5 | 4.168 | ||||||
6 | 4.377 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 4.2 | 3.8 | 3.8 | 3.6 | 3.2 | 2.2 | |
St. Dev.: | 0.1 | 0.4 | 0.1 | 0.1 | 0.1 | 0.2 | |
CV: | 2.8 | 11.6 | 2.9 | 1.7 | 4.2 | 9.4 | |
48h | 1 | 13.541 | 17.622 | 13.761 | 16.622 | 9.688 | 5.601 |
2 | 12.700 | 14.183 | 14.275 | 15.189 | 10.544 | 5.754 | |
3 | 12.632 | 15.508 | 17.171 | 17.360 | 9.019 | 5.361 | |
4 | 14.506 | ||||||
5 | 13.915 | ||||||
6 | 14.616 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 13.7 | 15.8 | 15.1 | 16.4 | 9.8 | 5.6 | |
St. Dev.: | 0.9 | 1.7 | 1.8 | 1.1 | 0.8 | 0.2 | |
CV: | 6.3 | 11 | 12.2 | 6.7 | 7.8 | 3.6 | |
72h | 1 | 55.207 | 77.040 | 55.616 | 69.421 | 38.076 | 14.146 |
2 | 45.952 | 60.703 | 54.419 | 61.237 | 42.250 | 17.598 | |
3 | 51.912 | 65.086 | 71.855 | 67.536 | 34.898 | 15.414 | |
4 | 56.225 | ||||||
5 | 54.715 | ||||||
6 | 57.483 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 53.6 | 67.8 | 60.6 | 66.1 | 38.4 | 15.7 | |
St. Dev.: | 4.2 | 8.8 | 9.7 | 4.3 | 3.7 | 1.7 | |
CV: | 7.8 | 13 | 16.1 | 6.5 | 9.6 | 11.1 |
Individual growth rates (day^-1)
WAF (mg/L) | |||||||
Time | Replicate | Control | 10 | 18 | 32 | 56 | 100 |
24h | 1 | 1.423 | 1.449 | 1.326 | 1.307 | 1.204 | 0.87 |
2 | 1.407 | 1.237 | 1.321 | 1.274 | 1.126 | 0.855 | |
3 | 1.396 | 1.274 | 1.373 | 1.298 | 1.139 | 0.695 | |
4 | 1.437 | ||||||
5 | 1.427 | ||||||
6 | 1.476 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.428 | 1.320 | 1.340 | 1.293 | 1.156 | 0.807 | |
St. Dev.: | 0.028 | 0.113 | 0.029 | 0.017 | 0.042 | 0.097 | |
CV: | 2.000 | 8.600 | 2.100 | 1.200 | 3.600 | 12.000 | |
48h | 1 | 1.303 | 1.435 | 1.311 | 1.405 | 1.135 | 0.861 |
2 | 1.271 | 1.326 | 1.329 | 1.360 | 1.178 | 0.875 | |
3 | 1.268 | 1.371 | 1.422 | 1.427 | 1.100 | 0.84 | |
4 | 1.337 | ||||||
5 | 1.316 | ||||||
6 | 1.341 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.306 | 1.377 | 1.354 | 1.398 | 1.138 | 0.859 | |
St. Dev.: | 0.032 | 0.055 | 0.059 | 0.034 | 0.039 | 0.018 | |
CV: | 2.400 | 4.000 | 4.400 | 2.400 | 3.400 | 2.100 | |
72h | 1 | 1.337 | 1.451 | 1.339 | 1.413 | 1.213 | 0.833 |
2 | 1.276 | 1.369 | 1.332 | 1.372 | 1.248 | 0.956 | |
3 | 1.317 | 1.392 | 1.425 | 1.404 | 1.184 | 0.912 | |
4 | 1.343 | ||||||
5 | 1.334 | ||||||
6 | 1.350 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.326 | 1.404 | 1.366 | 1.396 | 1.215 | 0.917 | |
St. Dev.: | 0.027 | 0.043 | 0.052 | 0.022 | 0.032 | 0.037 | |
CV: | 2.000 | 3.000 | 3.800 | 1.600 | 2.600 | 4.000 |
Section-by-section growth rate
WAF (mg/L) | |||||||
Time | Replicate | Control | 10 | 18 | 32 | 56 | 100 |
0 - 24h | 1 | 1.400 | 1.400 | 1.300 | 1.300 | 1.200 | 0.9 |
2 | 1.400 | 1.200 | 1.300 | 1.300 | 1.100 | 0.9 | |
3 | 1.400 | 1.300 | 1.400 | 1.300 | 1.100 | 0.7 | |
4 | 1.400 | ||||||
5 | 1.400 | ||||||
6 | 1.500 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.400 | 1.300 | 1.300 | 1.300 | 1.200 | 0.800 | |
St. Dev.: | 0.030 | 0.110 | 0.030 | 0.020 | 0.040 | 0.100 | |
CV: | 2.000 | 8.600 | 2.100 | 1.300 | 3.600 | 12.000 | |
24 - 48h | 1 | 1.200 | 1.400 | 1.300 | 1.500 | 1.100 | 0.900 |
2 | 1.100 | 1.400 | 1.300 | 1.400 | 1.200 | 0.900 | |
3 | 1.100 | 1.500 | 1.500 | 1.600 | 1.100 | 1.000 | |
4 | 1.200 | ||||||
5 | 1.200 | ||||||
6 | 1.200 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.200 | 1.400 | 1.400 | 1.500 | 1.100 | 0.900 | |
St. Dev.: | 0.040 | 0.030 | 0.090 | 0.050 | 0.100 | 0.070 | |
CV: | 3.400 | 2.000 | 6.700 | 3.700 | 8.600 | 7.400 | |
48 - 72h | 1 | 1.400 | 1.500 | 1.400 | 1.400 | 1.400 | 0.900 |
2 | 1.300 | 1.500 | 1.300 | 1.400 | 1.400 | 1.100 | |
3 | 1.400 | 1.400 | 1.400 | 1.400 | 1.400 | 1.100 | |
4 | 1.400 | ||||||
5 | 1.400 | ||||||
6 | 1.400 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 1.400 | 1.500 | 1.400 | 1.400 | 1.400 | 1.000 | |
St. Dev.: | 0.050 | 0.030 | 0.050 | 0.040 | 0.020 | 0.100 | |
CV: | 3.300 | 1.700 | 3.400 | 2.500 | 1.300 | 9.500 |
Individual yields
WAF (mg/L) | |||||||
Time | Replicate | Control | 10 | 18 | 32 | 56 | 100 |
24h | 1 | 3.151 | 3.260 | 2.766 | 2.696 | 2.333 | 1.388 |
2 | 3.083 | 2.445 | 2.749 | 2.575 | 2.083 | 1.351 | |
3 | 3.039 | 2.575 | 2.948 | 2.661 | 2.124 | 1.004 | |
4 | 3.208 | ||||||
5 | 3.168 | ||||||
6 | 3.377 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 3.171 | 2.760 | 2.821 | 2.644 | 2.180 | 1.248 | |
St. Dev.: | 0.118 | 0.438 | 0.11 | 0.062 | 0.134 | 0.212 | |
CV: | 3.700 | 15.900 | 3.900 | 2.400 | 6.200 | 17.000 | |
48h | 1 | 12.541 | 16.622 | 12.761 | 15.622 | 8.688 | 4.601 |
2 | 11.700 | 13.183 | 13.275 | 14.189 | 9.544 | 4.754 | |
3 | 11.632 | 14.508 | 16.171 | 16.360 | 8.019 | 4.361 | |
4 | 13.506 | ||||||
5 | 12.915 | ||||||
6 | 13.616 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 12.652 | 14.771 | 14.069 | 15.390 | 8.750 | 4.572 | |
St. Dev.: | 0.859 | 1.735 | 1.838 | 1.104 | 0.764 | 0.198 | |
CV: | 6.800 | 11.700 | 13.100 | 7.200 | 8.700 | 4.300 | |
72h | 1 | 54.207 | 76.740 | 54.616 | 68.421 | 37.076 | 13.146 |
2 | 44.952 | 59.703 | 53.419 | 60.237 | 41.250 | 16.598 | |
3 | 50.912 | 64.086 | 70.855 | 66.536 | 33.898 | 14.414 | |
4 | 55.225 | ||||||
5 | 53.715 | ||||||
6 | 56.483 | ||||||
n: | 6 | 3 | 3 | 3 | 3 | 3 | |
Mean: | 52.582 | 66.843 | 59.630 | 65.065 | 37.408 | 14.719 | |
St. Dev.: | 4.175 | 8.847 | 9.740 | 4.286 | 3.687 | 1.746 | |
CV: | 7.900 | 13.200 | 16.300 | 6.600 | 9.900 | 11.900 |
Description of key information
In a WAF study with Linseed oil, oxidized according to the guideline 201, the EL50 based on the growth rate was observed to be >100 mg/L. The study is used for read across to this dossier with Rape oil, oxidized
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 100 mg/L
- EC10 or NOEC for freshwater algae:
- 61 mg/L
Additional information
One study is available for the toxicity towards algae with Blown Rape oil. The study of Kroon (1992) is disregarded because effects are observed at levels exceeding the solubility limit of the substance and exposure solutions were opaque and inhomogenous. Undissolved material has disturbed the measurements of algal cell density.
The WAF study of Tobor-Kaplon (2013) with Blown Linseed oil is conducted according to the guideline 201 and fulfills all validity criteria. The EL50 based on the growth rate was >100 mg/L. This study is used for read across to this dossier with Rape oil, oxidized. A justification is provided in the read-across justification document.
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.