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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:
15 December 1998 to 19 December 1998
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Study conducted to GLP in accordance with generally accepted scientific principles, possibly with incomplete reporting or methodological deficiencies, which do not affect the quality of the relevant results.

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1999
Report date:
1999

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
other: EPA OPP 123-2
Deviations:
yes
Remarks:
Test solutions were not analytically verified.
Qualifier:
according to guideline
Guideline:
EPA OTS 797.1050 (Algal Toxicity, Tiers I and II)
Deviations:
yes
Remarks:
Test solutions were not analytically verified.
GLP compliance:
yes

Test material

Constituent 1
Chemical structure
Reference substance name:
4,6-Dichloro-2-ethoxypyrimidine
EC Number:
805-107-3
Cas Number:
40758-65-4
Molecular formula:
C6H6Cl2N2O
IUPAC Name:
4,6-Dichloro-2-ethoxypyrimidine
Test material form:
other: liquid
Details on test material:
- Physical state: liquid

Sampling and analysis

Analytical monitoring:
no

Test solutions

Vehicle:
yes
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION
An initial 100 mg/L primary stock solution was prepared by weighing out approximately 117.8 mg of the test material and dissolving it in 1.2 mL of N,N-dimethyl formamide (DMF).
Serial dilutions of the 100 mg/mL stock were prepared in DMF and a 50 µL aliquot of each of the concentration stocks was diluted with algal assay medium (AAM) to the mark in a 500 mL volumetric flask.
Control AAM and control medium containing 100 µL DMF/L AAM carrier were also prepared.

Test organisms

Test organisms (species):
Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum)
Details on test organisms:
TEST ORGANISM
- Species: Selenastrum capricornutum Printz
- Strain: 1648
- Age of inoculum (at test initiation): 6 days
- Maintenance of algae: stock cultures of algae were maintained aseptically by weekly transfer into sterile algal assay medium (AAM)

Study design

Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
96 h

Test conditions

Test temperature:
24.2 - 25.4 °C
Nominal and measured concentrations:
0 (medium control), 0 (solvent control), 0.31, 0.63, 1.3, 2.5, 5 and 10 mg/L (nominal)
Details on test conditions:
TEST SYSTEM
- Test vessel: sterilised 250 mL borosilicate Erlenmeyer flasks
- Type (delete if not applicable): closed (the flasks had Shimadzu closures)
- Fill volume: 100 mL
- Initial cell density: 11 000 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per medium control (replicates): 3
- No. of vessels per solvent control (replicates): 3

GROWTH MEDIUM
- Standard medium used: yes (Algal Assay Medium) The culture medium used for the definitive test was the same as that used to maintain the stock culture except that the medium used in the toxicity tests did not contain the chelant, Na2EDTA.2H2O
- Preparation of the Algal Assay Medium:
Each stock solution was filtered through a 0.45 µm membrane filter, then stored at 4 °C; the solutions were brought up to room temperature before using. 1 mL of each stock solution A, B1, B2, B3 and D, plus 10 mL of C were added to 900 mL of dilution water. The mixture was then made up to 1 L with additional water.
A: 12.75 g NaNO3, 6.08 g MgCl2.6H2O and 2.20 g CaCl2.2H2O was added to 500 mL dilution water
B1: 7.35 g MgSO4.7H2O dissolved in 500 mL dilution water
B2: 7.5 g NaHCO3 dissolved in 500 mL dilution water
B3: 0.522 g K2PO4 dissolved in 500 mL dilution water
C: 5 mL of number 1 (below) and 5 mL of number 3 (below) diluted to 500 mL with sterile dilution water.
1: 1.86 g H3BO3, 4.17 g MnCl2.4H2O, 0.0327 g ZnCl2 and 0.0726 g NaMoO4.2H2O dissolved in 1000 mL dilution water
2: 2.86 g CoCl2.6H2O and 0.22 g CuCl2.2H2O dissolved in 1000 mL dilution water
3: 2.5 mL of number 2 was made up to 500 mL
D: 0.30 g Na2EDTA.2H2O and 0.16 g FeCl3.6H2O dissolved in 1000 mL dilution water
Finally, the pH was adjusted to 7.0 to 7.5.

OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Photoperiod: continuous illumination
- Light intensity and quality: approximately 3500 - 5250 lux

EFFECT PARAMETERS MEASURED
The algal densities of the inoculum and test cultures were determined by electron particle counting using a Coulter Multisizer. Total cell counts were determined on day 0 and after approximately 96 hours of exposure. Cells were cumulatively counted at a lower threshold equivalent spherical diameter of approximately 2.7 µm to a higher threshold equivalent spherical diameter of approximately 8.6 µm. A blank correction for the algal assay medium used in preparing the dose solutions was also compensated for in the calculations.

PHYSICAL ANALYSIS
The incubator temperature was continuously monitored with a temperature probe which was placed in a representative vessel within the incubator. The light intensity was monitored daily at positions corresponding to the test flasks in the incubator.

TEST CONCENTRATIONS
- Spacing factor for test concentrations: test concentrations were set in a geometric series using a progression factor of approximately 2.0
- Range finding study: yes
- Range finding study concentrations: 0.01, 0.1, 1 and 10 mg/L
- Results used to determine the conditions for the definitive study: yes. The 4 day EC50 value in the range-finding study was greater than 1 mg/L and less than 10 mg/L.
Reference substance (positive control):
no

Results and discussion

Effect concentrationsopen allclose all
Duration:
96 h
Dose descriptor:
EC50
Effect conc.:
2.03 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Remarks on result:
other: 0.62 - 6.63 mg/L (95 % CL)
Duration:
96 h
Dose descriptor:
NOEC
Effect conc.:
0.31 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Details on results:
Effects of the test material on algal growth, relative to the controls, ranged from 13.9 % inhibition of growth at 0.31 mg/L, to 81.9 % inhibition of growth at 10 mg/L by day 4.

The 96 hour EbC50 value for inhibition of growth was 1.98 mg/L with 95 % confidence limits of 0.68 - 5.75 mg/L.
Reported statistics and error estimates:
The EC50 for algal growth was determined by a least squares linear regression of algal cell counts against the common log of the concentrations on day 4. The EbC50 for inhibition of growth was calculated by the regression of the differences in area under the growth curves for each dose group compared to the control against the log of the concentrations for day 4. The No Observed Effect Concentration (NOEC) for algal growth was calculated using the analysis of variance and Dunnett's t test.

Any other information on results incl. tables

Table 1: Mean Values for Total Cell Count/mL

Nominal Conc. (mg/L)

Mean Total Cell Count/mL

Day 0

Day 4

medium

12270

1237727

13076

1255756

11502

1110468

DMF

10696

946396

11106

1115385

11234

1143698

0.31

11144

994530

10396

922399

10922

1013174

0.63

11051

763782

10541

876339

11067

851225

1.3

11321

714943

12751

669035

11032

280775

2.5

10526

692344

11105

568756

10363

615408

5

10233

352460

10833

331939

10568

451382

10

11092

219184

10659

156179

9962

240837

Table 2: Mean Values for Inhibition of Growth

Nominal Conc. (mg/L)

Day 0

Day 4

% Inhibition (Day 4)

media

12283

1201317

-

DMF

11012

1068493

-

0.31

10820

976701

13.9

0.63

10886

830449*

26.8

1.3

11701

554918*

51.1

2.5

10665

625503*

44.9

5

10545

378594*

66.6

10

10571

205400*

81.9

* significant difference from the combined controls; p ≤ 0.05 one tailed Dunnett's t-test on raw data

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
Under the conditions of the study the 96 hour EbC50 for inhibition of growth was 1.98 mg/L. The 96 hour EC50 for algal cell growth was 2.03 mg/L and the No Observed Effect Concentration (algal cell growth) was 0.31 mg/L.
Executive summary:

The toxicity of the test material to aquatic algae was investigated in a study which was conducted under GLP conditions and in accordance with the standardised guidelines EPA OPP 123-2 and EPA OTS 797.1050.

During the study, the freshwater green alga Selenastrum capricornutum Printz was exposed to the test material at concentrations of 0 (medium control), 0 (solvent control), 0.31, 0.63, 1.3, 2.5, 5 and 10 mg/L for 96 hours. Three replicates were set in each treatment group, each with an initial cell density of 11 000 cells/mL. Effects of the test material on algal cell growth, relative to controls, ranged from 13.9 % inhibition of growth at 0.31 mg/L, to 81.9 % inhibition of growth at 10 mg/L by day 4. The EC50 values, together with the NOEC, were based on nominal concentrations.

Under the conditions of the study the 96 hour EbC50 for inhibition of growth was 1.98 mg/L (0.68 - 5.75 mg/L 95 % confidence limits). The 96 hour EC50 for algal cell growth was 2.03 mg/L (0.62 - 6.63 mg/L 95 % confidence limits) and the No Observed Effect Concentration (algal cell growth) was 0.31 mg/L.