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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:
05 Dec. 2016 to 06 Jan. 2017
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
Version / remarks:
OECD Guideline for the Testing of Chemicals No. 201, adopted 23. Mar. 2006, Annex 5 corrected: 28 July 2011 “Freshwater Alga and Cyanobacteria, Growth Inhibition Test”
Deviations:
yes
Remarks:
See "Any other information" for details
Qualifier:
according to guideline
Guideline:
EU Method C.3 (Algal Inhibition test)
Version / remarks:
Regulation EU No. 2016/266 amending Regulation EC No. 440/2008, Annex IV, Method C.3: “FRESHWATER ALGAE AND CYANOBACTERIA, GROWTH INHIBITION TEST,” adopted 07. December 2015
Deviations:
yes
Remarks:
See "Any other information" for details
Principles of method if other than guideline:
OECD guidance document no. 23, GUIDANCE DOCUMENT ON AQUATIC TOXICITY TESTING OF DIFFICULT SUBSTANCES AND MIXTURES, adopted 14. Dec. 2000
GLP compliance:
yes (incl. QA statement)
Specific details on test material used for the study:
No further details specified in the study report.
Analytical monitoring:
yes
Details on sampling:
Not specified
Vehicle:
no
Details on test solutions:
For the 1st experiment the water-accommodated fractions (WAF) were prepared individually for the test. This was done mixing the nominal loads with the corresponding amount of algal medium (demineralised water enriched with minerals but without algae) and shaking vigorously for 23 hours. The resulting solution was filtrated through 0.45 μm PTFE filters.
For the 2nd experiment the water-accommodated fraction (WAF) was prepared as stock solution for the test. This was done mixing the nominal load of 100 mg/L with the corresponding amount of algal medium (demineralised water enriched with minerals but without algae) and shaking vigorously for 24 hours. The resulting solution was filtrated through 0.45 μm PTFE filters. The lower concentrations were prepared by dilution of this stock solution.
Test organisms (species):
Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
Details on test organisms:
Unicellular freshwater green alga.
Genus: Desmodesmus
Species: subspicatus
SAG Strain Number: 86.81
Taxonomic position: Chlorophyta - Chlorophyceae

Origin and Culture
The culture of Desmodesmus subspicatus was obtained in January 2016 by MBM Sciencebridge GmbH (Institut für Pflanzenphysiologie of Universität Göttingen). The algae are kept as stock culture on solid agar at 2 - 8 °C. From the stock culture, a permanent culture was prepared. From an aliquot of the permanent culture, the pre-culture was prepared.
Test type:
static
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
72 h
Post exposure observation period:
No post exposure observation period specified
Hardness:
Not specified
Test temperature:
22.5 – 22.6 °C
pH:
7.5 - 9.3
Dissolved oxygen:
Not specified
Salinity:
Not applicable.
Conductivity:
Not specified
Nominal and measured concentrations:
The study was performed using 5 concentrations ranging from 1.0 to 100 mg/L (nominal).
Details on test conditions:
CONDUCT OF THE STUDY
1st Experiment
Pre-Culture
Four days prior to the start of each test, an aliquot of the permanent culture was mixed with nutrient medium and incubated under continuous lighting for 96 hours. The resulting culture grew exponentially.
Before usage, the pre-culture was checked for the absence of cell aggregates and the cell number of culture was determined.

Performance of the Study
For each treatment, 200 mL of the respective test item solution was mixed with the necessary amount of algal pre-culture (1.34 mL) to achieve a cell concentration of 4.9 *103 cells/mL. In this mixture, the pH-value was measured. Additional samples were obtained for analytical determination.
For the blank control, 350 mL nutrient medium was used in lieu of test item solution and mixed with the necessary amount of algal pre-culture (2.35 mL). In this mixture, the pH value was measured.
The real cell concentration at the beginning of the test was measured with an electronic particle counter in the blank control solution. This measured value was used as the starting cell concentration for all replicates.
The test vessels were filled with 45 mL of the respective test solution and incubated open (covered with perforated plastic foil) for 72 hours, and shaken on an orbital shaker. Before the start of incubation, and every 24 hours, the cell number was determined with an electronic particle counter. After the test, the pH value in treatments and blank control was measured again.
At the end of the test, the treatments were examined microscopically in order to assess the appearance of the algae and detect abnormalities (i.e., caused by the exposure to the test item).
The content of DOC in the test vessels was measured at the start and at the end of the test.

Experimental Conditions
Date: 06. – 09. December 2016
Treatments tested: 1.0 / 3.2 / 10 / 32 / 100 mg/L
Number of replicates: 6 replicates for the blank control
3 replicates for each treatment
Vessels: glass flasks total volume 65 mL
Duration: 72 hours
Temperature: 22.5 – 22.6 °C
Lighting: 4500 Lux
Blank control: deionised water with nutrient medium and algae
Treatments: test solution and algae

2nd Experiment
Pre-Culture
Four days prior to the start of each test, an aliquot of the permanent culture was brought into nutrient medium and incubated under continuous lighting for 96 hours. The resulting culture grew exponentially.
Before usage, the pre-culture was checked for the absence of cell aggregates and the cell number of culture was determined.

Performance of the Study
For each treatment, 200 mL of the respective test item solution was mixed with the necessary amount of algal pre-culture (1.82 mL) to achieve a cell concentration of 5.8 *103 cells/mL. In this mixture, the pH-value was measured.
Additional samples were obtained for analytical determination.
For the blank control, 350 mL nutrient medium was used instead of test item solution and mixed with the necessary amount of algal pre-culture (3.19 mL). In this mixture, the pH value was measured.
The real cell concentration at the beginning of the test was measured with an electronic particle counter in the blank control solution. This measured value was used as start cell concentration for all replicates.
The test vessels were filled with 45 mL of the respective test solution and incubated open (covered with perforated plastic foil) for 72 hours, while being kept in constant motion on an orbital shaker. Before the start of incubation and every 24 hours, the cell number was determined with an electronic particle counter. After the test, the pH value in treatments and blank control was measured again.
At the end of the test, the treatments were examined microscopically in order to assess the appearance of the algae and detect abnormalities (e.g. caused by the exposure to the test item).
The content of DOC in the test vessels was measured at the start and at the end of the test.

Experimental Conditions
Date: 03. - 06. January 2017
Treatments tested: 1.0 / 3.2 / 10 / 32 / 100 mg/L
Number of replicates: 6 replicates for the blank control
3 replicates for each treatment
Vessels: glass flasks total volume 65 mL
Duration: 72 hours
Temperature: 22.2 - 22.4°C
Lighting: 4500 Lux
Blank control: deionised water with nutrient medium and algae
Treatments: test solution and algae
Reference substance (positive control):
yes
Remarks:
Potassium dichromate K2Cr2O7 (CAS No. 7778-50-9)
Key result
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
>= 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: Growth rate & Yield
Key result
Duration:
72 h
Dose descriptor:
LOEC
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: Growth rate & Yield
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: Growth rate & Yield
Details on results:
In the 1st experiment the treatments were prepared by individual preparation of the water accommodated fraction (WAF). Inhibition in all tested concentrations was within the same range. Therefore, the study was repeated.
In the 2nd experiment the treatments were prepared by dilution of a 100 mg/L (nominal) WAF. This was in accordance with OECD Guidance Document No. 23 where it is stated that serial dilution of a stock WAF may be the only applicable method for chemicals being toxic at concentrations of 1 mg/L or lower.
The results of this experiment were used for evaluation of the biological results.
Slight inhibition of algal growth was only observed in the highest concentration of 100 mg/L nominal concentration. However, based on statistical evaluation, inhibition at the nominal concentration 100 mg/L must be stated as not significant and the NOEC must be stated as ≥ 100 mg/L for both endpoints. Whereas for the endpoint yield, the EC 10 must be stated as being within the range of 32 - 100 mg/L.
Results with reference substance (positive control):
The 72h-EC50s of potassium dichromate were determined in a separate reference test. For the estimation of the 72h-EC50s of the positive control, the fits showed sufficient statistical correspondence of the data with the dose-response-equation. The values were within the range of the laboratory.
Reported statistics and error estimates:
Calculation of results was performed with the help of validated software (Microsoft Excel ®). The estimation of the biological data was accomplished using the software ToxRat® Professional, version 3.2.1. Biological results are stated using two significant digits.

1st experiment

Cell Numbers

The mean and standard deviations of cell numbers for the blank control, and treatment groups are presented in the table below:

Cell Number/mL

Nominal Concentration in mg/L

Parameter

Cell Number/mL

0 h

24 h

48 h

72 h

Blank control

Mean

4920

18473

73120

235837

Blank control

SD

0

942

4407

24420

1.0

Mean

4920

19407

131820

165680

1.0

SD

0

1432

6748

15997

3.2

Mean

4920

17680

126027

158647

3.2

SD

0

1134

13694

17348

10

Mean

4920

18873

178233

452887

10

SD

0

896

11784

111566

32

Mean

4920

18893

127213

163127

32

SD

0

367

6301

36931

100

Mean

4920

23033

142487

126360

100

SD

0

7273

10092

2955

SD = Standard Deviation

 

Light Intensity

The table below details light intensity measured during the testing phase:

Light Intensity

 

0 h

24 h

48 h

72 h

Light intensity [lux]

4500

4500

4500

4500

 

pH values

In the following table, pH values measured at the start and the end of the test are stated:

pH values

Nominal Concentration in mg/L

0 h

72 h

Blank control

7.5

7.6

1.0

7.5

7.6

3.2

7.5

7.6

10

7.5

8.4

32

7.5

7.6

100

7.5

7.6

 

Microscopical Observations

In the following table, the appearance of the algae at the end of the test is stated:

Microscopical Observations

Nominal Concentration in mg/L

Normal and Healthy Appearance of the Algae

Blank control

Yes

1.0

Yes

3.2

Yes

10

Yes

32

Yes

100

Yes

 

Analytical Determination

At the start and at the end of each experiment, the content of dissolved organic carbon (DOC) in the test solutions was determined. The content of DOC in all treatments was in the same range as the blank control.

The details of which are given in the following tables:

Measured Concentration IC and TC

Nominal Concentration Test Item

Measured TC

t = 0 h

Measured TC

t = 72 h

Measured IC

t = 0 h

Measured IC

t = 72 h

mg/L

mg/L

mg/L

mg/L

mg/L

Blank control

7.59

6.51

7.45

6.22

1.0

7.03

6.71

6.82

6.34

3.2

7.14

7.03

7.04

6.64

10

10.44

8.74

7.05

6.70

32

7.88

7.21

7.12

6.18

100

8.00

9.01

7.30

5.94

LOQ (Limit of quantification) TC = 3.17 mg/L

LOQ (Limit of quantification) IC = 1.82 mg/L

 

Measured Concentrations DOC

Nominal Concentration Test Item

Measured DOC (TC-IC) t = 0 h

Measured DOC (TC-IC) t = 72 h

Measured DOC minus blank control

t = 0 h

Measured DOC minus blank control

t = 72 h

mg/L

mg/L

mg/L

mg/L

mg/L

Blank control

0.13

0.30

--

--

1.0

0.21

0.37

0.08

0.07

3.2

0.10

0.39

-0.03

0.09

10

3.38

2.04

3.25

1.74

32

0.76

1.03

0.63

0.73

100

0.70

3.07

0.57

2.77

 

Growth Rate, Yield

From the cell numbers, the Growth Rate μ and the Yield were calculated. The mean, and standard deviations, observed at the end of the test are given in the following table:

Growth Rate μ, Yield

Nominal Concentration in mg/L

Parameter

Growth Rate (0-72h) [day-1]

Yield (0-72h)

[Cell Concentration/mL]

Blank control

Mean

1.29

230917

SD

0.03

24420

1.0

Mean

1.17

160760

SD

0.03

15997

3.2

Mean

1.16

153727

SD

0.04

17348

10

Mean

1.50

447967

SD

0.08

111566

32

Mean

1.16

158207

SD

0.08

36931

100

Mean

1.08

121440

SD

0.01

2955

SD = Standard Deviation

 

Inhibition

The following mean inhibition values were calculated for the Growth Rate μ and the Yield.

Inhibition Values

Nominal Concentration in mg/L

% Inhibition

Growth Rate (0-72h)

Yield (0-72h)

Blank control

0

0

1.0

9.10

30.38

3.2

10.25

33.43

10

-16.50

-93.99

32

9.90

31.49

100

16.03

47.41

Negative inhibition values indicate a stimulation of algal growth compared to the blank control.

 

 

2nd experiment

Cell Numbers

The mean, and standard deviations, of cell numbers for the blank control, and treatment groups are presented in the table below:

Cell Number/mL

Nominal Concentration in mg/L

Parameter

Cell Number/mL

0 h

24 h

48 h

72 h

Blank control

Mean

5820

27757

131383

342993

Blank control

SD

0

2899

18327

96119

1.0

Mean

5820

24100

157127

754480

1.0

SD

0

2279

11867

112007

3.2

Mean

5820

23547

158660

699907

3.2

SD

0

873

11981

174012

10

Mean

5820

27093

172427

900187

10

SD

0

662

6839

69080

32

Mean

5820

24000

156080

642447

32

SD

0

616

4676

45446

100

Mean

5820

25753

130293

272220

100

SD

0

2454

13499

32184

SD = Standard Deviation

 

Light Intensity

The table below details light intensity measured during the testing phase:

Light Intensity

 

0 h

24 h

48 h

72 h

Light intensity [lux]

4500

4500

4500

4500

 

pH values

In the following table, the pH values measured at the start and the end of the test are stated:

pH values

Nominal Concentration in mg/L

0 h

72 h

Blank control

8.6

8.2

1.0

8.6

9.2

3.2

8.6

8.9

10

8.6

9.3

32

8.6

9.1

100

8.7

8.2

 

Microscopic Observations

In the following table, the appearance of the algae at the end of the test is stated:

Microscopical Observations

Nominal Concentration in mg/L

Normal and Healthy Appearance of the Algae

Blank control

Yes

1.0

Yes

3.2

Yes

10

Yes

32

Yes

100

Yes

 

Analytical Determination

At the start and at the end of each experiment, the content of dissolved organic carbon (DOC) in the test solutions was determined. The content of DOC in all treatments was in the same range as the blank control.

Therefore, determination of the biological results was based on the nominal concentrations.

The details of which are given in the following tables:

Measured Concentration IC and TC

Nominal Concentration Test Item

Measured TC

t = 0 h

Measured TC

t = 72 h

Measured IC

t = 0 h

Measured IC

t = 72 h

mg/L

mg/L

mg/L

mg/L

mg/L

Blank control

0.00

14.41

13.42

14.35

1.0

14.01

0.00

14.00

0.49

3.2

13.82

11.25

14.16

11.24

10

14.04

11.12

14.05

10.75

32

14.02

11.27

14.08

11.60

100

15.99

15.16

13.78

14.91

LOQ (Limit of quantification) TC = 2.81 mg/L

LOQ (Limit of quantification) IC = 1.08 mg/L

 

Measured Concentrations DOC

Nominal Concentration Test Item

Measured DOC (TC-IC) t = 0 h

Measured DOC (TC-IC) t = 72 h

Measured DOC minus blank control

t = 0 h

Measured DOC minus blank control

t = 72 h

mg/L

mg/L

mg/L

mg/L

mg/L

Blank control

0.00

0.06

--

--

1.0

0.01

0.00

0.01

-0.06

3.2

0.00

0.02

0.00

-0.04

10

0.00

0.37

0.00

0.32

32

0.00

0.00

0.00

-0.06

100

2.22

0.25

2.22

0.20

 

Growth Rate, Yield

From the cell numbers, the Growth Rate μ and the Yield were calculated. The mean and standard deviations, observed at the end of the test were measured, and are given in the following table:

Growth Rate μ, Yield

Nominal Concentration in mg/L

Parameter

Growth Rate (0-72h) [day-1]

Yield (0-72h)

[Cell Concentration/mL]

Blank control

Mean

1.35

337173

SD

0.09

96119

1.0

Mean

1.62

748660

SD

0.05

112007

3.2

Mean

1.59

694087

SD

0.09

174012

10

Mean

1.68

894367

SD

0.03

69080

32

Mean

1.57

636627

SD

0.02

45446

100

Mean

1.28

266400

SD

0.04

32184

SD = Standard Deviation

 

Inhibition

The following mean inhibition values were calculated for the Growth Rate μ and the Yield.

Inhibition Values

Nominal Concentration in mg/L

% Inhibition

Growth Rate (0-72h)

Yield (0-72h)

Blank control

0

0

1.0

-20.02

-122.04

3.2

-17.80

-105.85

10

-24.50

-165.25

32

-16.18

-88.81

100

5.11

20.99

Negative inhibition values indicate a stimulation of algal growth compared to the blank control.

 

 

Biological Results of the Reference Study (16102401R301)

The results of the last study with the positive control K2Cr2O7 are presented in the following table. The study was performed under GLP conditions in October 2016.

Parameter

Value

95% confidence interval

72h ErC50

0.80 mg/L

0.78 – 0.83 mg/L

72h EyC50

0.54 mg/L

0.52 – 0.56 mg/L

 

Validity criteria fulfilled:
yes
Conclusions:
The following results for the test item Hatcol 3178 were determined:
NOEC (Growth Rate) ≥ 100 mg/L
NOEC (Yield) ≥ 100 mg/L
LOEC (Growth Rate) > 100 mg/L
LOEC (Yield) > 100 mg/L
EC50 (Growth rate) > 100 mg/L
EC50 (Yield) > 100 mg/L
Executive summary:

Two valid experiments were performed.

The study was performed using 5 concentrations ranging from 1.0 to 100 mg/L (nominal).

Incubation time (test system Desmodesmus subspicatus) was 72 hours. The cell concentration of each replicate was determined by measuring the cell numbers every 24 hours with an electronic particle counter. Growth rate μ and the yield were determined from the cell number at the respective observation times.

 

In the 1st experiment the treatments were prepared by individual preparation of the water accommodated fraction (WAF). Inhibition in all tested concentrations was within the same range except the treatment containing 10 mg/L nominal concentration. Therefore, the study was repeated.

 

In the 2nd experiment the treatments were prepared by dilution of a 100 mg/L (nominal) WAF. This was in accordance with OECD Guidance Document No. 23 where it is stated that serial dilution of a stock WAF may be the only applicable method for chemicals being toxic at concentrations of 1 mg/L or lower.

The results of this experiment were used for evaluation of the biological results.

Slight inhibition of algal growth was only observed in the highest concentration of 100 mg/L nominal concentration. However, based on statistical evaluation, inhibition at the nominal concentration 100 mg/L must be stated as not significant and the NOEC must be stated as ≥ 100 mg/L for both endpoints. Whereas for the endpoint yield, the EC 10 must be stated as being within the range 32 - 100 mg/L.

 

At the start and at the end of each experiment, the content of dissolved organic carbon (DOC) in the test solutions was determined.

In the 1st experiment the content of DOC in all treatments was low and partly in the same range as the blank control. No dose-response relationship between increasing nominal load and rising DOC was observable.

In the 2nd experiment the content of DOC in all treatments was in the same range as the blank control.

 

However, slight inhibition of algal growth indicates the presence of a very low concentration of dissolved test item in the test solution.

Therefore, determination of the biological results was based on the nominal concentrations.

 

The 72h-EC50s of potassium dichromate (K2Cr2O7, CAS No. 7778-50-9) were determined in a separate reference test. The values lay within the range of the laboratory (growth rate 0.73 - 1.10 mg/L, yield 0.21 – 0.66 mg/L).

 

The following results for the test item Hatcol 3178 were determined:

Endpoint

NOEC

LOEC

EC10

EC50

Growth Rate

≥ 100 mg/L

> 100 mg/L

> 100 mg/L

> 100 mg/L

Yield

≥ 100 mg/L

> 100 mg/L

Within 32 – 100 mg/L

> 100 mg/L

 

Note: According to the guideline, NOEC is determined by comparing of the respective treatment with the blank control. Statistically insignificant variation is considered as “no observed effect”, although the EC10 which is read from the graph toxicity vs. concentration may lie lower.

Description of key information

The following results for the test item Hatcol 3178 were determined:

Endpoint

NOEC

LOEC

EC10

EC50

Growth Rate

≥ 100 mg/L

> 100 mg/L

> 100 mg/L

> 100 mg/L

Yield

≥ 100 mg/L

> 100 mg/L

Within 32 – 100 mg/L

> 100 mg/L

Key value for chemical safety assessment

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

Additional information

Two valid experiments were performed.

The study was performed using 5 concentrations ranging from 1.0 to 100 mg/L (nominal).

Incubation time (test system Desmodesmus subspicatus) was 72 hours.

 

In the 1st experiment the treatments were prepared by individual preparation of the water accommodated fraction (WAF). Inhibition in all tested concentrations was within the same range except the treatment containing 10 mg/L nominal concentration. Therefore, the study was repeated.

 

In the 2nd experiment the treatments were prepared by dilution of a 100 mg/L (nominal) WAF. This was in accordance with OECD Guidance Document No. 23 where it is stated that serial dilution of a stock WAF may be the only applicable method for chemicals being toxic at concentrations of 1 mg/L or lower.

The results of this experiment were used for evaluation of the biological results.

Slight inhibition of algal growth was only observed in the highest concentration of 100 mg/L nominal concentration. However, based on statistical evaluation, inhibition at the nominal concentration 100 mg/L must be stated as not significant and the NOEC must be stated as ≥ 100 mg/L for both endpoints. Whereas for the endpoint yield, the EC 10 must be stated as being within the range 32 - 100 mg/L.

 

The following results for the test item Hatcol 3178 were determined:

Endpoint

NOEC

LOEC

EC10

EC50

Growth Rate

≥ 100 mg/L

> 100 mg/L

> 100 mg/L

> 100 mg/L

Yield

≥ 100 mg/L

> 100 mg/L

Within 32 – 100 mg/L

> 100 mg/L