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EC number: 403-830-5 | CAS number: 89331-94-2 B 290; BK 400; CK 34; DIBUTYL-N-102; DX-20; FAT NR. 40391/A; FLUORAN BLACK BD 869; FLUORAN SCHWARZ BD 869; NOIR FLUORANE BD 869; ODB-2; PSD-290; SENOR-2; TG-31; TH-108; WINCON-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:
- 1991-06-21 to 1991-06-24
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 1 mg/L
- Sampling: Water samples (200 mL in duplicate) were taken from test and solvent control cultures at 0 and 72 hours and sent to the HRC Department of Analytical Chemistry for analysis. - Vehicle:
- yes
- Remarks:
- 1% Tween 80-acetone
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: 100 mg test substance was dissolved in auxiliary solvent and the volume made up to 10 mL, 10 µL aliquots of the stock solution dispensed to 100 mL of algal suspension on six occasions to give the required number of replicates at the test level.
- Controls: untreated control
- Chemical name of vehicle: organic solvent - Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Common name: green algae
- Strain No: CCAP 276/20
- Source: Cultre Centre of Algae and Protozoa c/o Freshwater Biological Association, Cumbria, U.K.
- Method of cultivation: Sterile nutrient medium was inoculated from a master culture and incubated under continuous illumination ( = 7000 lux) and stirring (orbital shaker) at 24 °C to give an algal suspension in log phase growth characterised by an absorbance of 0.062 (at 665 nm). The suspension was diluted to an absorbance of 0.022 prior to use. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
- Test temperature:
- 24 ± 1 °C
- pH:
- ca. 8
- Nominal and measured concentrations:
- Nominal: 1.0 mg/L
Measured: 0.76 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: conical flasks
- Type: loosely stoppered
- Material, size, headspace, fill volume: glass , 250 mL, 150 mL, 100 mL
- Aeration: No
- No. of vessels per concentration (replicates): 6
- No. of vessels per control (replicates): 3
- No. of vessels per vehicle control (replicates): 3
GROWTH MEDIUM
- Standard medium used: yes
- Detailed 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 0.08 mg/L
Na2EDTA.2H2O 0.1 mg/L
H3BO3 0.185 mg/L
MnCl2.4H2O 0.415 mg/L
ZnCl2 3x10^-3 mg/L
CoCI2.6H2O 1.5x10^-3 mg/L
CuCI2.2H2O 10^-5 mg/L
Na2MoO4.2H2O 7x10^-3 mg/L
NaHCO3 50 mg/L
OTHER TEST CONDITIONS
- Sterile test conditions: No
- Adjustment of pH: No
- Photoperiod: Continuous
- Light intensity and quality: 7000 lux
EFFECT PARAMETERS MEASURED
- Determination of cell concentrations: absorbance measured at 665 nm, at 0, 24 48 and 72 h.
TEST CONCENTRATIONS
- Test concentrations: nominal 1.0 mg/L, measured 0.76 mg/L - Reference substance (positive control):
- no
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 0.76 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 0.76 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- - Exponential growth in the control (for algal test): Yes
- Observation of abnormalities (for algal test): No
- Unusual cell shape: No
- Colour differences: No
- Flocculation: No
- Adherence to test vessels: No
- Aggregation of algal cells: No
- Any stimulation of growth found in any treatment: No
- Effect concentrations exceeding solubility of substance in test medium: Yes - Validity criteria fulfilled:
- not specified
- Conclusions:
- In this algae growth inhibition study a 72 h-EC50 of above 0.76 mg/L was determined with regard to growth rate. The respective NOEC was set to above or equal 0.76 mg/L.
- Executive summary:
In a 72 hour acute study, cultures of Scenedesmus subspicatus were exposed to the test substance at a nominal concentration of 1 mg/L in accordance with OECD guideline 201 (Huntingdon, 1991). 1.0 mg/L was the highest test concentration that could be prepared due to the limited solubility of the test substance in water and having regard to the amount of auxiliary solvent permitted in the test. However, because of the unstable nature of the test substance in water under light conditions, the calculated mean measured value of 0.76 mg/L over the study period has been quoted. Analysis of test concentrations at 0 and 72 hours expressed as % of nominal were 93 % and 59 % respectively. No abnormalities were observed in any test or control culture inspected at 72 hours.
The NOEC and EC50 values based on growth rate were above or equal to 0.76 mg/L.
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study without detailed documentation
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- GLP compliance:
- yes
- Details on test solutions:
- Identity and concentration of auxiliary solvent for dispersal: The stock solutions were prepared with Tween 80 which was diluted into test water. Appropriate amounts of this stock were added to test water to achieve the required concentration.
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 3.65 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 3.65 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Validity criteria fulfilled:
- not specified
- Conclusions:
- In this algae growth inhibition study a 72h-EC50 of above 3.65 mg/L was determined with regard to biomass. The respective NOEC was set to above or equal 3.65 mg/L.
- Executive summary:
In a 72 hour acute toxicity study, culture of Scenedesmus subspicatus were exposed to the test substance under semi-static conditions in accordance with EU method C.3 as cited in Commission Directive 92/69/EEC (RCC, ECHA RSS, 2017). The stock solutions were prepared with Tween 80 which was diluted into test water. Appropriate amounts of this stock were added to test water to achieve the required concentration.
The substance is poorly water soluble and was tested above the solubility limit. Concentrations higher than those tested could not be maintained in dispersion. No significant inhibition was observed at the highest concentration tested. The bioavailability of the substance cannot be guaranteed during the test and care should be taken in interpreting the results. The figures for EbC50 and NOEbC are above or equal to 3.65 mg/L (biomass) and are based on measured concentrations. EC50 and NOEC are not given for growth inhibition.
Referenceopen allclose all
Table 1: Absorbance Values
Treatment |
Conc., mg/L |
Absorbance Values |
pH |
||||||||
0 h |
Mean |
24 h |
Mean |
48 h |
Mean |
72 h |
Mean |
0 h |
72 h |
||
Control |
0 |
0.022 |
0.022 |
0.078 |
0.077 |
0.203 |
0.204 |
0.354 |
0.351 |
7.9 |
8.0 |
0.022 |
0.078 |
0.213 |
0.359 |
7.9 |
8.1 |
||||||
0.022 |
0.074 |
0.195 |
0.341 |
7.9 |
8.1 |
||||||
Test tem |
0.76 |
0.026 |
0.026 |
0.087 |
0.085 |
0.185 |
0.208 |
0.362 |
0.345 |
7.9 |
8.1 |
0.026 |
0.090 |
0.221 |
0.349 |
7.9 |
8.0 |
||||||
0.026 |
0.087 |
0.215 |
0.348 |
7.9 |
8.0 |
||||||
0.026 |
0.085 |
0.203 |
0.342 |
7.9 |
8.1 |
||||||
0.026 |
0.079 |
0.221 |
0.337 |
7.9 |
8.1 |
||||||
0.026 |
0.084 |
0.201 |
0.329 |
7.9 |
8.1 |
||||||
Solvent Control |
0 |
0.022 |
0.022 |
0.068 |
0.072 |
0.179 |
0.196 |
0.395 |
0.371 |
7.9 |
8.1 |
0.022 |
0.070 |
0199 |
0.347 |
7.9 |
8.1 |
||||||
0.022 |
0.077 |
0.211 |
0.342 |
7.9 |
8.1 |
Table 2: Inhibition of Growth
Measured Conc., mg/L |
Area under the Curve (72 h) |
% Inhibition |
Growth Rate (24 – 48 h) |
% inhibition |
Solvent Control |
9.564 |
- |
0.042 |
- |
0.76 |
9.612 |
<0.5> |
0.037 |
12 |
<Increase>
The substance is poorly water soluble and was tested above the solubility limit. Concentrations higher than those tested could not be maintained in dispersion. No significant inhibition was observed at the highest concentration tested. The bioavailability of the substance cannot be guaranteed during the test and care should be taken in interpreting the results. The figures for EbC50 and NOEC are based on measured concentrations. ErC50 and NOErC are not given.
Description of key information
In an algae test according to OECD guideline 201 (Huntingdon, 1991), an EC50 of >0.76 mg/L and a NOEC of 0.76 mg/L based on growth rate was observed.
Key value for chemical safety assessment
Additional information
Key study
In a 72 hour acute study, cultures of Scenedesmus subspicatus were exposed to the test substance at a nominal concentration of 1 mg/L in accordance with OECD guideline 201 (Huntingdon, 1991). 1.0 mg/L was the highest test concentration that could be prepared due to the limited solubility of the test substance in water and having regard to the amount of auxiliary solvent permitted in the test. However, because of the unstable nature of the test substance in water under light conditions the calculated mean measured value of 0.76 mg/L over the study period has been quoted. Analysis of test concentrations at 0 and 72 hours expressed as % of nominal were 93 % and 59 % respectively. No abnormalities were observed in any test or control culture inspected at 72 hours.
The NOEC and EC50 values based on growth rate were above or equal to 0.76 mg/L and 0.76 mg/L, respectively.
In accordance with Article 25(3) of the REACH Regulation the robust study summaries submitted 12 years previously, are additionally used for the purpose of the registration.
Supporting study
In a 72 hour acute toxicity study, culture of Scenedesmus subspicatus were exposed to the test substance under semi-static conditions in accordance with EU method C.3 as cited in Commission Directive 92/69/EEC (RCC, ECHA RSS, 2017). The stock solutions were prepared with Tween 80 which was diluted into test water. Appropriate amounts of this stock were added to test water to achieve the required concentration.
The substance is poorly water soluble and was tested above its solubility limit. Concentrations higher than those tested could not be maintained in dispersion. No significant inhibition was observed at the highest concentration tested. The bioavailability of the substance cannot be guaranteed during the test and care should be taken in interpreting the results. The figures for EbC50 and NOEbC are above or equal to 3.65 mg/L (biomass) and are based on measured concentrations. EC50 and NOEC are not given for growth inhibition.
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