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EC number: 240-085-3 | CAS number: 15956-58-8
- 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:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Test procedure according to National Standard with acceptable restrictions (e.g. exposure concentrations in the test and the stability of test item were not confirmed by chemical analysis)
- Qualifier:
- according to guideline
- Guideline:
- other: Method: other: German Industrial Standard DIN 38412, Part 9
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- not specified
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- pH:
- 3.82 - 7.98
- Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 500 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: pH adjusted
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 49.3 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95%: 37.9 - 64.1 mg/L
- Remarks:
- not pH-adjusted
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 32 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95 % = 22.9 - 44.6 mg/L
- Remarks:
- not pH-adjusted
Reference
Results related to nominal concentrations
-----------------------------------------
Effect values based on growth rate:
EµC10 (72 h) = 31.94 mg/l (CI 95 % = 22.90 - 44.56)
EµC10 (96 h) = 27.94 mg/l (CI 95 % = 17.81 - 43.83)
EµC50 (72 h) = 49.28 mg/l (CI 95 % = 37.91 - 64.06)
EµC50 (96 h) = 44.39 mg/l (CI 95 % = 31.42 - 62.71)
Effect values based on biomass:
EbC10 (72 h) = 32.54 mg/l (CI 95 % = 16.85 - 62.86)
EbC10 (96 h) = 24.50 mg/l (CI 95 % = 11.10 - 54.05)
EbC50 (72 h) = 60.51 mg/l (CI 95 % = 36.74 - 99.65)
EbC50 (96 h) = 40.62 mg/l (CI 95 % = 22.50 - 73.33)
Cell density values (cells * 10^3/ml):
Concentration (mg/l) 0 h 24 h 48 h 72 h 96 h
0 (Control) 12 28 56 140 415
25 12 28 55 128 290
50 12 27 42 50 70
100 12 17 17 13 13
250 11 10 10 4 4
500 12 8 4 4 4
500 (pH control) 12 23 31 52 75
Inhibition of growth rate and biomass after 72 and 96 h:
Inhibition (%)
Growth rate Biomass
Concentration (mg/l) 72 h 96 h 72 h 96 h
0 (Control) -- -- -- --
25 3.6 10.1 4.4 16.5
50 41.9 50.2 41.1 69.4
100 96.7 97.7 84.7 95.4
250 100.0 100.0 97.5 100.0
500 100.0 100.0 100.0 100.0
500 (pH control) 40.3 48.3 55.0 71.0
Physico-chemical parameters:
pH
Concentration (mg/l) 0 h 96 h
0 (Control) 7.83 7.92
25 7.52 7.77
50 7.19 7.45
100 5.48 5.59
250 4.25 4.30
500 3.82 3.85
500 (pH control) 7.84 7.98
- the temperature was 24.8 °C in all test concentrations
Description of key information
2-ethylhexanoic acid is with high probability acutely not harmful to aquatic algae
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 500 mg/L
- EC10 or NOEC for freshwater algae:
- 130 mg/L
Additional information
In a non-GLP, 72-h static test with the green alga Desmodesmus subspicatus according to German Industrial Standard DIN 38412 part 9, the algae toxicity of 2-ethylhexanoic acid was investigated. The test concentrations were not analytically verified.
As the test substance causes a pH-shift to more acidic conditions with increasing test substance concentrations, the highest test solution (500 mg/L) was tested in parallel after pH-adjustment. Statistical evaluation of the endpoint growth rate revealed an 72 -h ErC50 of 49.3 mg/L (95% CL: 37.9 - 64.1 mg/L, nominal; pH not adjusted) and an 72 -h ErC10 of 31.9 mg/L (95% CL: 22.9 - 44.6 mg/L, nominal; pH not adjusted; BASF AG, 1988, report no.: 2/0949/88).
The algae toxicity of the test substance was influenced by pH effects due to the acidity of the test substance. The toxicity in the pH-adjusted treatment (pH 8) after 72 h was lower (Algae growth inhibition: 40.3 %) compared to the 500 mg/l treatment (Inhibition: 100 %) without buffering the pH (pH < 4). Therefore, the 72 -h ErC50 was determined to be higher than the highest tested concentration (500 mg/L) under pH-adjusted test conditions.
In addition, under supervision of the Japanese Ministry of the Environment a test on the green algae Pseudokirchneriella subcapitata according to OECD 201 and under GLP was conducted and published in 2002. In opposite to the study with the acid, this study was conducted under GLP and the test concentrations were analytically verified. The test concentrations were analytically verified and deviated less than 20% from the nominal concentrations. Moreover, the study was performed with the salt of the acid (Sodium 2-ethylhexanoate, CAS 19766-89-3) which resembles the acid after neutralization. By that, in this study, the algae toxicity of the test substance was not influenced by acidic pH effects. Therefore, the study was used as a key study for the assessment of the algal toxicity of CAS 149-57-5.
In the original study report the 24-h-72 -h NOEC (growth rate) was 130 mg/L, the 24-h-72 -h ErC50 was 500 mg/L (nominal, NITE 2002, report no.: A010465-1).
Overall, based on the available experimental data for the acid and the salt of the acid, it can be concluded that 2-ethylhexanoic acid is with high probability acutely not harmful to aquatic algae.
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