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Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

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Link to relevant study record(s)

Reference
Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2009-04-27 to 2010-06-07
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Analytical monitoring:
yes
Details on sampling:
- Concentrations: The fractions C20 and C22 of C20/22 ATQ trocken were analytically determined from all test concentrations and the control after 0 h (test start) and 72 h (test end).
- Sampling method: Samples at start and end of the test were taken directly from the test replicates.
- Sample storage conditions before analysis: All samples were stored at room temperature before preparation and before analysis.
Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A stock solution of 40 mg/L was freshly prepared with test medium and treated with ultrasound for 30 min.
- Eluate: Natural river water
- Differential loading: 0.020 - 0.063 - 0.20 - 0.63 - 2.00 - 6.32 - 20.0 mg/L
- Controls: Six replicates without test item were tested under the same test conditions as the test replicates.
Test organisms (species):
Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
Details on test organisms:
TEST ORGANISM
- Common name: Desmodesmus subspicatus Chodat
- Strain: SAG 86.81
- Source (laboratory, culture collection): SAG Pflanzenphysiologisches Institut der Universitaet Goettingen, Nikolausberger Weg 18, D-37073 Goettingen, Germany
- Age of inoculum (at test initiation): 4 days
- Method of cultivation: Fresh stocks were prepared from Z-Agar. Light intensity amounted 35 - 70 µE x m-2 x s-1 for 24 h per day.


ACCLIMATION
- Culturing media and conditions (same as test or not): Same as test
- Any deformed or abnormal cells observed: No
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Post exposure observation period:
After 72 hours of exposure, 0.5 – 1 mL aliquots of the test medium (i.e. samples of exposed algal cells) from the nominal concentrations of 2.00 – 20.0 mg/L (geometric mean measured 1.39 – 15.4 mg/L) and control were transferred to 10 mL untreated test medium. Algae were then allowed to grow for further 3 - 7 days under test conditions. The test item effect was observed to be reversible at these concentrations. Therefore, there is potential for recovery following exposure up to 15.4 mg/L (highest geometric mean measured test concentration).
Please refer to the respective table below.
Hardness:
Not measured
Test temperature:
Mean: 23 °C, Min: 22 °C, Max: 24 °C
Adsorption on Glass - Test:
Mean: 21.5 °C, Min: 21 °C, Max: 22 °C
pH:
Geometric mean measured test item concentration of C20/22 ATQ trocken1)
pH-value
[mg/L] Start; 0 h End; 72 h
15.4 7.98 7.87
4.39 7.97 7.84
1.39 7.95 7.91
0.443 7.93 7.92
0.128 7.91 7.89
0.0405 7.88 7.89
0.0110 7.84 7.89
Control 7.91 7.87

Adsorption on Glass-Test:
Nominal test item concentration pH-value
[mg/L] Start; 0 h End; 72 h
6.32 7.88 7.96
2.00 7.88 7.93
0.630 7.89 7.90
Control 7.91 7.87
Dissolved oxygen:
Not measured
Salinity:
Not measured, freshwater
Nominal and measured concentrations:
Please refer to "Any other information on materials and methods incl. tables"
Details on test conditions:
TEST SYSTEM
- Test vessel: 250 mL Erlenmeyer flasks
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: sterile 250 mL Erlenmeyer flasks, test volume 100 mL
- Aeration: Test containers were placed on a rotary shaker and oscillated at appr. 70 rpm
- Type of flow-through (e.g. peristaltic or proportional diluter): None
- Renewal rate of test solution (frequency/flow rate): One application at test start
- Initial cells density: 4996 cells/mL
- Control end cells density: Mean 1038146 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- No. of vessels per vehicle control (replicates): None


GROWTH MEDIUM
- Standard medium used: yes



TEST MEDIUM / WATER PARAMETERS
Water of the river Innerste was used. This river is located in
Sarstedt / Ruthe. Water parameters are given below. Additionally 50 % of the components of the dilution water (total application volume 6.5 mL/L) acc. to the guideline were added to enable a sufficient growth of algae
Water Parameters of the River Water

River Innerste
Location D-31157 Sarstedt / Ruthe, Ruther Straße, Innerste
Sampling Date 2009-02-12
Weather on Day of Sampling dry, sunny, ca. 1 °C
Colour Slightly, turbid, yellowish
pH 8.08
Conductivity [µS/cm] 887
DOC [mg C/L] 2.8
TOC [mg C/L] 2.9
Ammonium-N [mg N/L] 0.163
Nitrate-N [mg N/L] 6.10
o-Phosphate-P [mg P/L] 0.103
Total Phosphate [mg P/L] 0.152
Suspended Matter [mg/L] 24
Total Hardness [mg CO3/L] 338




OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: no
- Photoperiod: 24 h
- Light intensity and quality: 60 - 120 µE x m-2 x s-1



EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: [counting chamber; electronic particle counter; fluorimeter; spectrophotometer; colorimeter] Fluorimeter, via Chlorophyll-a fluorescence (excitation at 436 nm, emission at 685 nm), cell concentrations were related to all cell density values acc. to a calibration curve.



TEST CONCENTRATIONS
- Range finding study: Yes
Results of the Range Finding Test (0-72 h)

Nominal
Test Item Concentration
[mg/L] Specific Growth Rate Inhibition [%] Yield Inhibition [%]
10 45 89
1 0 0
0.1 -1 -3
0.01 -1 -4








Reference substance (positive control):
yes
Remarks:
Potassium dichromate
Key result
Duration:
72 h
Dose descriptor:
EC10
Effect conc.:
0.78 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
growth rate
Remarks on result:
other: 0.63-0.95
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
3.48 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
growth rate
Remarks on result:
other: (3.28 - 3.70)
Details on results:
- Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test):
- Unusual cell shape: No
- Colour differences: No
- Flocculation: No
- Adherence to test vessels: No
- Aggregation of algal cells: No
- Other: No
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: No
Results with reference substance (positive control):
- Results with reference substance valid? Yes
- EC50:
Rate-related inhibition: 0.695 (CI 0.657 - 0.729) mg/L
Yield Inhibition: 0.320 (CI 0.294 - 0.358) mg/L
Reported statistics and error estimates:
EC10-, EC20- and EC50-values of the growth rate and yield inhibition after 72 h were calculated by sigmoidal dose-response regression. Calculation of the confidence intervals EC10-, EC20- and EC50-values were carried out using standard procedures.

EC - values and 95 % Confidence Intervals of C20/22 ATQ trocken (0-72 h)

                                            (based on the geometric mean measured test item concentrations of C20/22ATQ

                                 trocken)1) [mg/L]

Rate-related Inhibition

ErC10

0.927 (0.798 – 1.07)

ErC20

1.53 (1.38 – 1.68)

ErC50

3.48 (3.28 – 3.70)

Inhibition of Yield

EyC10

0.412 ( 0.0110 – 0.757)

EyC20

0.678 (0.482 – 0.914)

EyC50

1.17 (0.955 – 1.30)

Cell Densities

 

Geometric mean measured test item concentration of            C20/22 ATQ trocken1)

Replicate

Cell density [cells/mL]

[mg/L]

No.

0 h

24 h

48 h

72 h

 

15.4

1

4996

16961

2910

8840

 

2

4996

17392

4763

6501

 

3

4996

16236

3905

5645

 

Mean

4996

16863

3859

6995

 

4.39

1

4996

17740

26897

39859

 

2

4996

19896

26979

46414

 

3

4996

20513

26112

42600

 

Mean

4996

19383

26663

42958

 

1.39

1

4996

25519

117447

430852

 

2

4996

27670

104868

334361

 

3

4996

25982

117267

421409

 

Mean

4996

26390

113194

395541

 

0.443

1

4996

28773

172202

982629

 

2

4996

25717

158800

875632

 

3

4996

28127

176993

939302

 

Mean

4996

27539

169332

932521

 

0.128

1

4996

28593

188188

1025336

 

2

4996

26997

169225

946990

 

3

4996

30024

170078

839834

 

Mean

4996

28538

175830

937387

 

0.0405

1

4996

30885

203617

1040806

 

2

4996

32835

191395

928157

 

3

4996

27885

198725

868508

 

Mean

4996

30535

197912

945824

 

0.0110

1

4996

27044

188064

962026

 

2

4996

26861

183813

1001500

 

3

4996

34301

237494

1089092

 

Mean

4996

29402

203124

1017539

 

Control

1

4996

28626

210673

1006506

 

2

4996

25375

206098

950279

 

3

4996

28735

207245

1054860

 

4

4996

25723

215567

1077837

 

5

4996

26201

216862

1048452

 

6

4996

27661

203354

1090944

 

Mean

4996

27054

209967

1038146

 

Evaluation after 72 h

                              

Geometric mean measured test item concentration of            C20/22 ATQ trocken1)

Replicate

Growth rate

Rate-related inhibition

Yield

Inhibition of yield

[mg/L]

No.

[d-1]

[%]

[cells/mL]

[%]

15.4

1

0.190

89.30

3844

99.63

2

0.088

95.06

1505

99.85

3

0.041

97.71

649

99.94

Mean

0.106

94.02

1999

99.81

4.39

1

0.692

61.08

34863

96.63

2

0.743

58.22

41418

95.99

3

0.714

59.83

37604

96.36

Mean

0.717

59.71

37962

96.33

1.39

1

1.486

16.46

425856

58.78

2

1.401

21.21

329365

68.12

3

1.478

16.88

416413

59.69

Mean

1.455

18.18

390545

62.20

0.443

1

1.761

1.01

977633

5.37

2

1.722

3.17

870636

15.73

3

1.745

1.86

934306

9.57

Mean

1.743

2.01

927525

10.22

0.128

1

1.775

0.21

1020340

1.24

2

1.748

1.70

941994

8.82

3

1.708

3.95

834838

19.19

Mean

1.744

1.95

932391

9.75

0.0405

1

1.780

-0.07

1035810

-0.26

2

1.742

2.08

923161

10.65

3

1.719

3.32

863512

16.42

Mean

1.747

1.78

940828

8.94

0.0110

1

1.753

1.41

957030

7.37

2

1.767

0.65

996504

3.55

3

1.795

-0.92

1084096

-4.93

Mean

1.772

0.38

1012543

2.00

Control

1

1.769

1001510

2

1.749

945283

3

1.784

1049864

4

1.791

1072841

5

1.782

1043456

6

1.795

1085948

Mean

1.778

1033150

Section-by-Section and Average Specific Growth Rates of the Control Group
               (0 – 72 h)

Replicate No.

Specific growth rate [d-1]

Mean

(0 - 72 h)

SD

±

CV
[%]

Mean CV [%]

section-by-section                            

0 - 24 h

24 - 48 h

48 - 72 h

Control

1

1.746

1.996

1.564

1.769

0.2169

12.3

13.6

2

1.625

2.095

1.528

1.749

0.3029

17.3

3

1.749

1.976

1.627

1.784

0.1768

9.91

4

1.639

2.126

1.609

1.791

0.2901

16.2

5

1.657

2.113

1.576

1.782

0.2898

16.3

6

1.711

1.995

1.680

1.795

0.1735

9.66

Mean

1.778

 

± SD

0.02

 

CV [%]

0.96

 

Validity criteria fulfilled:
yes
Conclusions:
In this study C20/22 ATQ trocken was found to inhibit the growth of the freshwater green alga Desmodesmus subspicatus after 72 h with the following effect values (nominal test item concentrations): The EC50-values with 95 % confidence intervals for inhibition of specific growth rate (ErC50) and yield (EyC50) after 72 h were 3.48 (3.28 – 3.70) and 1.17 (0.955 – 1.30) mg/L, respectively.
The test effect was observed to be reversible at all tested concentrations following 72 h exposure and 3 – 7 days of growth under test conditions.
All effect levels are given based on geometric mean measured concentrations of C20/22 ATQ trocken.

The measured concentrations of C20/22 ATQ trocken (C20 and C22 fraction) at test start were in the range of 70 - 92% and after 72h in the range of < LOQ – 78 % of the nominal values. The recovery of the C20 fraction was a slightly higher than that of the C22 fraction.
The measured concentrations of the aqueous phases of the adsorption test which was carried out separately confirmed these values.
Adsorption to the test vessels after 72 h of exposure were determined exemplarily at the dosage levels 0.630 to 6.32 mg/L. The absorbed amount of the C20- and the C22-fraction was in the range of 11 to 46 % of the applied amount. This work was done in a second series.
The amount of adsorbed C20/C22 was higher at low nominal concentrations and lower at higher nominal concentrations.
All effect values are based on the geometric mean measured concentrations of the test item C20/22 ATQ trocken (C20 and C22 fraction).
Executive summary:

The toxicity of C20/22 ATQ trocken (batch number DEG4047322)to the unicellular freshwater green alga Desmodesmus subspicatus was determined according to the principles of OECD 201 at Dr.U.Noack-Laboratorienin 31157 Sarstedt, Germany from 2009-04-27 to 2010-06-07 with the definitive exposure phase from 2009-06-23 to 2009-06-26. The aim of the study was to assess the effects on growth rate and yield over a period of 72 h. The test was carried out in natural river water with a DOC of 2.8 mg/L.

The study was conducted under static conditions with an initial cell density of approximately 2 – 5 x 103 cells/mL. Seven concentration levels were tested in a geometrical series with a dilution factor of √10, nominal: 0.020 - 0.063 - 0.20 - 0.63 - 2.00 - 6.32 - 20.0 mg/L, corresponding to geometric mean measured concentrations of 0.0110 - 0.0405 - 0.128 - 0.443 - 1.39 - 4.39 - 15.4 mg/L. Three replicates were tested for each test item concentration and six replicates for the control. Environmental conditions were determined to be within the acceptable limits.

The concentrations of C20/22 ATQ trocken wereanalysed at all concentration levels after 0 and   72 h via LC-MS/MS analysis. The measured initial concentrations of C20/22 ATQ trocken were in good accordance with the nominal concentrations. The recovery rates in the fresh media (0 h) of the fractions C20 and C22 of C20/22 ATQ trocken were determined to be in the range of 82 to 92 % and 70 – 77 % of the nominal values, respectively. In 72h old media, the C20 and C22 fractions had decreased, but were still detectable, except for in the lowest test item concentration. The recoveries in the old media (72 h) of the fractions C20 and C22 of C20/22 ATQ trocken decreased to values in the range of below the limit of quantification ( LOQ) to 78 % and LOQ to 65 % of the nominal values, respectively.

Adsorption to the test vessels after 72 h of exposure were determined exemplarily at the dosage levels 0.0630 to 6.32 mg/L. The absorbed amount of the C20- and the C22-fraction was in the range of 11 to 46 % of the applied amount. This work was done in a second series. The recoveries in the aqueous phase were comparable to the first results of the definitive test. The analytical results are presented in Table 13 to Table 17.

The test item has a low water solubility and sorbs to organic and inorganic materials by different mechanisms. The sorption processes are mostly non-linear, means are concentration dependent. Due to these properties the test item is difficult to test in synthetic water (e.g. sorption to the test organisms and glass walls of the test vessels) and results from such tests depend from the test settings applied. Using natural river water which contains particulate as well as dissolved organic carbon to which the test item can sorb partially reduces the difficulties encountered in tests with synthetic water (e.g. preventing that the test item settles onto surfaces). The sorbed fraction of the test item is difficult to extract from the test system which normally leads to low analytical recoveries. Due to the short exposure period these low recoveries cannot be associated to biodegradation. This means the test substance is present in the test system and therefore available for exposure (dissolved in water and sorbed also called bulk). This so called Bulk Approach is described by ECETOC (2003).

However, all effect values given are based on geometric mean measured concentrations of the test item C20/22 ATQ trocken

EC - Values and 95 % Confidence Intervals of C20/22 ATQ trocken (0-72 h)

                                            (based on the geometric mean measured test item concentrations of C20/22ATQ

                                 trocken)1) [mg/L]

Rate-related Inhibition

ErC10

0.927 (0.798 – 1.07)

ErC20

1.53 (1.38 – 1.68)

ErC50

3.48 (3.28 – 3.70)

Inhibition of Yield

EyC10

0.412 ( 0.0110 – 0.757)

EyC20

0.678 (0.482 – 0.914)

EyC50

1.17 (0.955 – 1.30)

After 72 h algae were transferred from the nominal concentrations of 2.00 – 20.0 mg/L (geometric mean measured 1.39 – 15.4 mg/L) and control to fresh untreated medium and allowed to grow for further 3 – 7 days under test conditions. The test item effect was observed to be reversible at this concentration. Therefore, there is potential for recovery following exposure up to 15.4 mg/L (highest geometric mean measured test concentration)

Description of key information

In this study C20/22 ATQ trocken was found to inhibit the growth of the freshwater green alga Desmodesmus subspicatus after 72 h with the following effect values (nominal test item concentrations): The EC50-values with 95 % confidence intervals for inhibition of specific growth rate (ErC50) and yield (EyC50) after 72 h were 3.48 (3.28 – 3.70) and 1.17 (0.955 – 1.30) mg/L, respectively. 
The test effect was observed to be reversible at all tested concentrations following 72 h exposure and 3 – 7 days of growth under test conditions.
All effect levels are given based on geometric mean measured concentrations of C20/22 ATQ trocken.
The measured concentrations of C20/22 ATQ trocken (C20 and C22 fraction) at test start were in the range of 70 - 92% and after 72h in the range of < LOQ – 78 % of the nominal values. The recovery of the C20 fraction was a slightly higher than that of the C22 fraction.
The measured concentrations of the aqueous phases of the adsorption test which was carried out separately confirmed these values.
Adsorption to the test vessels after 72 h of exposure were determined exemplarily at the dosage levels 0.630 to 6.32 mg/L. The absorbed amount of the C20- and the C22-fraction was in the range of 11 to 46 % of the applied amount. This work was done in a second series.
The amount of adsorbed C20/C22 was higher at low nominal concentrations and lower at higher nominal concentrations.
All effect values are based on the geometric mean measured concentrations of the test item C20/22 ATQ trocken (C20 and C22 fraction).

Key value for chemical safety assessment

EC50 for freshwater algae:
3.48 mg/L
EC10 or NOEC for freshwater algae:
0.78 mg/L

Additional information