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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:
2004-01-27 to 2004-01-30
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Version / remarks:
June 1984
Qualifier:
according to guideline
Guideline:
EU Method C.3 (Algal Inhibition test)
Version / remarks:
Updating 29 December 1992
Qualifier:
according to guideline
Guideline:
EPA OPPTS 850.5400 (Algal Toxicity, Tiers I and II) (January 2012)
Version / remarks:
Public Draft, April 1996
GLP compliance:
yes (incl. QA statement)
Specific details on test material used for the study:
SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: batch No. 42638, substance no. 03/0183-1

STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: ambient, under N2
- Stability under test conditions: The stability of the test substance under storage conditions over the exposure period was confirmed by reanalysis

TREATMENT OF TEST MATERIAL PRIOR TO TESTING
- Treatment of test material prior to testing: Before weighting the test substance was melted in water quench at circa 60°C for circa 1.5 hours.

FORM AS APPLIED IN THE TEST (if different from that of starting material): liquid
Analytical monitoring:
yes
Details on sampling:
- Concentrations: 0, 1.56, 6.25, 25 and 100 mg/L, after 0 hours (start of exposure) and 72 h (end of exposure)
- Sampling method: Twenty milliliters (20 mL) samples were applied onto SPE-columns (solid phase extraction column, Chromabond easy). The columns were then eluted with five 5 mL acetonitrile each. Aliquots of the solutions were used for GC - analysis.
- Sample storage conditions before analysis: None (analyzed immediately after sample delivery)
Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A stock solution of 125.4 mg/L was freshly prepared. Before weighting the test substance was melted in water quench at circa 60°C for circa 1.5 hours. Circa 800 mL deion. water were put into 1000 mL flask .The water was stirred and heat to circa 60°C. The test substance (125 mg/L) was weighed on plastic pad and put into the flask. The flask was filled to 1000 mL with deion. water. The stock solution was stirred circa 0.5 hours.
- Evidence of undissolved material (e.g. precipitate, surface film, etc.): The stock solution was clear.
Test organisms (species):
Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
Details on test organisms:
TEST ORGANISM
- Common name: Green algae
- Strain: CHODAT SAG 86.81
- Source (laboratory, culture collection): The test strain of Desmodesmus subspicatus CHODAT SAG 86.81 is obtained at regular intervals from SAG (Sammlung von Algenkulturen/Collection of algal cultures in Göttingen) and is kept in liquid culture in the Laboratory of Experimental Toxicology and Ecology.
- Age of inoculum (at test initiation): 3 days
- Method of cultivation:
seed-culture: A seed culture was incubated for 4 days at 23 ± 2°C final cell density: 78 x 10^4 ceIls/mL
pre-culture: Seed-culture was taken to inoculate a pre-culture (initial cell density: 1 x 10^4 cells/mL). The pre-culture was incubated for 3 days at 23 ± 2°C. Final celI density: 36 x 10^4 cells/mL.

ACCLIMATION
- Culturing media and conditions (same as test or not): same as test
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Test temperature:
23 ± 2°C
pH:
8 - 8.2
After 0 h and 72 h in an additional uninoculated replicate and after 72 h in the inoculated replicate No. 1 of each concentration.
Nominal and measured concentrations:
nominal: 0 (control), 0.391, 0.781, 1.56, 3.13, 6.25, 12.5, 25, 50, 100 mg/L
measured: The concentration control analyses were performed with test solutions of the following nominal concentrations of the test substance (mg/L):
0 (control) = < LOQ
1.56 = 1.46 (mean of measured concentration d0)
6.25 = 5.60 (mean of measured concentration d0)
25 = 22.60 (mean of measured Ohconcentration d0)
100 = 102.59 (mean of measured concentration d0)

The analytical recovery rates in the range of the EC-values were > 80%. Therefore no transformation of the nominal EC-values into the values of the concentration control analysis occurs.
Details on test conditions:
TEST SYSTEM
- Test vessel: Erlenmeyer flasks (nominal volume 250 mL)
- Type: closed, plugged with gas permeable siliconsponge caps
- Material, size, headspace, fill volume: Size: 250 mL, fill volume: 100 mL
- Initial cells density: 1 x 10^4 cells/mL
- Control end cells density: The cell multiplication factor in the untreated control was after 72 hours: 28-fold (counted).
- No. of vessels per concentration (replicates): 3 replicates
- No. of vessels per control (replicates): 3 replicates

GROWTH MEDIUM
- Standard medium used: yes (OECD medium)

OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: no
- Photoperiod: permanent illumination
- Light intensity and quality: artificial light, type universal white (OSRAM L 25), about 60 - 120 µE/(m^2*s) at a wave length of 400 - 700 nm

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: After 72 h in a counting chamber (Neubauer improved)
- Chlorophyll measurement: in vivo chlorophyll-a-fluorescence (pulsed excitation with light flashes having a wavelength of 435 nm), after 0, 24, 48 and 72 h

TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Range finding study: yes (non-GLP)

Reference substance (positive control):
yes
Remarks:
Potassium dichromate
Duration:
72 h
Dose descriptor:
EC10
Effect conc.:
24.8 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
biomass
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
72 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
biomass
Duration:
72 h
Dose descriptor:
EC10
Effect conc.:
53.9 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.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
50 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
biomass
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
50 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
LOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
biomass
Duration:
72 h
Dose descriptor:
LOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Details on results:
- Observation of abnormalities (for algal test): no information available
Results with reference substance (positive control):
- Results with reference substance valid? Yes
- EC50 (72h): 0.42 mg/L

Table 1: Analytical recovery rates (%)

time (h)

inoculation

Test solution

minimum

maximum

0

yes

89.6

102.6

72

yes

72.3

120.9

Table 2: pH values at the start (t = 0 h) and at the end (t = 72 h) of the test (pa = parallel)

Concentration (mg/L)

uninoculated (pa.5)

0 h

uninoculated (pa.6)

72 h

inoculated (pa.1)

72 h

0 (control)

8.0

8.0

8.1

100

8.0

8.1

8.1

50

8.0

8.1

8.1

25

8.0

8.1

8.2

12.5

8.0

8.1

8.1

6.25

8.0

8.1

8.1

3.13

8.0

8.1

8.1

1.56

8.1

8.1

8.1*

0.781

8.1

8.1

8.1

0.391

8.1

8.1

8.1

Remark: * inoculated parallel 4

Table 3 – Test Data: Measured fluorescence (relative units) after 0 h, 24 h, 48 h and 72 h

time (h)

flask No.

concentration (mg/L)

0 (control)

100

50

25

12.5

6.25

3.13

1.56

0.781

0.391

0

1

38

39

38

38

35

38

38

37

38

37

2

38

39

38

39

35

37

39

37

37

37

3

37

38

40

39

35

37

38

37

37

38

no

0

0

0

0

0

0

0

0

0

0

24

1

140

85

120

140

120

130

140

120

140

150

2

130

86

120

140

120

120

130

130

140

140

3

130

80

110

130

130

130

130

130

130

150

no

0

0

0

0

0

0

0

0

0

0

48

1

600

140

500

540

530

670

570

570

620

530

2

550

140

430

430

580

510

530

540

550

680

3

530

140

440

500

510

520

490

540

540

550

no

0

0

0

0

0

0

0

0

0

0

72

1

1240

230

1120

1040

1260

1940

1280

1620

1230

980

2

1040

200

860

990

1980

920

1160

940

1090

1680

3

970

220

820

930

1030

960

890

990

980

1000

no

0

0

0

0

0

0

0

0

0

0

Table 4: Test Results: CeII density after 0 h, 24 h, 48 h and 72 h

The measured fluorescence was corrected by the fluorescence of the test substance and converted into celI densities (cells x 1 0000/mL) by the following correlation:

ceII density (cells x 10000/mL) = fluorescence (relative units) / slope (m); m = 22.779

The linear correlation was obtained from a calibration curve (cell density versus fluorescence).

time (h)

flask No.

concentration (mg/L)

0 (control)

100

50

25

12.5

6.25

3.13

1.56

0.781

0.391

0

1

1.7

1.7

1.7

1.7

1.5

1.7

1.7

1.6

1.7

1.6

2

1.7

1.7

1.7

1.7

1.5

1.6

1.7

1.6

1.6

1.6

3

1.6

1.7

1.8

1.7

1.5

1.6

1.7

1.6

1.6

1.7

mean

1.7

1.7

1.7

1.7

1.5

1.6

1.7

1.6

1.6

1.6

24

1

6.1

3.7

5.3

6.1

5.3

5.7

6.1

5.3

6.1

6.6

2

5.7

3.8

5.3

6.1

5.3

5.3

5.7

5.7

6.1

6.1

3

5.7

3.5

4.8

5.7

5.7

5.7

5.7

5.7

5.7

6.6

mean

5.9

3.7

5.1

6.0

5.4

5.6

5.9

5.6

6.0

6.4

48

1

26.3

6.1

22.0

23.7

23.3

29.4

25.0

25.0

27.2

23.3

2

24.1

6.1

18.9

18.9

25.5

22.4

23.3

23.7

24.1

29.9

3

23.3

6.1

19.3

22.0

22.4

22.8

21.5

23.7

23.7

24.1

mean

24.6

6.1

20.0

21.5

23.7

24.9

23.3

24.1

25.0

25.8

72

1

54.4

10.1

49.2

45.7

55.3

85.2

56.2

71.1

54.0

43.0

2

45.7

8.8

37.8

43.5

86.9

40.4

50.9

41.3

47.9

73.8

3

42.6

9.7

36.0

40.8

45.2

42.1

39.1

43.5

43.0

43.9

mean

47.6

9.5

41.0

43.3

62.5

55.9

48.7

51.9

48.3

53.6

Table 5 - Test Results: Calculation of biomass and inhibition of biomass after 72 h

 

parameter

flask No.

concentration (mg/L)

0 (control)

100

50

25

12.5

6.25

3.13

1.56

0.781

0.391

biomass [rel]

1

56

11

48

49

52

74

55

62

56

47

2

49

10

39

42

70

44

50

46

50

69

3

46

10

38

44

47

46

43

47

47

49

mean

50

10

41

45

57

54

49

52

51

55

Inhibition [%]

 

0.0

79.4

17.3

10.3

-12.9

-8.4

1.6

-3.1

-2.0

-9.6

 

 

Table 6 - Test Results: Calculation of growth rate and inhibition of growth rate after 72 h

 

parameter

flask No.

concentration (mg/L)

0 (control)

100

50

25

12.5

6.25

3.13

1.56

0.781

0.391

growth rate [rel]

1

0.0484

0.0246

0.0470

0.0460

0.0498

0.0546

0.0488

0.0525

0.0483

0.0455

2

0.0460

0.0227

0.0433

0.0449

0.0560

0.0446

0.0471

0.0449

0.0470

0.0530

3

0.0454

0.0244

0.0420

0.0441

0.0470

0.0452

0.0438

0.0456

0.0455

0.0454

mean

0.0466

0.0239

0.0441

0.0450

0.0509

0.0482

0.0466

0.0477

0.0469

0.0480

Inhibition [%]

 

0.0

48.7

5.3

3.4

-9.3

-3.4

0.0

-2.4

-0.8

-3.0

Validity criteria fulfilled:
yes
Conclusions:
The toxicity of Nonane-1,9-diol on Desmodesmus subspicatus was determined in a reliable GLP study according to OECD 201. The algae were exposed to 0.391, 0.781, 1.56, 3.13, 6.25, 12.5, 25, 50 and 100 mg/L of Nonane-1,9-diol for 72 hours. The concentrations were analytically verified via GC-FIS and recovery rates were > 80%. Therefore, results were given based on nominal concentrations. Inhibition of growth rate (ErC50) and biomass (EyC50) of the algae were observed at > 100 mg/L and 72 mg/L, respectively. The NOEC and LOEC of both, inhibition of growth rate and biomass, were 50 mg/L and 100 mg/L, respectively.

Description of key information

Effect on growth rate:

ErC10 (72 h) = 53.9 mg/L

ErC50 (72 h) > 100 mg/L

NOEC (72 h) = 50 mg/L

LOEC (72 h) = 100 mg/L

Effect on biomass:

EyC10 (72 h) = 24.8 mg/L

EyC50 (72 h) = 72.0 mg/L

NOEC (72 h) = 50 mg/L

LOEC (72 h) = 100 mg/L

Key value for chemical safety assessment

EC50 for freshwater algae:
100 mg/L
EC10 or NOEC for freshwater algae:
53.9 mg/L

Additional information

The toxicity of Nonane-1,9-diol on Desmodesmus subspicatus was determined in a reliable GLP study according to OECD 201. The algae were exposed to 0.391, 0.781, 1.56, 3.13, 6.25, 12.5, 25, 50 and 100 mg/L of Nonane-1,9-diol for 72 hours. The concentrations were analytically verified via GC-FIS and recovery rates were > 80%. Therefore, results were given based on nominal concentrations. Inhibition of growth rate (ErC50) and biomass (EyC50) of the algae were observed at > 100 mg/L and 72 mg/L, respectively. The NOEC and LOEC of both, inhibition of growth rate and biomass, were 50 mg/L and 100 mg/L, respectively.