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EC number: 202-719-7 | CAS number: 98-98-6
- 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
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 11 Aug - 24 Oct 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- The Department of Health of the United Kingdom
Test material
- Reference substance name:
- Pyridine-2-carboxylic acid
- EC Number:
- 202-719-7
- EC Name:
- Pyridine-2-carboxylic acid
- Cas Number:
- 98-98-6
- Molecular formula:
- C6H5NO2
- IUPAC Name:
- pyridine-2-carboxylic acid
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: control, 1.0, 3.2, 10, 32, 100 mg/L
- Sampling method: Samples were taken at the beginning (0 h) and the end of the study (72 h).
- Sample storage conditions before analysis: The samples were stored frozen prior to analysis.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A nominal amount of test item (100 mg) was dissolved in culture medium and the volume adjusted 1 L to give a 100 mg/L stock solution from which a series of dilutions was made to give further stock solutions of 32, 10, 3.2 and 1.0 mg/L. An aliquot (450 mL) of each of the stock solutions was separately inoculated with algal suspension (1.9 mL) to give the required test concentrations of 1.0, 3.2, 10, 32 and 100 mg/L. The stock solutions and each of the prepared concentrations were inverted several times to ensure adequate mixing and homogeneity.
- Eluate: no
- Differential loading: no
- Controls: yes, test medium control
- Evidence of undissolved material (e.g. precipitate, surface film, etc.): No, test solutions were clear and colorless.
Test organisms
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: green algae
- Strain: CCAP 278/4
- Source (laboratory, culture collection): Liquid cultures of Pseudokirchneriella subcapitata were obtained from the Culture Collection of Algae and Protozoa (CCAP), SAMS Research Services Ltd, Scottish Marine Institute, Oban, Argyll, Scotland. Master cultures were maintained in the laboratory by the periodic replenishment of culture medium.
- Preparation of culture for testing: Prior to the start of the test sufficient master culture was added to approximately 100 mL volumes of culture media contained in conical flasks to give an initial cell density of approximately 10E+03 cells/mL. The flasks were plugged with polyurethane foam stoppers and kept under constant agitation by orbital shaker (100 - 150 rpm) and constant illumination at 24 ± 1 °C until the algal cell density was approximately 10E+04 - 10E+05 cells/mL.
ACCLIMATION
- Culturing media and conditions (same as test or not): same as test
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
Test conditions
- Test temperature:
- 24 ± 1 °C
- pH:
- test start: 7.3 (control), 7.3 (1.0 mg/L), 7.3 (3.2 mg/L), 6.9 (10 mg/L), 5.2 (32 mg/L), 5.2 (100 mg/L)
test end: 7.7 (control), 7.9 (1.0 mg/L), 7.9 (3.2 mg/L), 7.7 (10 mg/L), 6.6 (32 mg/L), 5.6 (100 mg/L) - Nominal and measured concentrations:
- nominal: control, 1.0, 3.2, 10, 32, 100 mg/L
measured (0 h): < LOQ, 0.875, 3.06, 9.58, 31.1, 101 mg/L
measured (72 h): < LOQ, 0.824, 3.04, 9.60, 31.6, 102 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: conical flasks
- Type (delete if not applicable): plugged with polyurethane foam bungs
- Material, size, headspace, fill volume: glass, 250 mL, headspace: 150 mL, fill volume: 100 mL
- Aeration: constantly shaken at approx. 150 rpm
- Initial cells density: 5E+03 cells/mL
- Control end cells density: 9.61E+05 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: The culture medium was prepared using reverse osmosis purified deionized water and the pH adjusted to 7.5 with 0.1 N NaOH or HCl.
- Culture medium different from test medium: same as test
- Intervals of water quality measurement: The water quality parameters were checked regularly.
OTHER TEST CONDITIONS
- Photoperiod: continuous illumination
- Light intensity and quality: approximately 7000 lux provided by warm white lighting (380 – 730 nm)
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: Cell density of each flask was determined using a Coulter® Multisizer Particle Counter.
- Other: The shape and size of the algal cells was inspected microscopically and any abnormalities recorded
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 3.2
- Range finding study
- Test concentrations: 0.10, 1.0, 10 and 100 mg/L (perfomed two times)
- Results used to determine the conditions for the definitive study: The results of the initial test showed a flat response occurred in terms of inhibition of growth rate. The results of the second test showed no effect on growth at the test concentrations of 0.10 and 1.0 mg/L. However, growth was observed to be reduced at 10 and 100 mg/L. Based on this information test concentrations of 1.0, 3.2, 10, 32 and 100 mg/L were selected for the definitive test. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate (tested: 28 Nov - 01 Dec 2016)
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 6 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 13 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95% CI: 11 - 16 mg/L
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 4.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: yield
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 6.3 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: yield
- Remarks on result:
- other: 95% CI: 5.6 - 7.1 mg/L
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: yield
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: yield
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test): After 72 h there were no abnormalities detected in the control or test cultures at 1.0 and 3.2 mg/L. Some misshapen cells were observed to be present in the 10 and 32 mg/L test cultures whilst no intact cells were observed to be visible in the 100 mg/L test cultures.
- Any stimulation of growth found in any treatment: no
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: After the 72-hour test period all control, 1.0 and 3.2 mg/L test cultures were observed to be green dispersions. The 10 mg/L test cultures were observed to be pale green dispersions whilst the 32 and 100 mg/L test cultures were observed to be clear colorless solutions.
- Effect concentrations exceeding solubility of substance in test medium: no - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- EC50: ErC50 (72 h) 1.4 mg/L (95% CI: 1.2 - 1.5 mg/L); EyC50 (72 h) 0.60 mg/L (95% CI: 0.52 - 0.69 mg/L) - Reported statistics and error estimates:
- Statistical analysis of the growth rate and yield data was carried out for the control, 1.0, 3.2, 10 and 32 mg/L test groups using one way analysis of variance incorporating Bartlett's test for homogeneity of variance (Sokal and Rohlf, 1981) and Dunnett's multiple comparison procedure for comparing several treatments with a control (Dunnett, 1955).
Any other information on results incl. tables
Analysis of the test preparations at 0 and 72 hours showed measured test concentrations to range from 82% to 102% of nominal and so the results are based on nominal test concentrations only.
Table 1: Inhibition of Growth Rate and Yield in the Definitive Test
Nominal Concentration (mg/L) |
Growth Rate (cells/mL/hour) |
Yield (cells/mL) |
|||
0 – 72 h |
% Inhibition |
0 – 72 h |
% Inhibition* |
||
Control |
R1 |
0.075 |
|
1.07E+06 |
|
R2 |
0.075 |
|
1.11E+06 |
|
|
R3 |
0.077 |
|
1.24E+06 |
|
|
R4 |
0.065 |
- |
5.52E+05 |
- |
|
R5 |
0.071 |
|
8.11E+05 |
|
|
R6 |
0.073 |
|
9.42E+05 |
|
|
Mean |
0.073 |
|
9.56E+05 |
|
|
SD |
0.004 |
|
2.47E+05 |
|
|
1.0 |
R1 |
0.078 |
[7] |
1.41E+06 |
|
R2 |
0.077 |
[5] |
1.32E+06 |
|
|
R3 |
0.078 |
[7] |
1.42E+06 |
|
|
Mean |
0.078 |
[6] |
1.38E+06 |
[44] |
|
SD |
0.001 |
|
5.37E+04 |
|
|
3.2 |
R1 |
0.075 |
[3] |
1.13E+06 |
|
R2 |
0.075 |
[3] |
1.09E+06 |
|
|
R3 |
0.074 |
[1] |
1.02E+06 |
|
|
Mean |
0.075 |
[2] |
1.08E+06 |
[13] |
|
SD |
0.001 |
|
5.96E+04 |
|
|
10 |
R1 |
0.051 |
30 |
1.90E+05 |
|
R2 |
0.050 |
32 |
1.82E+05 |
|
|
R3 |
0.048 |
34 |
1.56E+05 |
|
|
Mean |
0.050 |
32 |
1.76E+05 |
82 |
|
SD |
0.002 |
|
1.79E+04 |
|
|
32 |
R1 |
0.011 |
85 |
6.12E+03 |
|
R2 |
0.008 |
89 |
4.07E+03 |
|
|
R3 |
0.004 |
95 |
1.80E+03 |
|
|
Mean |
0.008 |
90 |
4.00E+03 |
100 |
|
SD |
0.004 |
|
2.16E+03 |
|
|
100 |
R1 |
-0.005 |
107 |
-1.46E+03 |
|
R2 |
-0.005 |
107 |
-1.62E+03 |
|
|
R3 |
-0.004 |
105 |
-1.35E+03 |
|
|
Mean |
-0.005 |
106 |
-1.48E+03 |
100 |
|
SD |
0.001 |
|
1.37E+02 |
|
* In accordance with the OECD test guideline only the mean value for yield for each test concentration is calculated
R1-R6= Replicates 1 to 6
SD = Standard Deviation
[Increase in growth as compared to controls]
Table 2: Validity criteria for OECD 201.
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
The biomass in the control cultures should have increased exponentially by a factor of at least 16 within the 72-hour test period. |
192 |
yes |
The mean coefficient of variation for section-by-section specific growth rates (days 0-1, 1-2 and 2-3, for 72-hour tests) in the control cultures must not exceed 35% |
14% |
yes |
The coefficient of variation of average specific growth rates during the whole test period in replicate control cultures must not exceed 7% in tests with Pseudokirchneriella subcapitata and Desmodesmus subspicatus. For other less frequently tested species, the value should not exceed 10%. |
5% |
yes |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- For further details please refer to “Any other information on results incl. tables”.
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