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Ecotoxicological information

Short-term toxicity to aquatic invertebrates

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Reference
Endpoint:
short-term toxicity to aquatic invertebrates
Type of information:
experimental study
Adequacy of study:
key study
Study period:
04 June - 06 June, 2019
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
Deviations:
yes
Remarks:
Experimental temperature 20.0 – 23.8 °C [not in the desired range (18.0 – 22.0°C)]. Experimental temperature f 20.0 – 23.8 °C [fluctuated by more than ± 1 °C]. As no immobility was observed in the blank control these deviations was stated as uncritical.
GLP compliance:
yes (incl. QA statement)
Analytical monitoring:
yes
Details on sampling:
see report attached
Vehicle:
yes
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A stock solution containing 100.6 mg/L test item in dilution water was prepared. The lower treatments (4.6 / 10 / 22 / 46 mg/L nominal) were prepared by dilution of this stock solution with dilution water. The appearance of the final solutions was clear and free of turbidity.
The concentrations 46 mg/L (2x) and 100 mg/L (5x) were diluted, because they were not in the calibrated range.
- Controls:
Blank control 4 vessels, each containing 20 ± 5 mL dilution water and 5 daphnia
- Chemical name of vehicle: Water
- Concentration of vehicle in test medium:
stock solution containing 100.6 mg/L test item
final test solutions 4.6 / 10 / 22 / 46 mg/L nominal
- Evidence of undissolved material (e.g. precipitate, surface film, etc.): the final solutions were clear and free of turbidity
Test organisms (species):
Daphnia magna
Details on test organisms:
TEST ORGANISM
- Common name: Daphnia magna
- Strain/clone: STRAUS
- Age at study initiation (mean and range, SD): between 0 and 24 hours
- Method of breeding: In-house breeding
- Feeding during test
- Food type: green algae (Desmodesmus subspicatus)
- Photo period: 16/8 hours, using neon tubes
- Medium: M4-Medium (recipe of ELENDT)
- Medium renewal: twice a week
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
48 h
Remarks on exposure duration:
Observation times 24 and 48 hours
Test temperature:
20.0 – 23.8 °C
pH:
7.5 - 7.8
Dissolved oxygen:
8.7 - 8.9
Nominal and measured concentrations:
4.6 / 10 / 22 / 46 / 100 mg/L (nominal concentration)
4.09 / 9.59 / 22.84 / 47.20 / 11.46 mg/l (measured concentration t= 48h)
Reference substance (positive control):
yes
Remarks:
Potassium dichromate K2Cr2O7
Duration:
24 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
48 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
48 h
Dose descriptor:
NOEC
Effect conc.:
ca. 46 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
48 h
Dose descriptor:
LOEC
Effect conc.:
ca. 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility

FINDINGS

Immobility

In the blank control, none of the daphnia was immobilised (see table below).

Table: Immobility

Conc (mg/l)

Immobility 24 hours

Immobility 48 hours

Absolute

%

Absolute

%

Blank

0

0

0

0

0

0

0

0

0

0

4.6

0

0

0

0

0

1

0

0

0

5

10

0

0

0

0

0

0

0

0

0

0

22

0

0

0

0

0

0

0

0

0

0

46

0

0

0

0

0

0

1

0

0

5

100

0

0

0

1

5

0

3

2

2

35

 

pH and O2

The pH values and the concentration of dissolved oxygen in the test media and the blank

control are given in the following table:

Table: pH and O2-values

Conc (mg/l)

pH

O2-Concentration in mg/L

0 h

48 h

0 h

48 h

Blank

7.8

7.7

8.9

8.7

4.6

7.8

7.7

8.9

8.7

10

7.8

7.7

8.9

8.8

22

7.8

7.7

8.9

8.7

46

7.7

7.7

8.9

8.7

100

7.5

7.7

8.9

8.7

 

Analytical Determinations

At the beginning and at the end of the test, the content of the test item in the test solutions was determined using a photometer. The concentrations determined at the start of the test laid between 82 % and 101 % of the nominal concentration. At the end of the test the determined concentrations laid between 89 % and 111 % of the nominal concentration.

Therefore, the determination of the biological results was based on the nominal concentration (see Guidance Doc. No.23 (§176)). The measured QC sample (10 mg/L) was taken into account at the beginning (96.7 %) and the end of the test (96.4 %). The concentrations 46 mg/L (2x) and 100 mg/L (5x) were diluted, because they were not in the calibrated range.

The measured concentrations for treatment and blank control are given in the following table:

 

Table: Raw Data and Measured Concentration

 

Nominal concentration

Absorbance t = 0 h

Absorbance t = 48 h

Meas. Conc. T= 0 h*

Meas. Conc. T= 48 h*

 

 

 

mg/l

mg/l

Blank control

0.0000

0.0000

0.016

0.16

0.0000

0.0001

0.016

0.025

4.6

0.0387

0.0419

3.640

3.940

0.386

0.0419

3.630

3.940

10

0.0926

0.0982

8.715

9.245

0.0925

0.0982

8.706

9.245

22

0.2147

0.2321

20.341

22.013

0.2147

0.2321

20.341

22.013

46

0.2357

0.2398

22.359

22.754

0.2356

0.2397

22.350

22.744

100

0.261

0.2267

19.517

21.494

0.2060

0.2266

19.507

21.484

QC (10 mg/l)

0.1027

0.1024

9.670

9.642

0.1027

0.1023

9.670

9.632

*Without dilution factor and recovery of the QC samples

 

Table: Measured Concentrations and % of Nominal Concentration

 

Nominal conc.

(mg/l)

Meas. Conc t = 0 h

(mg/l)

Meas. Conc t = 48 h

(mg/l)

% of Nominal

Conc. t = 0 h

% of Nominal

Conc. t = 48 h

Blank

0.02

0.02

-

-

4.6

3.76

4.09

82

89

10

9.01

9.59

90

96

22

21.04

22.84

96

104

46

46.24

47.20

101

103

100

100.89

111.46

101

111

LOQ

0.5

0.5

-

-

LOQ = limit of quantification

 

RESULTS AND STATISTICS

The estimation of the biological results was accomplished using the software ToxRat® Professional, version 3.3.0.

 

VALIDITY

-         Immobilisation in the controls may not exceed 10 %.

Immobilisation in the controls was 0 %.

-         The concentration of dissolved oxygen at the end of the test must be at least 3 mg/L.

The lowest concentration of dissolved oxygen at the end of the test was 8.7 mg/L.

Validity criteria fulfilled:
yes
Remarks:
Immobilisation in the controls may not exceed 10 % [It was 0 %]. The concentration of dissolved oxygen at the end of the test must be at least 3 mg/L [It was 8.7 mg/L].
Conclusions:
48h-EC50 > 100 mg/L
Executive summary:

Guidelines

One valid experiment was performed according to the OECD Guideline 202.

 

Discussion

The study was performed using 5 concentrations ranging from 4.6 to 100 mg/L nominal concentration. For each test concentration and the blank control, 20 daphnia were exposed to the test item for 48 hours in a static test system. After 24 and 48 hours, the immobilised daphnia were counted. Three concentrations showed toxicity between 5 and 35 % immobilisation. None of the animals was immobilised in the blank control. Because of the immobilisation of 35 % in the highest tested concentration at 48 h, the 48h-EC50was set as higher than the highest tested concentration. At the beginning and at the end of the test, the content of the test item in the test solutions was determined using a photometer. The concentrations determined at the start of the test laid between 82 % and 101 % of the nominal concentration. At the end of the test the determined concentrations laid between 89 % and 111 % of the nominal concentration. Therefore, the determination of the biological results was based on the nominal concentration. Potassium dichromate K2Cr2O7(CAS No. 7778-50-9) was used as positive control in a current reference study to assure that the test conditions are reliable. No observations were made which might cause doubts concerning the validity of the study outcome. All validity criteria were met.

The result of the test is considered valid.

 

Results

The following results were determined for the test item (species:Daphnia magna).

48h-NOEC = 46 mg/L

48h-LOEC = 100 mg/L

24h-EC50 > 100 mg/L

48h-EC50 > 100 mg/L

Description of key information

EC50 (48h) > 100 mg/l

Key value for chemical safety assessment

Fresh water invertebrates

Fresh water invertebrates
Effect concentration:
100 mg/L

Additional information

The acute toxicity of the test item to aquatic invertebrated was investigated on Daphnia magna STRAUS according to the OECD Guideline 202.

the test was performed using 5 concentrations ranging from 4.6 to 100 mg/L nominal concentration. For each test concentration and the blank control, 20 daphnia were exposed to the test item for 48 hours in a static test system.

After 24 and 48 hours, the immobilised daphnia were counted. None of the animals was immobilised in the blank control. Because of the immobilisation of 35 % in the highest tested concentration at 48 h, the 48h-EC50 was set as higher than the highest tested concentration (EC50 48h >100 mg/l)