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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:
2015
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 203 (Fish, Acute Toxicity Test)
Version / remarks:
17 July 1992
Deviations:
not specified
GLP compliance:
yes
Analytical monitoring:
yes
Details on sampling:
Samples were taken at 0, 96 h and 24 h, 48 h, 72 h (before and after test solution renewal)
Vehicle:
yes
Remarks:
test water
Test organisms (species):
Danio rerio (previous name: Brachydanio rerio)
Details on test organisms:
TEST ORGANISM
- Common name: zebra fish
- Source: Guangzhou Yangshi breeding farm
- Length at study initiation (length definition, mean, range and SD): 2.0-4.0 cm

ACCLIMATION
- Acclimation period: 23 days
- Acclimation conditions (same as test or not): same
- Type and amount of food during acclimation: 3 times per day until 24 h before test
- Health during acclimation (any mortality observed): 0.9% mortality during 7 days preceding the test

FEEDING DURING TEST : no
Test type:
semi-static
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
96 h
Hardness:
111 mg CaCO3/L
Test temperature:
21.2 - 22.9 °C
pH:
7.41 - 7.90
Dissolved oxygen:
min. 60% of air saturation value
Nominal and measured concentrations:
Nominal: 0.26, 0.36, 0.51, 0.71, 1.0 mg/L
Measured: 0.0492, 0.0580, 0.0677, 0.0819, 0.0936 mg/L (geometric means)
Details on test conditions:
14 h light / 10 h darkness
Mortality and visible abnormalities were recorded at 3, 24, 48, 72, and 96 h after the start of the test
Reference substance (positive control):
yes
Remarks:
Potassium dichromate
Key result
Duration:
96 h
Dose descriptor:
LC50
Effect conc.:
0.42 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mortality (fish)
Duration:
96 h
Dose descriptor:
LC50
Effect conc.:
59.4 µg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
mortality (fish)
Duration:
96 h
Dose descriptor:
LC100
Effect conc.:
81.9 µg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
mortality (fish)
Duration:
96 h
Dose descriptor:
NOEC
Effect conc.:
< 0.049 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
mortality (fish)
Details on results:
- Behavioural abnormalities: spasmodic swimming, reduced activity, overturn and loss of equlibrium were observed at all dose levels
- Observations on body length and weight: no effects
- Other biological observations: none
- Mortality of control: no effects
- Other adverse effects control: no effects
- Abnormal responses:no effects
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: no effects
- Effect concentrations exceeding solubility of substance in test medium: no
Results with reference substance (positive control):
K2Cr2O7: 24-h LC50 = 282 mg/L, 95% CI: 251 - 318 mg/L (LC50 validity range: 200 - 400 mg/L)
Reported statistics and error estimates:
96-h LC50 = 0.0594 mg/L, 95% CI: 0.0568 - 0.0621 mg/L
Sublethal observations / clinical signs:

Nominal conc. (mg/L)

No. of fish in group

Cumulative mortality (%) after (h)

3

24

48

72

96

0

21

0

0

0

0

0

0.26

21

0

0

0

4.8

4.8

0.36

21

4.8

4.8

29

38

37

0.51

21

38

67

90

90

90

0.71

21

81

100

100

100

100

1.0

21

100

100

100

100

100

 

Validity criteria fulfilled:
yes
Remarks:
mortality of controls < 10% (0%), dissolved oxygen >60% (80-100%), the measured concetrations (geomean) are used since these were outside the 80-120% window
Conclusions:
96 hLC50 = 0.42 mg/L, nominal
Executive summary:

The short-term toxicity of GDMP to zebra fish (Brachydanio rerio) was assessed in a study according to OECD TG 203. The fish were exposed to five test concentrations of 0.26, 0.36, 0.51, 0.71 and 1.0 mg/L (nominal) of the test item under semi-static conditions (renewal every 24 h).


The cumulative mortality was 0% at the end of the test. The cumulative mortality in teh 0.26, 0.36, 0.51, 0.71 and 1.0 mg/Lgroups was 4.8, 38, 90, 100 and 100%, respectively.No abnormal sublethal responsed were observed in the control. Behavioural abnormalities including spasmodic swimming, reduced activity, overturn and loss of equlibrium were observed at all concentrations levels.


Under the conditions of this test, the 96 h LC50 to Danio rerio was 0.0594 mg/L (mean, meas.).


Since measured values don't represent the real environmental conditions because the test substance is rapidly oxidized by the oxygen content in the aqueous phase.


As the transformation products are less toxic than the parent substances (no free –SH groups) regulatory endpoints calculated on the basis of nominal concentrations represent a realistic worst case approach.  Moreover, for thiochemicals nominal concentrations represent the real environmental conditions, because the test substance is rapidly oxidized by the oxygen content in the aqueous phase.  The effect values therefore reflect the toxicity of the system – in the sense of the UVCB approach – rather than the toxicity of the original chemical substance. Under these conditions it is more meaningful to assess their toxicities on the basis of nominal concentrations instead of measured concentrations during exposure. This may better correspond to the situation under environmental conditions as recommended for multi-component-substances (OECD23).


The 96 h LC50 based on nominal concentrations was determined to be 0.42 mg/L.





 


 

Description of key information

The 96 h LC50 based on nominal concentrations was determined to be 0.42 mg/L.

Key value for chemical safety assessment

Fresh water fish

Fresh water fish
Dose descriptor:
LC50
Effect concentration:
0.42 mg/L

Additional information

The short-term toxicity of GDMP to zebra fish (Brachydanio rerio) was assessed in a study according to OECD TG 203. The fish were exposed to five test concentrations of 0.26, 0.36, 0.51, 0.71 and 1.0 mg/L (nominal) of the test item under semi-static conditions (renewal every 24 h).


The cumulative mortality was 0% at the end of the test. The cumulative mortality in teh 0.26, 0.36, 0.51, 0.71 and 1.0 mg/Lgroups was 4.8, 38, 90, 100 and 100%, respectively.No abnormal sublethal responsed were observed in the control. Behavioural abnormalities including spasmodic swimming, reduced activity, overturn and loss of equlibrium were observed at all concentrations levels.


Under the conditions of this test, the 96 h LC50 to Danio rerio was 0.0594 mg/L (mean, meas.).


Since measured values don't represent the real environmental conditions because the test substance is rapidly oxidized by the oxygen content in the aqueous phase.


As the transformation products are less toxic than the parent substances (no free –SH groups) regulatory endpoints calculated on the basis of nominal concentrations represent a realistic worst case approach.  Moreover, for thiochemicals nominal concentrations represent the real environmental conditions, because the test substance is rapidly oxidized by the oxygen content in the aqueous phase.  The effect values therefore reflect the toxicity of the system – in the sense of the UVCB approach – rather than the toxicity of the original chemical substance. Under these conditions it is more meaningful to assess their toxicities on the basis of nominal concentrations instead of measured concentrations during exposure. This may better correspond to the situation under environmental conditions as recommended for multi-component-substances (OECD23).


The 96 h LC50 based on nominal concentrations was determined to be 0.42 mg/L.