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Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

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Reference
Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
key study
Study period:
29 August - 13 October 2006
Reliability:
1 (reliable without restriction)
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 (incl. QA statement)
Remarks:
except for the analysis of the test material
Analytical monitoring:
yes
Details on sampling:
- Concentrations: 0.15, 0.33, 0.726, 1.60, 3.51 and 7.73 mg TOS/L
- Sampling method: Triplicate samples (10 mL) taken at the start of the definitive test from the freshly-prepared control and test media.
- Sample storage conditions before analysis: frozen at ca. -20°C
Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: The test substance was supplied as a frozen liquid and an aliquot of the test substance was thawed. At the four highest concentrations (0.726 to 7.73 mg TOS/L) the test substance (19.9, 21.9, 48.1 and 106 mg) was dispersed in dilution medium (1 or 2 L) in a volumetric flask. The contents of the flasks were inverted 30 times to mix the contents. These preparations were than used directly in the test. At the lower levels, aliquots (206 and 454 mL) of the preparation made at 0.726 mg TOS/L was diluted to provide test media at 0.15 and 0.33 mg TOS/L.
- Controls: one algal nutrient medium control group.
Test organisms (species):
Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum)
Details on test organisms:
TEST ORGANISM
- Common name: green algae
- Strain: CCAP 278/4
- Source (laboratory, culture collection): Culture Collection of Algae and Protozoa (CCAP), SAMS Research Services Ltd., Dunstaffnage Marine Laboratory, Dunbeg, Oban, Argyll, Scotland
- Age of inoculum (at test initiation): three days

Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Test temperature:
22.4 - 24.8 °C
pH:
The pH of the culture medium was adjusted to pH 6 by addition of 0.1 M hydrochloric acid. The pH of the control media was 6.02 at 0 hours and 6.65 at 72 hours. At 72 hours, the pH of the test media at the three lowest levels (0.15 to 0.726 mg TOS/L) had decreased to between 5.01 and 5.11 and at 1.6 and 7.73 mg TOS/L pH values had increased to 7.33 to 7.50.
Nominal and measured concentrations:
Nominal: 0.15, 0.33, 0.726, 1.60, 3.51 and 7.73 mg TOS/L
Measured: 0.0728, 0.137, 0.249, 0.566, 2.62 and 6.87 mg TOS/L
Details on test conditions:
TEST SYSTEM
- Test vessel: 250 mL conical flask
- Type (delete if not applicable): loosely plugged with a foam bung
- Material, size, headspace, fill volume: 250 mL conical flask, 100 mL fill volume
- Initial cells density: appr. 10000 cells/mL
- Control end cells density: 1260000 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: Sterile algal nutrient medium as recommended in Official Journal No. L383A Part C.3 and OECD Procedure 201. Prepared in-house using filtered, dechlorinated tap water which had been softened and treated by reverse osmosis, before microfiltration and purification (resistivity of 18 Megohm/cm).

OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH: yes, adjusted to pH 6 with 0.1 M hydrochloric acid
- Photoperiod: continuous illumination
- Light intensity and quality: 6000-7000 lux provided by a 6 x 30 W 'cool white' 1 metre fluorescent tubes; mean measured values in the range 6080-6730 lux

EFFECT PARAMETERS MEASURED (with observation intervals if applicable): Cell density. Samples were taken at 24, 48 and 72 hours.
- Determination of cell concentrations: Cell densities were measured using a haemocytometer (Improved Neubauer).

TEST CONCENTRATIONS
- Spacing factor for test concentrations: approximately 2.2
- Range finding study
- Test concentrations: 1, 10 and 100 mg TOS/L
- Results used to determine the conditions for the definitive study: yes
Reference substance (positive control):
no
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
0.513 mg/L
Nominal / measured:
meas. (initial)
Conc. based on:
other: total organic solids
Basis for effect:
biomass
Remarks on result:
other: 95% confidence limits 0.441 - 0.606 mg/L
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
290 µg/L
Nominal / measured:
meas. (initial)
Conc. based on:
act. ingr.
Remarks:
active enzyme protein
Basis for effect:
biomass
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
0.073 mg/L
Nominal / measured:
meas. (initial)
Conc. based on:
other: total organic solids
Basis for effect:
biomass
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
41 µg/L
Nominal / measured:
meas. (initial)
Conc. based on:
act. ingr.
Remarks:
active enzyme protein
Basis for effect:
biomass
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
1.48 mg/L
Nominal / measured:
meas. (initial)
Conc. based on:
other: total organic solids
Basis for effect:
growth rate
Remarks on result:
other: 95% confidence limit 1.13 - 2.00 mg/L
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
830 µg/L
Nominal / measured:
meas. (initial)
Conc. based on:
act. ingr.
Remarks:
active enzyme protein
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
0.566 mg/L
Nominal / measured:
meas. (initial)
Conc. based on:
other: total organic solids
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
317 µg/L
Nominal / measured:
meas. (initial)
Conc. based on:
act. ingr.
Remarks:
active enzyme protein
Basis for effect:
growth rate
Details on results:
- Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test): At 3.51 and 7.73 mg TOS/L the algal cells showed signs of cell lysis.
- Any stimulation of growth found in any treatment: no
Reported statistics and error estimates:
The data were compiled in an Excel spreadsheet and analysed using SAS 8.2 (SAS Institute 1999). Test results were expressed in terms of the nominal and initial measured concentrations. The area under the curve was divided by initial count and total time to give AUCP (Area Under the Curve expressed as a Proportion of the initial cell count), where a value of 1 represents no growth and a value of 0 represents complete toxicity (all algae killed). In order to estimate the concentration at which 50% inhibition of growth occurred (EC50), sigmoidal curves were fitted to AUCP and growth rate. For both variables, 0% inhibition was defined as the control mean and 100% inhibition was defined as no growth. The minimum of the curve (for infinite concentration) was bounded between 0 and 1 for AUCP and between -1000 and 0 for growth rate. All 95% confidence intervals for EC50 were calculated using the likelihood ratio method (Donaldson and Schnabel, 1985). For AUC and growth rate, Williams’ test (1971, 1972) was also used to compare each treated group with control unless there was evidence of a non-monotonic dose-response relationship, in which case Dunnett’s test (1955, 1964) was used.
Validity criteria fulfilled:
yes
Conclusions:
After 72 hours of exposure to the test substance, the EbC50 and ErC50, respectively were nominally 1.44 and 2.60 mg TOS/L. Based on the initial measured levels, the 72-hour EbC50 and ErC50 were 0.513 and 1.48 mg TOS/L corresponding to 290 and 830 µg aep/L, respectively. The "no observed effect concentration" (NOEC) of the test substance for the area under the growth curve and growth rate respectively, were 0.33 and 1.6 mg TOS/L; equivalent to 0.0728 and 0.566 mg TOS/L as initial measured.
Executive summary:

The effect of the test substance on the growth of the unicellular green alga Pseudokirchneriella subcapitata was assessed. The study was conducted in accordance with OECD and EC guidelines, and in compliance with GLP.

Triplicate algal cultures, with an initial cell density of 1 x 104/mL, were exposed to the test substance,at nominal concentrations of 0.15, 0.33, 0.726, 1.60, 3.51 and 7.73 mg/L based on Total Organic Solid (TOS). The test media were prepared in OECD algal nutrient medium; because the activity of the active component of the enzyme was reduced under alkaline conditions, the pH of the OECD medium was adjusted to approximately 6 before use. The cultures were incubated in an orbital incubator under continuous illumination at temperatures ranging from 22.4 to 24.8 °C for 72 hours.

The test concentrations were verified by the Sponsor based on the determination of the test substance by ELISA. Since the measured concentrations were lower than nominal values at the start of the exposure period, and little or no test substance was detected at the end, the test results have been calculated in terms of both the nominal and initial measured concentrations (0.0728, 0.137,0.249, 0.566, 2.62 and 6.87 mg TOS/L). The test results are expressed in terms of the area under the growth curve and growth rate.

The following values were derived from the data:

Area under growth curve

EbC50(72 h):

nominal: 1.44 mg TOS/L (1.25,1.64)              

initial measured: 0.513 mg TOS/L (0.441; 0.606) or 290 µg aep/L

No-observed effect concentration:

nominal: 0.33 mg TOS/L

initial measured: 0.0728 mg TOS/L or 41 µg aep/L

Average specific growth rate

ErC50(0-72 h):

nominal: 2.60 mg TOS/L (2.27, 3.04)              

initial measured: 1.48 mg TOS/L (1.13; 2) or 830 µg aep/L

No-observed effect concentration:

nominal: 1.6 mg TOS/L

initial measured: 0.566 mg TOS/L or 317 µg aep/L

Description of key information

After 72 hours of exposure to the test substance, the EbC50 and ErC50, respectively were nominally 1.44 and 2.60 mg total organic substance (TOS)/L. Based on the initial measured levels, the 72-hour EbC50 and ErC50 were 0.513 and 1.48 mg TOS/L corresponding to 290 and 830 µg active enzyme protein (aep)/L, respectively.

The "no observed effect concentration" (NOEC) of the test substance for the area under the growth curve and growth rate respectively, were 0.33 and 1.6 mg TOS/L; equivalent to 0.0728 and 0.566 mg TOS/L as initial measured and 41 µg and 317 µg active enzyme protein (aep)/L, respectively.

CLP Conclusion: Aquatic Chronic 3, H412

Key value for chemical safety assessment

EC50 for freshwater algae:
830 µg/L
EC10 or NOEC for freshwater algae:
317 µg/L

Additional information

The effect of the test substance on the growth of the unicellular green alga Pseudokirchneriella subcapitata was assessed. The study was conducted in accordance with OECD and EC guidelines, and in compliance with GLP.

Triplicate algal cultures were exposed to the test substance for 72 hours, at nominal concentrations of 0.15, 0.33, 0.726, 1.60, 3.51 and 7.73 mg/L based on Total Organic Solid (TOS). The test media were prepared in OECD algal nutrient medium adjusted to pH 6 due to the reduced activity of the enzyme under alkaline conditions. The test concentrations were verified by the Sponsor based on the determination of the test substance by ELISA.

The test results are expressed in terms of the area under the growth curve and growth rate and are given in both nominal and initial measured concentrations.

The following values were derived from the data:

Area under growth curve

EbC50 (72 h):

nominal: 1.44 mg TOS/L (95% C.L.: 1.25,1.64)              

initial measured: 0.513 mg TOS/L (95% C.L.: 0.441; 0.606) or 290 µg aep/L

No-observed effect concentration:

nominal: 0.33 mg TOS/L

initial measured: 0.0728 mg TOS/L or 41 µg aep/L

Average specific growth rate

ErC50 (0-72 h):

nominal: 2.60 mg TOS/L ( 95% C.L.: 2.27, 3.04)              

initial measured: 1.48 mg TOS/L (95% C.L.: 1.13; 2) or 830 µg aep/L

No-observed effect concentration:

nominal: 1.6 mg TOS/L

initial measured: 0.566 mg TOS/L or 317 µg aep/L