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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:
2010-01-15 to 2010-01-27
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: well performed OECD study with GLP

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2010
Report date:
2010

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Deviations:
no
GLP compliance:
yes

Test material

Constituent 1
Chemical structure
Reference substance name:
4-amino-2,5-dimethoxy-N-methylbenzenesulphonamide
EC Number:
256-435-3
EC Name:
4-amino-2,5-dimethoxy-N-methylbenzenesulphonamide
Cas Number:
49701-24-8
Molecular formula:
C9H14N2O4S
IUPAC Name:
4-amino-2,5-dimethoxy-N-methylbenzene-1-sulfonamide
Details on test material:
- Name of test material (as cited in study report): Chinonbasesulfmethylamid
- Molecular formula: C9H14N2O4S
- Molecular weight: 246.29 g/mol
- Physical state: Solid, dark brown wet powder
- Analytical purity: 91.5 % (w/w)
- Expiration date of the lot/batch: 2010-07-29
- Storage condition of test material: Room temperature, protected from moisture and light.

Sampling and analysis

Analytical monitoring:
yes
Details on sampling:
- Concentrations: The test item concentrations were analytically determined from all test concentrations and the control after 0 h (test start) and 72 h (test end).
- Sampling method: Separate samples were prepared at test start. Samples at end of the test were taken directly from the test replicates.
- Sample storage conditions before analysis: All samples were stored at 6 ± 2 °C until start of analysis, if necessary.

Test solutions

Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A saturated solution* of 550 mg/L was prepared with dilution water. The dispersion was shaken with 20 rpm for 48 h at ambient temperature and filtrated with 0.45 µm RC filter.
- Eluate: Dilution water
- Differential loading: The saturated solution and further four dilution levels were tested in a geometrical series with a dilution factor √10: 1.0 - 3.2 - 10 - 32 and 100 % of the saturated solution corresponding to geometric mean measured test item concentrations of 0.304 – 0.991 – 3.45 – 11.7 – 40.2 mg/L.
- Controls: Six replicates (without test item) were tested under the same test conditions as the test replicates.

Test organisms

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):3 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

Study design

Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Post exposure observation period:
No

Test conditions

Hardness:
Not measured
Test temperature:
Mean: 21.5 °C, Min: 21 °C, Max: 22 °C
pH:
Geometric mean measured test item concentration pH-value
[mg/L] Start; 0 h End; 72 h
40.2 7.70 7.80
11.7 7.76 7.81
3.45 7.80 7.90
0.991 7.78 7.90
0.304 7.82 7.91
Control 7.83 8.01
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: 5074 cells/mL
- Control end cells density: Mean 964055 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
- Source/preparation of dilution water: Dilution water, composition acc. to the guideline
- Hardness: 0.24 mmol Ca+Mg/L
- pH-value: 8.1 +/- 0.2
- Culture medium: Nutrient Medium Z acc. to LÜTTGE et al. (1994)


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)

Dilution level of the saturated solution
[%] Rate Related Inhibition[%] Yield Inhibition [%]
100 18 61
1 3 14
0.1 1 4


Reference substance (positive control):
yes
Remarks:
Potassium dichromate

Results and discussion

Effect concentrations
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
40.2 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
growth rate
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: 0.600 (CI 0.545 - 0.653) mg/L
Yield Inhibition: 0.280 (CI 0.266 - 0.299) mg/L
Reported statistics and error estimates:
The NOEC and LOEC were determined by calculation of statistical significance of growth rates and yield.
One Way Analysis of Variance and DUNNETT’s test was carried out for the determination of statistically significant differences compared to control replicates. When running a One Way Analysis of Variance a Normality Test and an Equal Variance Test were done first. P-values for both Normality and Equal Variance Tests were 0.05. The a-value for ANOVA was a=0.05.
Detection of statistically significant differences were considered negligible when inhibition values were ≤ 10 %. These findings were marked “biologically not significant”. Following the recommendations of the UBA (HEGER ET AL. 1998), inhibitions > 10 % are significant. The findings were marked “biologically significant”.


EC-values and statistical EC20-values of the yield inhibition after 72 h were calculated by polynomial regression. Calculation of the confidence intervals were carried from the best fit values, the standard error and the t-distribution with the software GraphPad Prism.

Any other information on results incl. tables

NOEC, LOEC and EC - values and 95 % Confidence Intervals of Chinonbasesulfmethylamid (0-72 h)

                   based on geometric mean measured test item concentrations [mg/L]

                               

Rate-related Inhibition

NOEC

40.2

LOEC

> 40.2

ErC10

> 40.2

ErC20

> 40.2

ErC50

> 40.2

Inhibition of Yield

NOEC

0.304

LOEC

0.991

EyC10

0.304 EC10 0.991

EyC20

0.444 ( 0.304 – 0.731)

EyC50

> 40.2

Cell Densities

 

Geometric mean measured test item concentration

Replicate

Cell density [cells/mL]

[mg/L]

No.

0 h

24 h

48 h

72 h

 

40.2

1

5074

41498

150317

616466

 

2

5074

50334

199455

628069

 

3

5074

42470

181210

602342

 

Mean

5074

44767

176994

615626

 

11.7

1

5074

44512

149234

534794

 

2

5074

46090

174625

549525

 

3

5074

43569

194494

613321

 

Mean

5074

44724

172784

565880

 

    3.45

1

5074

50313

152850

521207

 

2

5074

48345

196544

775858

 

3

5074

44844

179357

624666

 

Mean

5074

47834

176250

640577

 

      0.991

1

5074

33762

184035

601235

 

2

5074

46759

156175

582657

 

3

5074

36681

195790

670689

 

Mean

5074

39067

178667

618194

 

      0.304

1

5074

38005

198246

908128

 

2

5074

40150

177598

811220

 

3

5074

30006

205667

878735

 

Mean

5074

36054

193837

866028

 

Control

1

5074

38001

172748

929649

 

2

5074

32532

136967

846095

 

3

5074

34098

170337

951243

 

4

5074

32081

190361

1000743

 

5

5074

33159

166307

983994

 

6

5074

32269

172920

1072603

 

Mean

5074

33690

168273

964055

 

Evaluation after 72 h

                  Statistically significant differences of growth rates and yield compared to

                   control values are marked (+), not significant differences are marked (-).

               

Geometric mean measured test item concentration

Replicate

Growth rate

Rate-related inhibition

Yield

Inhibition of yield

[mg/L]

No.

[d-1]

[%]

[cells/mL]

[%]

40.2

1

1.60

  8.48

611392

36.3

2

1.61

  8.12

622995

35.0

3

1.59

  8.92

597268

37.7

Mean

(+)*

1.60

  8.51

(+)

610552

36.3

11.7

1

1.55

11.2

529720

44.8

2

1.56

10.7

544451

43.2

3

1.60

  8.57

608247

36.6

Mean

(+)*

1.57

10.1

(+)

560806

41.5

    3.45

1

1.54

11.7

516133

46.2

2

1.68

  4.09

770784

19.6

3

1.60

  8.22

619592

35.4

Mean

(+)*

1.61

  8.00

(+)

635503

33.7

      0.991

1

1.59

  8.95

596161

37.8

2

1.58

  9.55

577583

39.8

3

1.63

  6.87

665615

30.6

Mean

(+)*

1.60

  8.46

(+)

613120

36.1

      0.304

1

1.73

  1.09

903054

  5.83

2

1.69

  3.24

806146

15.9

3

1.72

  1.72

873661

  8.90

Mean

(-)

1.71

  2.02

(-)

860954

10.2

Control

1

1.74

924575

2

1.71

841021

3

1.75

946169

4

1.76

995669

5

1.76

978920

6

1.79

1067529

Mean

1.75

958981

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

2.01

1.51

1.68

1.74

0.254

14.6

9.16

2

1.86

1.44

1.82

1.71

0.233

13.7

3

1.91

1.61

1.72

1.75

0.150

  8.59

4

1.84

1.78

1.66

1.76

0.0938

  5.32

5

1.88

1.61

1.78

1.76

0.134

  7.61

6

1.85

1.68

1.83

1.79

0.0925

  5.18

Mean

1.75

 

± SD

0.03

 

CV [%]

1.52

 

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
In this study Chinonbasesulfmethylamid was found to inhibit the growth of the freshwater green alga Desmodesmus subspicatus after 72 h with the following effect values (geometric mean measured test item concentrations): The NOEC-values for inhibition of specific growth rate (ErC50) and yield (EyC50) after 72 h were 40.2 and 0.304 mg/L, respectively. The EC50-values for both inhibition of specific growth rate (ErC50) and yield (EyC50) after 72 h were > 40.2 mg/L. All effect levels are given based on geometric mean measured concentrations of Chinonbasesulfmethylamid.
Executive summary:

The toxicity of Chinonbasesulfmethylamid(batch number DALA 060326) 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 January 15 to 27, 2010 with the definitive exposure phase being conducted from January 18 to 21, 2010. The aim of the study was to assess the effects on growth rate and yield over a period of 72 h.

The study was conducted under static conditions with an initial cell density of approximately  2 – 5 x 103cells/mL. Based on a preliminary test, a definitive test with the saturated solution and further four dilution levels were tested in a geometrical series with a dilution factor of 2, nominal: 1 - 3.2 - 10 - 32 - 100 % of the saturated solution corresponding to geometric mean measured test item concentrations of 0.304 – 0.991 – 3.45 – 11.7 – 40.2 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 Chinonbasesulfmethylamidwere analysed at all concentration levels after 0 and 72 h via HPLC analysis. The measured concentrations of Chinonbasesulfmethylamidat test end were in the range of 56 – 90 % of the initially measured concentrations. All effect values are given based on geometric mean measured concentrations of the test item.

NOEC, LOEC and EC - values and 95 % Confidence Intervals of Chinonbasesulfmethylamid (0-72 h)

                   based on geometric mean measured test item concentrations [mg/L]

                               

Rate-related Inhibition

NOEC

40.2

LOEC

> 40.2

ErC10

> 40.2

ErC20

> 40.2

ErC50

> 40.2

Inhibition of Yield

NOEC

0.304

LOEC

0.991

EyC10

0.304 EC10 0.991

EyC20

0.444 ( 0.304 – 0.731)

EyC50

> 40.2