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EC number: 201-286-1 | CAS number: 80-51-3
- 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:
- 2004
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- Principles of method if other than guideline:
- NA
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Test concentrations were measured at the beginning (0 hr) and the end (72 hrs) of the study
- Vehicle:
- yes
- Remarks:
- DMF 0.1 mL/L
- Details on test solutions:
- Stock solution was prepared by diluting test chemical in dimethylformamide (100,000 mg/L). Test solutions were prepared by adding the corresponding amounts of stock solution into 1,000 mL of OECD medium. The concentration of solvent was 100 µL/L.
- Test Design
Nominal concentration: control, solvent control, 0.50, 0.82, 1.40, 2.20, 3.70, 6.10, and 10.0 mg/L
Initial cell density: 1 x 104 cells/mL
Number of Replicate: 3 - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- Laboratory culture: ATCC culture medium 625 Gorham’s medium
Supplier: American Type Culture Collection, USA
Strain No.: ATCC 22662
Method of cultivation: Sterilization - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Post exposure observation period:
- no
- Hardness:
- no data
- Test temperature:
- 23 ± 2 °C
- pH:
- pH 7.7 ~ 7.8 at the beginning and pH 8.1 ~ 9.4 at the end of the test
- Dissolved oxygen:
- no data
- Salinity:
- NA
- Nominal and measured concentrations:
- Nominal
Concentration (mg/L) Measured Concentration (mg/L)
O hr % of Nominal 72 hrs % of Nominal
Control < 0.01 – < 0.01 –
Solvent control < 0.01 – < 0.01 –
0.50 0.45 90 < 0.01 < 2
0.82 0.70 85 < 0.01 < 2
1.40 1.17 84 < 0.01 < 1
2.20 1.83 83 < 0.01 < 1
3.70 3.11 84 0.04 1
6.10 5.20 85 0.04 1
10.0 8.21 82 0.08 1 - Details on test conditions:
- Light: 4,000 Lux, Light Periodicity: 24/0 (light/dark)
Shaking: 100 rpm - Reference substance (positive control):
- not specified
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.35 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.059 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- NA
- Results with reference substance (positive control):
- no data
- Reported statistics and error estimates:
- Data analysis: The EC50 value (α=0.05) was calculated by linear regression analysis. The NOEC were determined by an analysis of variance (ANOVA), Williams test, subsequent to Bartlett test for homogenecity of variances. Statistical analyses were performed using Yukms Stalight #4 software (Yukms Corp., Tokyo) and all tests of significance were at α = 0.05, except Bartlett test, which was at α = 0.01.
- Validity criteria fulfilled:
- not specified
- Conclusions:
- 72 hr-EC50 of OBSH to Pseudokirchneriella subcapitata was 0.35 mg/L based on the growth rate and the 72 hr-NOEC was 0.059 mg/L.
- Executive summary:
The toxicity of OBSH towards aquatic algae (Pseudokirchneriella subcapitata) was tested applying the OECD Guideline no. 201. The study was conducted in compliance with GLP. The test was conducted under static test conditions with the following nominal test concentrations: control, solvent control, 0.50, 0.82, 1.40, 2.20, 3.70, 6.10, and 10.0 mg/L. DMF was used as solvent (0.1 mL/L). Based on the results obtained and the mean measired concentrations of the test an ErC50 (72h) of 0.35 mg/L was calculated. The corresponding NOEC was 0.059 mg/L.
Reference
Measured concentration of the test substance in test water under the static condition
Nominal Concentration (mg/L) | Measured Concentration (mg/L) | |||
O hr | % of Nominal | 72 hrs | % of Nominal | |
Control | < 0.01 | – | < 0.01 | – |
Solvent control | < 0.01 | – | < 0.01 | – |
0.50 | 0.45 | 90 | < 0.01 | < 2 |
0.82 | 0.70 | 85 | < 0.01 | < 2 |
1.40 | 1.17 | 84 | < 0.01 | < 1 |
2.20 | 1.83 | 83 | < 0.01 | < 1 |
3.70 | 3.11 | 84 | 0.04 | 1 |
6.10 | 5.20 | 85 | 0.04 | 1 |
10.0 | 8.21 | 82 | 0.08 | 1 |
Cell density ofPseudokirchneriella subcapitata(ATCC 22662) during the test
Nominal Conc. (mg/L) | Measured Con. (mg/L) | Cell density (x 104cell/mL) | |||
0 hr | 24 hrs | 48 hrs | 72 hrs | ||
Control | Control | 1 | 6.32± 0.48 | 45.54± 3.7 | 333.92± 39.23 |
Solvent control | Solvent control | 1 | 6.78± 0.39 | 46.87± 0.96 | 322.92± 5.57 |
0.50 | 0.047 | 1 | 5.75± 0.31 | 42.54± 0.85 | 346.25± 26.41 |
0.82 | 0.059 | 1 | 5.48± 0.26 | 38.50± 1.33 | 313.92± 21.17 |
1.40 | 0.076 | 1 | 4.54± 0.38 | 34.77±2.59 | 279.59± 24.01 |
2.20 | 0.096 | 1 | 4.25± 0.38 | 32.54± 1.53 | 229.59± 23.46 |
3.70 | 0.35 | 1 | 3.24± 0.15 | 21.37± 1.31 | 171.59± 14.64 |
6.10 | 0.46 | 1 | 2.57± 0.40 | 15.44± 2.11 | 131.25± 5.69 |
10.0 | 0.81 | 1 | 2.22± 0.32 | 11.08± 2.67 | 81.15± 34.53 |
Growth inhibition (%) of Pseudokirchneriella subcapitata
Nominal Conc. (mg/L) | Measured Con. (mg/L) | Area under the curve (0~72hrs) | |
Area | Inhibition(%)* | ||
Control | Control | 51,916,000± 5,707,000 | - |
Solvent control | Solvent control | 51,027,000± 677,000 | - |
0.50 | 0.047 | 52,538,000± 2,999,000 | -3.0 |
0.82 | 0.059 | 47,627,000± 2,780,000 | 6.7 |
1.40 | 0.076 | 42,386,000± 3,473,000 | 16.9** |
2.20 | 0.096 | 35,780,000± 3,227,000 | 29.9** |
3.70 | 0.35 | 25,896,000± 1,661,000 | 49.3** |
6.10 | 0.46 | 19,472,000± 1,100,000 | 61.8** |
10.0 | 0.81 | 12,331,000± 4,854,000 | 75.8** |
Nominal Conc. (mg/L) | Measured Con. (mg/L) | Growth rates | |||
Rate (24~48 hrs) | Inhibition (%)* (24~48 hrs) | Rate (24~72hrs) | Inhibition (%)* (24~72 hrs) | ||
Control | Control | 1.94±0.01 | - | 0.0826±0.0010 | - |
Solvent control | Solvent control | 1.93±0.01 | - | 0.0805±0.0016 | - |
0.50 | 0.047 | 1.95±0.03 | -3.6 | 0.0854±0.0015 | -6.1 |
0.82 | 0.059 | 1.92±0.02 | -0.7 | 0.0843±0.0022 | -4.7 |
1.40 | 0.076 | 1.88±0.03 | -5.2 | 0.0858±0.0020 | -6.6 |
2.20 | 0.096 | 1.81±0.03 | -5.2 | 0.0831±0.0004 | -3.2 |
3.70 | 0.35 | 1.71±0.03 | 2.5 | 0.0827±0.0009 | -2.7 |
6.10 | 0.46 | 0.0748±0.0120 | 7.2 | 0.0821±0.0041 | -2.0 |
10.0 | 0.81 | 0.0664±0.0051 | 17.6** | 0.0735±0.0077 | 8.7** |
Description of key information
A reliable ecotoxicity study (72 hr, static) to Pseudokirchnerella subcapitata was carried out according to OECD 201. The 72h-ECr50 (growth rate) was 0.35 mg/L and the NOErC (growth rate) was 0.059 mg/L (mean measured).
The findings are supported in another study with following results: 72h-ECr50 (growth rate) = 0.57 mg/L, NOErC (growth rate) = 0.21 mg/L (mean measured).
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 0.35 mg/L
- EC10 or NOEC for freshwater algae:
- 0.059 mg/L
Additional information
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.
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