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EC number: 202-259-7 | CAS number: 93-58-3
- 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:
- 1992-07-14 to 1992-07-17
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: stock solution was prepared by dissolving 1 g test substance per litre dilution water - Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Common name: green alga
- Strain: CHODAT (86.81 SAG)
- Source (laboratory, culture collection): initially obtained from the Institut für Wasser-, Boden- und Lufthygiene, Berlin, Germany and cultures then maintained in testing laboratory
- Method of cultivation: in sterile Erlenmeyer flasks under light (ca. 8000 lux, white) - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 24 ± 2 °C
- pH:
- study start: 8.1
study end: 7.8 to 9.5 - Nominal and measured concentrations:
- Nominal concentrations: control, 30, 60, 100, 170, 300, 500 and 900 mg/L
- Details on test conditions:
- TEST SYSTEM
- Type: not reported
- Material, size, headspace, fill volume: Erlenmeyer flasks
- Aeration: with sterile air
- Initial cells density: 20000/mL
- Control end cells density: 1150000/mL
- No. of vessels per concentration (replicates): 8
- No. of vessels per control (replicates): 5
GROWTH MEDIUM
- Standard medium used: not reported
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: tap water; information of composition not available
OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH: no, but significant increase in pH was observed in some test flasks
- Photoperiod: test performed under continuous light
- Light intensity and quality: ca. 8000 lux
EFFECT PARAMETERS MEASURED: growth rate
- Determination of cell concentrations: photometric cell number determination - Reference substance (positive control):
- no
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 111.9 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 62.4 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- Complete growth inhibition was observed with test concentrations equal to or greater than 300 mg/L. The pH values of some test and control vessels was significantly increased at the end of the study period. However, this change had no influence on the cell growth and was considered to not affect the validity of the test.
- Reported statistics and error estimates:
- The effect concentrations were calculated after Probit transformation of percentages of inhibition by regression analysis followed by a Probit analysis according to Cavalli-Sforza (1972).
The validity of the study was evaluated with ToxRat v.3.3. - Validity criteria fulfilled:
- yes
- Conclusions:
- The substance inhibited the growth of the green alga Desmodesmus subspicatus and the observed EC50 value (based on growth rate) was 111.9 mg/L after 72 hours.
- Executive summary:
The toxicity of the test substance methyl benzoate to the green alga Desmodesmus subspicatus was tested under GLP in a static test over a period of 72 hours in accordance with OECD TG 201. The test substance was directly added to dilution water at 1 g/L and test solutions were prepared from this stock solution. The study was performed with five controls using dilution water and eight replicates of nominal test concentrations of methyl benzoate in dilution water of 30, 60, 100, 170, 300, 500 and 900 mg/L. Tests were conducted at 24 ± 2 °C in Erlenmeyer flasks with sterile aeration with an initial cell density of 20000 cells/mL under constant white light at ca. 8000 lux. The cell number was counted photometrically. The cell growth was completely inhibited at concentrations equal to or greater than 300 mg/L. The EC50 value based on growth rate was 111.9 mg/L and the EC10 value was 62.4 mg/L. A significant increase in the pH value was seen in some of the test and control flasks, which had no influence on cell growth.
Reference
Description of key information
The substance exhibited low acute toxicity to freshwater algae. In a 72-hour study with Desmodesmus subspicatus the ErC50 for inhibition of the growth rate was 111.9 mg/L.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 111.9 mg/L
- EC10 or NOEC for freshwater algae:
- 62.4 mg/L
Additional information
The algal toxicity of the registration item methyl benzoate to the freshwater green alga Desmodesmus subspicatus was studied in a valid test in accordance with EU Method C.3. The substance inhibited the cell growth and the ErC50 value was 111.9 mg/L. Complete growth inhibition was seen at 300 mg/L or greater.
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