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Diss Factsheets

Ecotoxicological information

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:
October 2017
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Title:
Unnamed
Year:
2017
Report date:
2018

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Principles of method if other than guideline:
N/A
GLP compliance:
yes

Test material

Constituent 1
Reference substance name:
Saccharides of mannose and galactose from Ceratonia Siliqua seed
IUPAC Name:
Saccharides of mannose and galactose from Ceratonia Siliqua seed
Test material form:
solid: particulate/powder
Details on test material:
- Appearance: beige powder
- Storage: in a dark place at room temperature
- Batch : 14 262
- Manufacturing date: September 19th 2014
- Expiry date: September 19th 2018

Sampling and analysis

Analytical monitoring:
yes
Details on sampling:
Chemical analyses of test item were performed in the test solutions (biotic and abiotic replicates). In order to verify the nominal or initial concentrations of the test item and maintenance of the concentrations during the ecotoxicological testing, chemical analysis in algae test solutions was performed according to the Analytical protocol FCBA chimie no.368-e: version 2, Method for the chemical analysis of Total Carbon (TC) in samples containing the test item from algae ecotoxicology solutions by a Total Organic Carbon analyzer and the following protocol:
- at the beginning of the test (T = 0h)
- at the end of the test (T = 72h)
- for the Control (i.e. algae test medium filtered), the highest and the lowest concentrations and a concentration around expected EC50.


Schedule analysis at initial time (T0h):
Control Abiotic
10 mg/L Abiotic
328 mg/L Abiotic
1050 mg/L Abiotic

Schedule analysis at final time (T72h):
Control Biotic
10 mg/L Biotic
328 mg/L Biotic
1050 mg/L Biotic

Control Abiotic
10 mg/L Abiotic
328 mg/L Abiotic
1050 mg/L Abiotic

The measured concentrations of the test item should not vary more than ± 20 % of nominal or initial measured concentration during the test.
All the solutions were kept in refrigerator or freeze in order to be analyzed if necessary or relevant.

Test solutions

Vehicle:
no
Details on test solutions:
The test item was soluble in the test medium. A concentrated test solution was prepared. Dilutions were then prepared in this medium for each tested concentration.
At the request of the sponsor, the test medium and the five tested concentrations solutions were filtered through a membrane filter (cellulose acetate) with a mesh size of 0.22 μm to sterilizing and all the manipulations were done under sterile conditions to prevent contamination.
Five concentrations (determined from a non-GLP preliminary test) in a geometric serie, were performed plus a Control (Test medium).
Based on the results of the preliminary Test, the following test concentrations 10 – 32 – 102 - 328 and 1050 mg test item /L were proposed for the definitive test in agreement with the Sponsor.

Test organisms

Test organisms (species):
Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum)
Details on test organisms:
Freshwater unicellular green alga Pseudokirchneriella subcapitata of the chlorococcal order (formerly named Raphidocellis subcapitata) strain number CCAP 278.4 was used in this study.
The algae cultures are stored in the laboratory on a solid medium (LC/agar Petri plates) and in a liquid medium with regular sub-culturing (every week).

Study design

Test type:
not specified
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Post exposure observation period:
none

Test conditions

Hardness:
no data
Test temperature:
22.7 – 23.3 °C
pH:
8.0 (Algae test medium)
Dissolved oxygen:
no data
Salinity:
no data
Conductivity:
no data
Nominal and measured concentrations:
Control - 10- 32 – 102 – 328 and 1050 mg
Details on test conditions:
TEST SYSTEM
- Test vessel: 250 mL Erlenmeyer flasks
- Initial cells density: 10000 cells/mL at the start of the test
- No. of vessels per concentration (replicates): 3 biotic replicates per concentration + 1 abiotic replicate for the concentrations: 10, 328 and 1050 mg/L
- Control: 6 biotic replicates + 1 abiotic replicates

TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Algae test medium (OECD medium); Algae dilution water

OTHER TEST CONDITIONS
- Light intensity and quality :6129 Lux

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: The algae growth inhibition in relation to the control was evaluated over a period of 72 h. The algae cells per unit volume were measured during the test at 24,48 and 72 h with a particle counter (Beckman Coulter Z2) and under a microscope with a Malassez counting cell.
- pH: pH of each test concentration was measured at the start and at the end of the test. The pH of the control medium had not increased by more than 1.5 units during the test.

TEST CONCENTRATIONS
According to the results of the preliminary test, we proposed to test five concentrations for this study: 10 – 32 – 102 – 328 and 1050 mg/L.
A growing exponential phase inoculum of the freshwater unicellular alga Pseudokirchneriella subcapitata was added in order to have an initial concentration of 104 cells/mL at the start of the test: 100 mL of algae cultures grown in 250 mL erlenmeyer flasks which were placed in a cooling incubator at a temperature in the range of 21 to 24°C controlled at ± 2°C and under a constant shaking fixed at 120 rpm and a continuous illumination comprised between 4 440 and 8 880 lux.
The algae growth inhibition in relation to the control was evaluated over a period of 72 hours. The algae cells per unit volume were measured during the test at 24, 48 and 72 hours with a particle counter (Beckman Coulter Z2) and/ or under microscope with Malassez counting cell.
Reference substance (positive control):
yes
Remarks:
Potassium dichromate

Results and discussion

Effect concentrationsopen allclose all
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
> 1 050 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Remarks on result:
other: highest tested cocentration
Key result
Duration:
72 h
Dose descriptor:
EC50
Remarks:
yield
Effect conc.:
ca. 386.9 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Details on results:
The results obtained for the test item on the toxicological endpoint “inhibition of growth rate” indicate an ErC50-(0-72h) superior to 1050 mg/L (highest tested cocentration) value expressed in nominal test item concentration.
The results obtained for the test item on the toxicological endpoint “Yield inhibition” indicate an EyC50-(0-72h) equal to 386.9 mg/L, value expressed in nominal test item concentration.
Results with reference substance (positive control):
The last algae growth inhibition test performed with the reference item K2Cr2O7 (September 18 2017) gave an ErC50(0-72h) = 1.11 mg/L (0.98 – 1.24), indicating that the algae sensitivity is correct (within the accepted interval of 0.65 to 1.73 mg/L fixed by the International Standard NF EN ISO 8692 from Mai 2012 as mentioned in the OECD Guideline) and in accordance with previous data obtained by the laboratory.

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
The results obtained for the test item on the toxicological endpoint “inhibition of growth rate” indicate an ErC50-(0-72h) superior to 1050 mg/L (highest tested cocentration) value expressed in nominal test item concentration.
The results obtained for the test item on the toxicological endpoint “Yield inhibition” indicate an EyC50-(0-72h) equal to 386.9 mg/L, value expressed in nominal test item concentration.
In the control, the increase of the biomass during 72 hours was determined to be higher than factor of 16.
The coefficients of variation of daily section-by-section specific growth rate and of average specific growth rate were determined respectively to be less than 35% and 7% in the control.
The validity criteria were successful fulfilled
Executive summary:

The aim of this study was to determine the effects of the test item on the growth of the unicellular green algaPseudokirchneriella subcapitata, according to the OECD 201 guideline (March 2006, corrected July 2011).

The study was carried out in accordance with the study plan n°16/1182F/b dated from January 31, 2017.

There was one deviation during this study.

There was no amendment during this study.

The results of this study are summarized below:

Test system       Pseudokirchneriella subcapitata

Exposure duration       72 hours

Test concentrations       Control - 10- 32 – 102 – 328 and 1050 mg/L

Incubator Temperature       22.7 - 23.3°C; shaking at 120 rpm; light intensity: 6330 Lux

Measurement of cell growth Beckman Coulter Z2

The results obtained for the test item on the toxicological endpoint “inhibition of growth rate” indicate an ErC50-(0-72h) superior to 1050 mg/L (highest tested cocnetration) value expressed in nominal test item concentration.

The results obtained for the test item on the toxicological endpoint “Yield inhibition” indicate an EyC50-(0-72h) equal to 386.9 mg/L, value expressed in nominal test item concentration.

In the control, the increase of the biomass during 72 hours was determined to be higher than factor of 16.

The coefficients of variation of daily section-by-section specific growth rate and of average specific growth rate were determined respectively to be less than 35% and 7% in the control.

The validity criteria were successful fulfilled