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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:
Nov 20, 2018 - Jan 28, 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)
Version / remarks:
2004
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.2 (Acute Toxicity for Daphnia)
Version / remarks:
Council Regulation (EC) No. 440/2008 laying down test methods pursuant to Regulation (EC) No. 1907/2006 of the European Parliament and the council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH).
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Specific details on test material used for the study:
Preparation of the Test Item:
A stock preparation with a test item concentration of 100 mg/L was freshly prepared. For that purpose, the test item was weighed in a calibrated flask and vehicle was added. The preparation was stirred with a magnetic stirrer for 24 hours. Then the formulation was passed through a filter membrane (pore size: 0.2 µm). The filtrate was used for the study. The pH was not adjusted.
Analytical monitoring:
yes
Details on sampling:
Two replicates of each sample were directly taken after preparation (0 hour) and after 24 and 48 hours and subsequently analysed. The samples were analyzed undiluted due to the very low solubility in water. The concentrations of the test item were determined using the calibration curve. One replicate was used for analysis. The second replicate was used as backup.

Vehicle:
yes
Details on test solutions:
Macro nutrients (mg/L)
CaCI2 •2H20 293.80
MgSO4•7H20 123.30
NaHCO3 64.80
KCI 5.80
Na2SiO3•9H20 10.00
NaNO3 0.27
KH2PO4 0.14
K2HPO4 0.18

Trace elements (mg/L)
B 0.5000
Fe 0.2000
Mn 0.1000
Li, Rb and Sr 0.0500
Mo 0.0250
Br 0.0125
Cu and Zn 0.0063
Co and I 0.0025
Se 0.0010
V 0.0003

Macro nutrients (mg/L)
Na2EDTA • 2H20 2.50

Vitamins (µg/L):
Thiamine 75.00
B12 1.00
Biotin 0.75

- pH: 7.84
- O2: 8.61 mg/L
- Conductivity: 734 µS/cm
- Total hardness: 237 mg CaCO3/L

Preparation of the Test Item:
A stock preparation with a test item concentration of 100 mg/L was freshly prepared. For that purpose, the test item was weighed in a calibrated flask and vehicle was added. The preparation was stirred with a magnetic stirrer for 24 hours. Then the formulation was passed through a filter membrane (pore size: 0.2 µm). The filtrate was used for the study. The pH was not adjusted.
Test organisms (species):
Daphnia magna
Details on test organisms:
Species: Daphnia magna Straus
Culture conditions: The clone is bred in the laboratories of Merck KGaA.
Parental daphnids are used for reproduction until they are about 6 weeks old. Thereafter, they are replaced by neonates.
Daphnids are kept individually in 100 mL glass vessels containing approximately 60 mL reconstituted water (ELENDT M4 medium) at a water temperature of 20 ± 2°C and a 16 hour light and 8 hour dark regime to ensure similar conditions as in the experiment. Offspring are removed from the vessels at least twice per week.
Feeding: The parental daphnids are fed ad libitum with unicellular green algae Desmodesmus subspicatus three times per week.
Age: Offspring less than 24 hours old were used for the study.
Acclimation period: same as test

Feeding during test: None

Test type:
static
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
48 h
Hardness:
232 mg CaCO3/L
Test temperature:
20.3 - 21.0°C
pH:
7.88 to 7.98
Dissolved oxygen:
8.31 - 8.65 mg/L
Conductivity:
717 µS/cm
Nominal and measured concentrations:
Nominal 100 mg/L
Details on test conditions:
TEST SYSTEM
- Test vessel: Glass test tubes
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: 20 mL glass test tubes containing 20 mL medium
- Aeration: no
- 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 medium according OECD 202)
- Total organic carbon: no data
- Particulate matter: no data
- Metals: no data
- Pesticides: no data
- Chlorine: no data
- Alkalinity: no data
- Ca/mg ratio: no data
- Conductivity: 734 µS/cm
- Salinity: no data
- Culture medium different from test medium: no
- Intervals of water quality measurement: at start and end of exposure

OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16h light / 8h dark
- Light intensity: The mean light intensities were 583 Lux and 599 Lux prior to and at the end of the exposure period, respectively.

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Immobilisation (daily)

VEHICLE CONTROL PERFORMED: no

RANGE-FINDING STUDY
- Test concentrations:
100 mg/L (nominal)
< LOD of 0.0056 mg/L (measured)
Reference substance (positive control):
no
Remarks:
No positive control used in this study. The accuracy and reliability of the test method is demonstrated periodically as recommended by guidelines with potassium dichromate.
Key result
Duration:
24 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Remarks on result:
other: EC50 >0.0056 mg/L
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
Remarks on result:
other: EC50 > 0.0056 mg/L
Details on results:
An aqueous solution of nominal 100 mg/L of the test item revealed no aquatic toxicity in the test system.

The 48h EC50 exceeded the LOD of 0.0056 mg/L (nominal >100 mg/L) and, thus, could not be determined in this study.

- Behavioural abnormalities: no
- Other biological observations: no
- Mortality of control: no
- Other adverse effects control: no
- Abnormal responses: no
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: no
Results with reference substance (positive control):
Study No.: 18-DA0616-0

Experimental start date: October 24, 2018
Experimental completion date: October 26, 2018


Objective:
The objective of this study was to determine the effect of the positive control substance
Art. 104864 (Potassium dichromate) on the immobilization of Daphnia magna in order to check the sensitivity of the test system as recommended by guidelines (Council Regulation (EC) No. 440/2008 and OECD Guideline No. 202).

Study design:
Juvenile daphnids were exposed to different concentrations of the test item (0, 0.31, 0.46, 0.69, 1.02 and 1.52 mg/L) in an open static system. 20 daphnids, divided into four replicates, each with five animals were used per concentration and control. The daphnids were observed for immobilization after 24 and 48 hours of exposure.

Results:
No effect on the mobility of the daphnia was observed at the two lowest concentrations of
0.31 mg/L and 0.46 mg/L. A concentration dependent immobilization was observed at concentrations of 0.69 to 1.52 mg/L.


EC50 values with 95% confidence intervals:
24h EC50 0.92 mg/L (0.81 – 1.04 mg/L)
48h EC50 0.70 mg/L (0.62 – 0.79 mg/L)

Conclusion:
Under the conditions of the present study, the test item Art. 104864 (Potassium dichromate) showed a 24h EC50 value of 0.92 mg/L which is within the range of the published data of 0.6 to 1.7 mg/L (Council Regulation (EC) No. 440/2008) and 0.6 to 2.1 mg/L (OECD Guideline No. 202).
Therefore, this study confirms the sensitivity and reliability of the test system used in the test facility.




Objective

The objective of this study was to determine the effect of the test item on the immobilization of Daphnia magna.

Study Design

Juvenile daphnids were exposed to a nominal test item concentration of 100 mg/L (limit test) in an open static system. 20 daphnids, divided into four replicates, each with five animals were used in the test item group and the control group. The daphnids were observed for immobilization after 24 and 48 hours of exposure.

Samples of the test and control media were taken directly after preparation and then daily for test item concentration analysis via HPLC with UV detection.

Results

The measured concentrations of the test material were <LOD (LOD = 0.0056 mg/L) during the experimental phase. No test item was measured in the control medium. Therefore, it was confirmed that daphnia in the control group were not exposed to the test item.

No effect on the mobility of the daphnia was observed at a nominal concentration of 100 mg/L.

For the test item the following EC50 values were determined:

EC50 (24h) >0.0056 mg/L (nominal >100 mg/L)

EC50 (48h) >0.0056 mg/L (nominal >100 mg/L)

Conclusion

Under the conditions of the present study, an aqueous solution of nominal 100 mg/L of the test item revealed no toxicity to daphnids. The 48h EC50 was >0.0056 mg/L (nominal >100 mg/L) and, thus, could not be determined in this study.

Validity criteria fulfilled:
yes
Conclusions:
Under the conditions of the present study, an aqueous solution of nominal 100 mg/L of the test item revealed no toxicity to daphnids.
The 48h EC50 was >0.0056 mg/L (nominal >100 mg/L) and, thus, could not be determined in this study.


Executive summary:

This study was performed according to GLP and the methods applied are fully compliant with OECD TG 202. Under the conditions of the present study, an aqueous solution of nominal 100 mg/L of the test item revealed no toxicity to daphnids. The 48h EC50 was >0.0056 mg/L (nominal >100 mg/L) and, thus, could not be determined in this study.

Description of key information

The 48 h EC50 could not be quantified due to the absence of toxicity at the highest concentration achievable in water.

GLP compliant OECD 202 study: EC50 (48 h) > 100 mg/L (nominal)

Key value for chemical safety assessment

Fresh water invertebrates

Fresh water invertebrates
Effect concentration:
100 mg/L

Additional information