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Diss Factsheets

Ecotoxicological information

Toxicity to aquatic plants other than algae

Administrative data

Endpoint:
toxicity to aquatic plants other than algae
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2015-09-29 to 2015-10-08
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:
2015
Report date:
2015

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
OECD Guideline 221 (Lemna sp. Growth Inhibition Test)
Deviations:
no
GLP compliance:
yes

Test material

Constituent 1
Chemical structure
Reference substance name:
3,3'-[(9,10-dihydro-9,10-dioxo-1,4-anthrylene)diimino]bis[N-cyclohexyl-2,4,6-trimethylbenzenesulphonamide]
EC Number:
245-728-1
EC Name:
3,3'-[(9,10-dihydro-9,10-dioxo-1,4-anthrylene)diimino]bis[N-cyclohexyl-2,4,6-trimethylbenzenesulphonamide]
Cas Number:
23552-74-1
Molecular formula:
C44H52N4O6S2
IUPAC Name:
3,3'-[(9,10-dioxo-9,10-dihydroanthracene-1,4-diyl)diimino]bis(N-cyclohexyl-2,4,6-trimethylbenzenesulfonamide)

Sampling and analysis

Analytical monitoring:
no

Test solutions

Vehicle:
no
Details on test solutions:
Preparation of the saturated solution
The saturated solution (100 mg/L test item were weighed out) was prepared with dilution water one day prior to the start of the exposure.

Treatment
The test item was dispersed in the dilution water by stirring with approximately 1100 rpm for 24 hours at room temperature. After completion of stirring, the test item dispersion was filtered with a membrane filter (0.45 µm, RC, MACHEREY-NAGEL) to achieve the saturated solution.

Test concentration
One limit concentration was tested. The limit concentration is based on the results of a preliminary range finding test.

Control
Six replicates (without test item) were tested under the same test conditions as the test vessels.

Test organisms

Test organisms (species):
Lemna gibba
Details on test organisms:
Test organism
Duckweed, Lemna gibba G3, Lemnaceae, Arales, Arecidae, Monocotyledonae
Young, rapidly growing plants without visible lesions or discoloration (chlorosis) were used for the test.

Reason for the selection of the test organism
According to the guideline Lemna gibba is a suitable species because it is a species representative of temperate areas and is commonly used for toxicity tests.

Origin
EUROFINS-GAB GMBH, Eutinger Str. 24, 75223 Niefern-Öschelbronn, Germany.

Date of receipt 2014-08-15

Cultivation at test facility
The species was bred in the test facility. Density was kept low to prevent conglomerates of plants on the surface. At least once per week, plants were transferred to freshly prepared growth medium. Growth media and breeding vessels were autoclaved before use to enable the breeding of axenic cultures.

Breeding vessels
Crystallisation dishes of glass, vol. 900 mL, filled with ca. 500 mL growth medium, covered with glass tops.

Medium
20X-AAP-medium (Algal Assay Procedure medium), pH-value 7.5 ± 0.1

Temperature 24 ± 2 °C

Light regime Continuous fluorescent light, 15 - 60 µE•m-2•s-1

Acclimatization of the test system
The test system was held for 7 days under test conditions to acclimatize. These acclimatize plants (test system) were used in the test.

Study design

Test type:
semi-static
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
7 d

Test conditions

Test temperature:
min: 22.6
max: 23.7
mean value: 23.2
pH:
Nominal loading
of the test item
[mg/L] 0 h(Fresh medium) 2 d (Old medium) 2 d (Fresh medium) 5 d (Old medium) 5 d (Fresh medium) 7 d (Old medium)
100 7.78 8.17 7.80 8.18 7.81 8.21
Control 7.53 8.15 7.69 8.19 7.76 8.20
Nominal and measured concentrations:
Nominal loading of the test item: 100 mg/L
Details on test conditions:
TEST SYSTEM
- Incubation chamber used: no
- Test vessel: Crystallisation dishes
- Type (delete if not applicable): covered with glass tops
- Material, size, headspace, fill volume: glass, 500 mL, with headspace, filled with 200 mL
- Type of cover: glass tops
- Aeration: no
- Agitation: no
- Renewal rate of test solution (frequency/flow rate): Semi-static, with renewal of the test solutions every 2 – 3 days (i.e. exposure to freshly prepared test and control solutions on at least two occasions during the exposure)
- Control end cells density: 192 fronds
- No. of colonies per vessel: 3
- No. of fronds per colony: 4
- No. of vessels per concentration (replicates): 6
- No. of vessels per control (replicates): 6

GROWTH MEDIUM
- Standard medium used: yes

OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: no
- Photoperiod: 24 h cool daylight
- Light intensity and quality: Continuous, fluorescent light, 6500 to 10000 lux (corresponding to 85 to 135 µE*m-2*s-1) on the surface of the test medium. The difference of light intensity at any measured incubation place was less than 15 % from the mean value. Actual: min: 87.2 max: 114 mean value: 102

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of frond number: manual counting
- Determination of biomass: dry weight


RANGE-FINDING STUDY
The results of the preliminary test (static) are presented below:

Table 3: Results of the Range Finding Test after 7 days
(mean values)
Nominal Test Item Concentration [%] Growth Rate Inhibition [%] Yield Inhibition [%]
10.0 -1 -1
100 -1 -3
Negative values = growth stimulation
Reference substance (positive control):
yes

Results and discussion

Effect concentrationsopen allclose all
Duration:
7 d
Dose descriptor:
NOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
7 d
Dose descriptor:
LOEC
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
7 d
Dose descriptor:
EC10
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
7 d
Dose descriptor:
NOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
7 d
Dose descriptor:
LOEC
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
7 d
Dose descriptor:
EC10
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
7 d
Dose descriptor:
NOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: yield frond number
Duration:
7 d
Dose descriptor:
LOEC
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: yield frond number
Duration:
7 d
Dose descriptor:
EC10
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: yield frond number
Duration:
7 d
Dose descriptor:
NOEC
Effect conc.:
100 mg/L
Nominal / measured:
not specified
Conc. based on:
test mat.
Basis for effect:
other: yield dry weight
Duration:
7 d
Dose descriptor:
LOEC
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: yield dry weight
Duration:
7 d
Dose descriptor:
EC10
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: yield dry weight
Details on results:
- Any visual signs of phytotoxicity (abnormalities): No
- Decrease in frond size: No
- Necrosis / chlorosis: No
- Sinking of fronds: No
- Any stimulation of growth found in any treatment: see results
Results with reference substance (positive control):
The acute toxicity of 3,5-Dichlorophenol (FLUKA, batch number SZBD168XV, purity 99.4%, CAS RN 591-35-5) to the monocotyledon Lemna gibba was determined over a period of 7 days from
2015-09-30 to 2015-10-07 according to OECD Guideline 221.

EC50-Values of the Reference Item based on the nominal concentrations [mg/L], (0-7 days)


Growth rate inhibition (number of fronds) Valid Range (average ± 3 x SD)
ErC50 5.25 5.39 ± 2.70 95% confidence interval 5.14 – 5.36
Yield inhibition (number of fronds)
EyC50 4.17 4.46 ± 2.95 95% confidence interval 2.52 – 7.22
Growth rate inhibition (dry weight)
ErdwC50 4.29 5.21 ± 2.24 95% confidence interval 2.61 – 7.24
Yield inhibition (dry weight)
EydwC50 4.08 4.44 ± 2.28 95% confidence interval 2.40 – 7.23

SD = standard deviation
Reported statistics and error estimates:
EC-values and statistical analyses
EC-values were estimated empirically based on the results of the single treatment level (limit test design).

NOEC and LOEC values
NOEC/LOEC was determined by calculation of statistical significance of inhibition of growth rates and yield in comparison to the control using: One Way Analysis of Variance (ANOVA) and DUNNETT’s test as a standard. A normality test and an equal variance test were done first. The SHAPIRO-WILK-Test was used to test for normally distributed populations. The SPEARMAN rank test was used for equal variance test. P-values for both Normality and equal variance test are 0.05. The -value (acceptable probability of incorrectly concluding that there is a difference) is =0.05.

Software
All data will be computer generated and rounded for presentation from the full derived data. Consequently, if calculated manually based on the given data, minor variations may occur from these figures.
Calculations and graphics will be carried out using the following software
- Excel, MICROSOFT CORPORATION
- SigmaPlot, SPSS INC.
- GraphPad Prism, GRAPHPAD SOFTWARE, INC.

Any other information on results incl. tables

Frond Numbers

Nominal loading of thetest item
[mg/L]

Repl.

number

Frond number

0 days*

2 days

5 days

7 days

100

1

12

22

69

200

2

12

25

87

234

3

12

27

89

222

4

12

24

77

211

5

12

23

71

175

6

12

26

85

205

Mean

12

25

80

208

Control

1

12

22

66

179

2

12

21

67

165

3

12

26

82

206

4

12

23

78

189

5

12

25

80

212

6

12

23

75

201

Mean

12

23

75

192

 

* = 3 colonies with 4 fronds each per replicate were inoculated at start of the exposure

 

Evaluation of Frond Numbers after 7 Days

 Statistically significant differences of growth rates and yield compared to control values are marked (+) and not significant differences are marked (-).

                                               

Nominal loading of the test item
[mg/L]

Repl.

No.

Growth rate

[d-1]

Inhibition of Growth rate
[%]

Yield


[fronds]

Inhibition of yield

[%]

Doubling time

[d]

100

1

 

0.402

-1

 

188

-4

1.72

2

 

0.424

-7

 

222

-23

1.63

3

 

0.417

-5

 

210

-17

1.66

1

 

0.410

-3

 

199

-11

1.69

2

 

0.383

3

 

163

9

1.81

3

 

0.405

-2

 

193

-7

1.71

Mean

(-)

0.407

-3

(-)

196

-9

1.71

Control

1

 

0.386

 

 

167

 

1.80

2

 

0.374

 

 

153

 

1.85

3

 

0.406

 

 

194

 

1.71

4

 

0.394

 

 

177

 

1.76

5

 

0.410

 

 

200

 

1.69

6

 

0.403

 

 

189

 

1.72

Mean

 

0.396

 

 

180

 

1.75

Repl. No. = Replicate number

 

 


Evaluation of Specific Growth Rate and Yield Dry Weight after 7 Days

Statistically significant differences of specific growth rates and yield compared to control values are marked (+) and not significant differences are marked (-).

 

Nominal loading of thetest item
[mg/L]

Repl.

No.

Dry weight

[mg]

Growth rate of dry weight

[d-1]

Inhibition of growth rate of dry weight
[%]

Yield of dry weight

[mg]

Inhibition of yield of dry weight
[%]

100

1

36.1

 

0.360

-2

 

33.2

-5

2

34.6

 

0.354

-1

 

31.7

-1

3

40.0

 

0.375

-7

 

37.1

-18

4

35.0

 

0.356

-1

 

32.1

-2

5

31.4

 

0.340

3

 

28.5

10

6

37.1

 

0.364

-3

 

34.2

-9

Mean

35.7

(-)

0.358

-2

(-)

32.8

-4

Control

1

28.1

 

0.324

 

 

25.2

 

2

29.4

 

0.331

 

 

26.5

 

3

35.9

 

0.359

 

 

33.0

 

4

33.1

 

0.348

 

 

30.2

 

5

39.8

 

0.374

 

 

36.9

 

6

40.4

 

0.376

 

 

37.5

 

Mean

34.4

 

0.352

 

 

31.5

 

Initial biomass dry weight was 2.9 mg per replicate

Repl. No. = Replicate number

 

 Colony Number (Plants) on Days 0 and 7

Nominal loading of thetest item
[mg/L]

Replicate

No.

Colony number

 

0 days

7 days

100

1

3

17

2

3

27

3

3

21

4

3

21

5

3

15

6

3

18

Mean

3

20

Control

1

3

18

2

3

14

3

3

20

4

3

14

5

3

18

6

3

17

Mean

3

17

 


 Further Observations on Days 2, 5 and 7

Nominal loading of thetest item
[mg/L]

Observations on day

2

5

7

100

1

1

1

Control

1

1

1

Observations were made compared to the appearance of control colonies (plants) and vessels

1     = No observed effects

 

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
At the saturated solution of the test item with a nominal concentration of 100 mg/L no effects were observed on the growth rate and yield (frond and dry weight) of Lemna gibba.
All effect values are given based on the nominal loading levels of the test item.
Executive summary:

The effects of test item ) on the growth of the monocotyledon species Lemna gibba was determined according to the principles of OECD 221.

A semi-static exposure over 7 days was carried out. Based on a preliminary test a saturated solution with a nominal concentration of 100 mg/L was tested. Six replicates were investigated for the limit concentration and for the control. Frond numbers were assessed on days 0, 2, 5 and 7. Environmental parameters light, temperature and pH-value were within the acceptable limits.The validity criteria of the test guideline were fulfilled.

 

No analytical monitoring of the test item concentration was carried out because a measured concentration below the system quantification limit of the analytical method (0.4 mg/L of the test item) was determined during the non GLP preliminary range finding test in the saturated solution . This was also expected for the definitive study with Lemna gibba.

All effect values are given based on the nominal loading levels of the test item.

 

 

NOEC-, LOEC-, EC-Values and 95 % Confidence Intervals of the test item after 7 Days based on nominal loading of the test item [mg/L]

Frond number

Dry weight

Growth Rate Inhibition [mg/L]

NOEC

100

NOEC

100

LOEC

> 100

LOEC

>100

ErC10

>100

ErdwC10

>100

ErC20

>100

ErdwC20

>100

ErC50

>100

ErdwC50

>100

Yield Inhibition [mg/L]

NOEC

100

NOEC

100

LOEC

>100

LOEC

>100

EyC10

>100

EydwC10

>100

EyC20

>100

EydwC20

>100

EyC50

>100

EydwC50

>100