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Ecotoxicological information

Short-term toxicity to fish

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Reference
Endpoint:
short-term toxicity to fish
Type of information:
experimental study
Adequacy of study:
key study
Study period:
Experimental start date: October 28, 2019; Experimental completion date: December 19, 2019
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Reason / purpose for cross-reference:
reference to other study
Qualifier:
according to guideline
Guideline:
OECD Guideline 203 (Fish, Acute Toxicity Test)
Version / remarks:
2019
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Analytical monitoring:
yes
Details on sampling:
- Concentrations: Control and 100 mg/L treatment
- Sampling method: For the determination of the test item concentrations, duplicate samples were taken from the test media of the test concentration and the control at the start and at the end of the test.
- Sample storage conditions before analysis: All samples were stored frozen (-20 ± 5 °C) immediately after sampling until analysis.
- Analysed samples: The concentrations of the test item were measured in one of the duplicate test medium samples of the single test concentration and the control, taken at the start and end of the test.
Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: At the start of the test, a stock solution with a nominal test item concentration of 500 mg/L was prepared by mixing 1.501 g test item into 3000 mL test water using intense stirring for 15 minutes at room temperature. A volume of 2400 mL of this intensively mixed stock solution was added to test water to make up a volume of 12 L test medium, resulting in a test item nominal concentration of 100 mg/L.
- Controls: A control (test water without test item) was tested in parallel.
- Evidence of undissolved material: No remarkable observations were made concerning the appearance of the test medium. Test medium was clear throughout the entire test duration.
Test organisms (species):
Oncorhynchus mykiss (previous name: Salmo gairdneri)
Details on test organisms:
•TEST ORGANISM
- Common name: Rainbow trout
- Source: The test fish were obtained from fish breeding farm Störk, 88348 Bad Saulgau, Germany.
- Age at study initiation: The study was performed with juvenile fish. The fish were obtained from a commercial breeder 12 days before start of the test.
- Length at study initiation: From the acclimatized test fish batch, a representative sub-batch of 10 fish was measured at the start of the test. The mean total body length (measured from the mouth to the end of the tail fin) of the fish was 3.4 ± 0.25 cm (Mean ± SD). The measured fish were not used for the test.
- Weight at study initiation: From the acclimatized test fish batch, a representative sub-batch of 10 fish was measured at the start of the test. The mean body wet weight was 1.1 ± 0.30 g (Mean ± SD). The measured fish were not used for the test.

•ACCLIMATION
- Acclimation period: The fish were acclimatized to the test water and test temperature for seven days prior to test start.
- Acclimation conditions: Same as test
- Type and amount of food during acclimation: During holding and acclimatization until one day before the start of the test, the fish were fed with a commercial fish diet (Hokovit, Hofmann Nutrition AG, CH-4922, Bützberg, Switzerland).
- Health during acclimation (any mortality observed): During the 10 days prior to the main test, no significant mortality was observed in the test fish batch (1 fish out of 194 had died) and all fish were healthy. No medication was applied during holding and acclimatization of the fish.
Test type:
static
Water media type:
freshwater
Remarks:
Reconstituted test water (EPA Medium) was used in the study.
Limit test:
yes
Total exposure duration:
96 h
Hardness:
The total hardness of the reconstituted test water was measured to be 120 m g/L (as CaCO3), i.e. in the recommended range of 40-250 (preferably <180) mg/L (as CaCO3) (in the reconstituted test water before the initiation of the test).
Test temperature:
The water temperature in the test vessels was maintained at 13 °C during the test period. For this, the aquaria were placed in a temperature regulated water bath.
pH:
The pH throughout the test ranged from 6.5 to 7.2.
Dissolved oxygen:
The dissolved oxygen concentration was in the range of 9.6 to 9.7 mg/L at the start of the test and in the range of 9.5 to 9.7 mg/L (i.e. 90-92 % saturation) from day 1 to the end of the test.
Conductivity:
The conductivity was 353 μS/cm (measured in the reconstituted test water before the initiation of the test)
Nominal and measured concentrations:
Nominal 100 mg/L.
- The measured concentration of the test item in the test medium was 106 and 105 % of the nominal value at the start and the end of the test, respectively.
Details on test conditions:
•TEST SYSTEM
- Test vessel: Mono block aquarium
- Material, size, headspace, fill volume: Glass, 13 L, 1 L, 12 L
- Aeration: The test water was aerated prior to the preparation of the test media until oxygen saturation was reached. The test medium and the control were not aerated during the test.
- No. of organisms per vessel: At the start of the test, seven fish were introduced into each aquarium in a random order.
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
- Biomass loading rate: The loading rate of the fish was 0.20 g fish wet weight per liter medium.

•TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstituted test water was used in the study. It consisted of analytical grade salts dissolved in purified water to obtain the following nominal concentrations:
- Ingredient / Concentration mmol/L / Concentration mg/L
• CaCl2 × 2H2O / 1.0 / 147
• MgSO4 × 7H2O / 0.25 / 61.5
• NaHCO3 / 0.38 / 32.5
• KCl / 0.038 / 2.9
- Alkalinity: The alkalinity was measured to be 0.5 mmol/L (in the reconstituted test water before the initiation of the test)
- Ca/Mg ratio (molar): 1.0÷0.25 = 4

•OTHER TEST CONDITIONS
- Adjustment of pH: Since the pH of the test medium was 3.6 after preparation and outside of the recommended range of 6 to 9, the pH of the test medium was adjusted to 6.5 with 1 M sodium hydroxide solution.
- Photoperiod: A 16-hour light to 8-hour dark photoperiod with a 30-minute transition period was used.
- Light intensity: The light intensity during the light period was approximately 12 to 13 microeinstein [μE/(m²·s)]

•EFFECT PARAMETERS MEASURED
The test fish were observed for mortality and visible abnormalities approximately 2 and 5 hours after the start of the exposure and further on each exposure day in the morning and the afternoon. The fish were checked for the mandatory clinical signs presented below, including the corresponding sub-categories (as presented in Annex 4 of the test guideline):
•E: Loss of equilibrium
•S: Abnormal swimming behavior
•V: Ventilatory function
•P: Abnormal skin pigmentation
•O: Other visible abnormalities

•TEST CONCENTRATIONS
- Spacing factor for test concentrations: Not applicable in a limit test

•RANGE-FINDING STUDY
- Test concentrations: 1, 10 and 100 mg/L
- Results used to determine the conditions for the definitive study: No effects observed
Reference substance (positive control):
no
Key result
Duration:
96 h
Dose descriptor:
NOEC
Effect conc.:
>= 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mortality (fish)
Key result
Duration:
96 h
Dose descriptor:
LC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mortality (fish)
Details on results:
In the control and the test item nominal concentration of 100 mg/L, all fish survived until the end of the test and no visible abnormalities were observed in the test fish.
- Behavioural abnormalities: None.
- Mortality of control: None
- Other adverse effects control: None
- Abnormal responses: None.
- Any observations that might cause a difference between measured and nominal values: None. No remarkable observations were made concerning the appearance of the test medium. Test medium was clear throughout the entire test duration.
- Effect concentrations exceeding solubility of substance in test medium: No
Reported statistics and error estimates:
No statistics needed due to the absence of toxicity of the test item. The 24 and 48-hour EC50 of the test item could not be calculated.
Sublethal observations / clinical signs:

No fish in the control died during test period (mortality should be ≤ 10% or 1 fish if seven used). Oxygen concentration did not drop below actual minimum 90% (should be >60%). Analytical dose verification confirmed the exposure to the test item.

Validity criteria fulfilled:
yes
Conclusions:
The test item was not acutely toxic to rainbow trouts (Oncorhynchus mykiss) in a 96-hour static limit test up to the nominal concentration of 100 mg/L.
Executive summary:

The acute toxicity of the test item to juvenile fish of the species rainbow trout (Oncorhynchus mykiss) was determined under GLP in a 96 hour static test according to the OECD TG 203, adopted 2019. The validity criteria were met. On the basis of the pre-test results, a limit test was performed in accordance with the test guideline to demonstrate that the test item has no toxic effect on the test organisms up to and including the nominal concentration of 100 mg/L during an exposure period of 96 hours. A control was tested in parallel. Seven fish were used in the treatment group and the control. The fish were observed for visible abnormalities and mortality at approximately 2 and 5 hours after the start of exposure and twice every 24 hours period thereafter.


No remarkable observations were made concerning the appearance of the test medium. Test medium was clear throughout the entire test duration. The measured concentration of the test item in the test medium was 106 and 105 % of the nominal value at the start and the end of the test, respectively. The test item showed no toxicity under the conditions of the test.

Description of key information

96-hour LC50 >100 mg/L, rainbow trout

Key value for chemical safety assessment

Additional information

The acute toxicity of the substance to the freshwater fish rainbow trout (Oncorhynchus mykiss) was studied under GLP to OECD TG 203 over a period of 96 hours. The substance did not exhibit any adverse effects on the test organisms and the 96-hour LC50 value was greater than 100 mg/L.