Registration Dossier

Data platform availability banner - registered substances factsheets

Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Ecotoxicological information

Short-term toxicity to aquatic invertebrates

Currently viewing:

Administrative data

Link to relevant study record(s)

Reference
Endpoint:
short-term toxicity to aquatic invertebrates
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2020-06-11 to 2020-08-27
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)
Version / remarks:
Adopted April 13, 2004
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.2 (Acute Toxicity for Daphnia)
Version / remarks:
June 6, 2008
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Analytical monitoring:
yes
Details on sampling:
- Sampling method: The samples were taken from the biological phase of the study. Duplicate samples from the freshly prepared test media of all test concentrations and the control were taken at the start of the test and at day 1. For the determination of the stability of the test item under the test conditions and of the maintenance of the test item concentrations during the test period, duplicate samples from the aged test media of all test concentrations and the control were collected at day 1 (after 24 hours of exposure) and at the end of the test by pouring together the contents of the test beakers of each treatment. All samples remained undiluted until analysis.

- Sample storage conditions before analysis: All samples were stored in a freezer (≤ - 20 °C), protected from light, until analysis was performed.
Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The test medium of the only test item concentration of nominal 100 mg/L was prepared by dissolving 51.7 and 49.0 mg test item into 517 and 490 mL test water by intense stirring for 25 and 20 minutes. The test media was prepared just before introduction of the daphnids (= start of the test) and test medium renewal on Day 1.

- Controls: In the control, test water was used without addition of the test item.

- Evidence of undissolved material: There were no remarkable observations
Test organisms (species):
Daphnia magna
Details on test organisms:
TEST ORGANISM
- Strain/clone: Daphnia magna (Straus), clone 5
- Stage and instar at study initiation: from 1.5 to 16.25 hours old
- Breeding conditions: The daphnids were bred in the laboratory under similar temperature and light conditions as used in the test. The cultivation of the parental daphnids was performed in Elendt M4 medium. The test organisms were not first brood progeny. The daphnids in the stock culture were fed at least on all working days with freshly grown green algae (Desmodesmus subspicatus).
Source: ibacon's in-house laboratory culture

ACCLIMATION
- Acclimation period: Was not necessary, since the test was performed in the same medium used for the culture
Test type:
semi-static
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
48 h
Hardness:
2.5 mmol/L (= 250 mg/L) as CaCO3
Test temperature:
20.3 to 20.4 °C in the freshly prepared media;
20.2 to 20.3°C in the aged test media
pH:
7.9 to 8.0 in the freshly prepared media;
8.0 in the aged test media
Dissolved oxygen:
8.6 to 8.8 mg/L in the freshly prepared media;
8.7 to 8.8 mg/L in the aged test media
Nominal and measured concentrations:
Nominal conc.: 100 mg/L; Measured concentration: 96% of nominal measured concentration
Details on test conditions:
TEST SYSTEM
- Test vessel: Glass beakers of 100 mL volume containing approximately 60 mL of test medium.
- Type: closed (The test vessels were covered with a lid to reduce the loss of water due to evaporation and to avoid the entry of dust into the solutions).
- Volume of solution: ca. 60 mL
- Renewal of test solution: test medium renewal was done on Day 1
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4

TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstituted Water (Elendt "M4"):
- Culture medium different from test medium: no, the same

OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 h light: 8 h dark
- Light intensity: 260 to 440 lux

EFFECT PARAMETERS MEASURED: The number of immobile daphnids were determined by visual observation and recorded after 24 and 48 hours.

RANGE-FINDING STUDY
- Test concentrations: 100 mg test item/L and a control.
- Results used to determine the conditions for the definitive study: yes
Reference substance (positive control):
yes
Remarks:
Potassium dichromate
Key result
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:
EC10
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Key result
Duration:
48 h
Dose descriptor:
NOEC
Effect conc.:
>= 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
48 h
Dose descriptor:
LOEC
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Details on results:
After 48 hours of exposure no immobilisation of the test animals was observed in the control and the only test item concentration of 100 mg test item/L.
Results with reference substance (positive control):
- Results with reference substance valid? Yes
- Relevant effect levels: 48-h EC50: 0.986 mg/L

Table 1: Summary of Biological Results

Nominal Concentration

[mg test item/L]

% of immobilised daphnids after

24 hours

48 hours

Control

0

0

100

0

0

EC50 [mg test item/L]:

> 100

> 100

95 % CI [mg test item/L]:

n.d.

n.d.

EC20 [mg test item/L]:

> 100

> 100

95 % CI [mg test item/L]:

n.d.

n.d.

EC10 [mg test item/L]:

> 100

> 100

95 % CI [mg test item/L]:

n.d.

n.d.

NOEC [mg test item/L]:

≥ 100

≥ 100

LOEC [mg test item/L]:

> 100

> 100

 

Values refer to nominal test concentrations

CI: Confidence interval

n.d.: not determinable

NOEC and LOEC were determined directly from the raw data.

 

Table 2: Summary of Analytical Results

Sample Description

(mg test item/L)

% of nominal1

RSD

(%)

Control

n.a.

n.a.

100

96

1

 

1 mean value of all measured samples per treatment group

RSD: relative standard deviation per treatment group

n: number of analysed samples

n.a.: not applicable

 

Table 3: Influence of the test item on the Mobility of Daphnia magna and Sublethal Effects

 

Nominal concentration (mg test item/L)

No. of Daphnia tested

No. of immobilised Daphnia after

% of immobilised Daphnia after

Observations

24 h

48 h

24 h

48 h

24 h

48 h

Control

5

0

0

0

0

0

0

5

0

0

0

0

5

0

0

0

0

5

0

0

0

0

100

5

0

0

0

0

0

0

5

0

0

0

0

5

0

0

0

0

5

0

0

0

0

Abbreviations for observations:

0: No abnormalities

 

Table 4: Results of the Analytical Determination of the Test Item in the Test Samples

Sample Description

Concentration

found

Concentration

calculated

[mg test item/L]

Concentration

nominal

[mg test item/L]

% of

nominal1

 

Sampling Age

[mg test item/L]

day

[h]

[mg test item/L]

D.F.

Control

0

0

<LOD

1

n.a

0.000

n.a

Control

0

0

<LOD

1

n.a

0.000

n.a

Control

1

24

<LOD

1

n.a

0.000

n.a

Control

1

24

<LOD

1

n.a

0.000

n.a

Control

1

0

<LOD

1

n.a

0.000

n.a

Control

1

0

<LOD

1

n.a

0.000

n.a

Control

2

24

<LOD

1

n.a

0.000

n.a

Control

2

24

<LOD

1

n.a

0.000

n.a

100

0

0

95.062

1

95.062

100.000

95

100

0

0

95.841

1

95.841

100.000

96

100

1

24

95.286

1

95.286

100.000

95

100

1

24

94.553

1

94.553

100.000

95

100

1

0

97.621

1

97.621

100.000

98

100

1

0

97.330

1

97.330

100.000

97

100

2

24

96.879

1

96.879

100.000

97

100

2

24

95.585

1

95.585

100.000

96

           

mean value (n=8):

96

           

RSD (n=8):

1

 

1 The tabulated results represent rounded results calculated on the exact raw data LOD: Limit of Detection = 0.3 mg test item/L

n.a.: not applicable

RSD: Relative Standard Deviation

D.F.: Dilution factor

Validity criteria fulfilled:
yes
Conclusions:
In the 48-h acute toxicity of the test item on Daphnia magna according to OECD T 202, no immobilisation was observed in the control and in the 100 mg/L concentration group. In both groups no abnormal behaviour or appearance of test animals was noted. The 48-h NOEC was determined to be > 100 mg/L. The 48-h LOEC and the EC50 values were determined to be > 100 mg/L.
Executive summary:

The influence of the test item on the mobility of Daphnia magna was determined in a 48-h “Acute Immobilisation Test” according to OECD TG 202 and under GLP conditions. For this purpose, young daphnids (< 24 hours old) were exposed in a semi-static test for 48 hours to the only concentration of nominal 100 mg/L under defined conditions. The recorded effects were the mobility of the daphnids after 24 and 48 hours. This limit-test was performed in compliance with the test guidelines in order to demonstrate that the test item has no toxic effects on the daphnids up to this concentration. The test method and the test species Daphnia magna are recommended by the test guidelines. This study encompassed two treatment groups (one test item concentration at nominal 100 mg/L, and one control) each containing 20 individuals. The mobility of the daphnids was determined by visual observation after 24 and 48 hours. Environmental conditions were recorded. All measured values remained within acceptable ranges. No immobilisation or any abnormal behaviour was observed in the control and the 100 mg/L concentration group after 48 hours of exposure. All validity criteria were within acceptable limits and therefore, the study was considered valid. The quantification of the test item in the test samples was performed using high performance liquid chromatography with HPLC-UV detection. The purpose of the analytical part of this study was to verify the concentration of the test item in the test medium. The analytically measured test item concentration remained within ± 20 % of the nominal during the test period of 48 hours; therefore, biological results are based on the nominal concentration. The 48-h NOEC was determined to be > 100 mg/L. The 48-h LOEC and the EC50 values were determined to be > 100 mg/L.

Description of key information

In the 48-h acute toxicity of the test item on Daphnia magna according to OECD T 202, no immobilisation was observed in the control and in the 100 mg/L concentration group. In both groups no abnormal behaviour or appearance of test animals was noted. The 48-h NOEC was determined to be > 100 mg/L. The 48-h LOEC and the EC50 values were determined to be > 100 mg/L (reference 6.1.3-1).

Key value for chemical safety assessment

Additional information

The influence of the test item on the mobility of Daphnia magna was determined in a 48-h “Acute Immobilisation Test” according to OECD TG 202 and under GLP conditions. For this purpose, young daphnids (< 24 hours old) were exposed in a semi-static test for 48 hours to the only concentration of nominal 100 mg/L under defined conditions. The recorded effects were the mobility of the daphnids after 24 and 48 hours. This limit-test was performed in compliance with the test guidelines in order to demonstrate that the test item has no toxic effects on the daphnids up to this concentration. The test method and the test species Daphnia magna are recommended by the test guidelines. This study encompassed two treatment groups (one test item concentration at nominal 100 mg/L, and one control) each containing 20 individuals. The mobility of the daphnids was determined by visual observation after 24 and 48 hours. Environmental conditions were recorded. All measured values remained within acceptable ranges. No immobilisation or any abnormal behaviour was observed in the control and the 100 mg/L concentration group after 48 hours of exposure. All validity criteria were within acceptable limits and therefore, the study was considered valid. The quantification of the test item in the test samples was performed using high performance liquid chromatography with HPLC-UV detection. The purpose of the analytical part of this study was to verify the concentration of the test item in the test medium. The analytically measured test item concentration remained within ± 20 % of the nominal during the test period of 48 hours; therefore, biological results are based on the nominal concentration. The 48-h NOEC was determined to be > 100 mg/L. The 48-h LOEC and the EC50 values were determined to be > 100 mg/L.