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Ecotoxicological information

Short-term toxicity to fish

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Administrative data

Link to relevant study record(s)

Reference
Endpoint:
short-term toxicity to fish
Type of information:
experimental study
Adequacy of study:
key study
Study period:
1987-11-17 to 1987-11-21
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
guideline study with acceptable restrictions
Qualifier:
according to guideline
Guideline:
OECD Guideline 203 (Fish, Acute Toxicity Test)
Version / remarks:
Supposed as the informatiom was not reported.
GLP compliance:
yes
Analytical monitoring:
yes
Remarks:
GC-analysis
Details on sampling:
A sub-sample (250 ml) of the test solution was measured into a separating funnel and extracted with dichloromethane (2 x 75 ml). The extracts were filtered through anhydrous sodium sulphate and combined in a round bottomed flask. The solvent was evaporated under vacuum just to dryness (RFE at 35 °C) and the residue dissolved in an appropriate volume of carbon tetrachloride (4-30 ml).
Vehicle:
yes
Remarks:
Tween 80-acetone
Details on test solutions:
Preliminary solution in 10% Tween 80-acetone.
Test organisms (species):
Oncorhynchus mykiss (previous name: Salmo gairdneri)
Details on test organisms:
TEST ORGANISM
- Common name: Rainbow trout
- Strain: Salmo gairdneri
- Source: Parkwood Trout Farm, Kent.
- Length at study initiation (length definition, mean, range and SD): 4.2 cm (S.D. = 0.4 cm)
- Weight at study initiation (mean and range, SD): 1.38 g (S.D. = 0.37 g)

ACCLIMATION
- Acclimation period: Stock held since 9 October 1986 and acclimatised to test conditions from 3'November 1986.
- Acclimation conditions (same as test or not): yes
- Type and amount of food during acclimation: Commercial trout pellets, daily. Discontinued 24 h prior to test
- Health during acclimation (any mortality observed): 0%
Test type:
semi-static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
96 h
Hardness:
350 mg/L as CaCO3 (This value is slightly higher than the recommended Tange but is not considered to have had any significant effects an the results of the test).
Test temperature:
13 +/- 1 °C
pH:
7.4 - 7.8
Dissolved oxygen:
9.6 -10.7 mg/L
Nominal and measured concentrations:
Nominal concentrations: 0.56, 1.0, 1.8, 3.2 and 5.6 mg/L;
Mean measured concentrations:
at 0 h: 0.597, 1.06, 1.79, 3.101 and 5.374 mg/L;
at 24 h: 0.071, 0.207, 0.600, 1.787 and 3.353 mg/L;
at 96 h: 0.06 and 0.309 mg/L (only for the nominal concentraion 0.56 and 1.0 mg/L)
Details on test conditions:
TEST SYSTEM
- Test vessel: Glass aquaria
- Fill volume: 20 L
- Aeration: Gentle aeration via narrow bore glass tubes.
- Renewal rate of test solution (frequency): 24 h
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 1
- No. of vessels per vehicle control (replicates): 1
- Biomass loading rate: 0.69 g/L

OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 h light / 8 h dark

TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.8
Key result
Duration:
96 h
Dose descriptor:
LC50
Effect conc.:
0.75 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mortality (fish)
Details on results:
See below
Sublethal observations / clinical signs:

Cumulative mortality data for rainbow trout exposed for 96 h to test item:








































































Concentration [mg/L]



Cumulative mortality (initial population : 10)



3 h



6 h



24 h



48 h



72 h



96 h



Control



0



0



0



0



0



0



0.56



0



0



0



1



1



1



1.0



1



1



1



5



6



9



1.8



1



8



10



10



10



10



3.2



3



9



10



10



10



10



5.6



8



10



10



10



10



10


Validity criteria fulfilled:
yes
Conclusions:
The value of LC50 (96 h) of the test item to fish was determined to be 0.75 mg/L based on the nominal concentration.
Executive summary:

The acute biological effect of the item on fish was performed with Rainbow trout according to OECD TG 203 (1984) and GLP. The test was conducted under semi-static conditions with 5 concentrations: 0.56, 1.0, 1.8, 3.2 and 5.6 mg/L with a spacing factor of 1.8. The preliminary solution was prepared in 10% Tween 80-acetone. The concentrations were measured via GC-method. The value of LC50 (96 h) of the test item to fish was determined to be 0.75 mg/L based on the nominal concentration.

Description of key information

A study on the acute toxicity of the item to fish is available. The test was performed with Rainbow trout according to OECD TG 203 (1984) and GLP under semi-static conditions with 5 concentrations: 0.56, 1.0, 1.8, 3.2 and 5.6 mg/L with a spacing factor of 1.8. The preliminary solution was prepared in 10% Tween 80-acetone. The concentrations were measured via GC-method. The value of LC50 (96 h) of the test item to fish was determined to be 0.75 mg/L based on the nominal concentration.

Key value for chemical safety assessment

Fresh water fish

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

Additional information