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Short-term toxicity to fish

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Endpoint:
short-term toxicity to fish
Type of information:
experimental study
Adequacy of study:
key study
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: GLP status unknown, guideline study, published in peer reviewed literature, adequate for assessment.
Qualifier:
according to guideline
Guideline:
other: EPA-660/3-75-009
Deviations:
no
GLP compliance:
not specified
Analytical monitoring:
yes
Details on sampling:
A 100 mL water sample was collected and placed in a modified 100 mL volumetric flask. Each aquarium sampled at least 3 times to determine concentration.
Vehicle:
yes
Details on test solutions:
Acetone used as co-solvent to introduce chemicals into the diluter. Nominal acetone concentrations were 79-198 mg/l depending on diluter cell; measured concentrations of acetone in test tanks did not exceed 2% of LC50 for acetone (8,500 mg/l).
Test organisms (species):
Jordanella floridae
Details on test organisms:
Laboratory-reared juvenile (2-4 month old) fish were used. Fish were raised in the dilutent water and fed freshly-hatched and adult brine shrimp.
Test type:
flow-through
Water media type:
freshwater
Limit test:
no
Total exposure duration:
96 h
Post exposure observation period:
None
Hardness:
48 mg/l as CaCO3
Test temperature:
25±2°C
pH:
6.95 ± 0.35
Dissolved oxygen:
>90%
Salinity:
Not applicable
Nominal and measured concentrations:
5 or 6 duplicate concentrations in logarithmic series,
Details on test conditions:
Dechlorinated Lake Superior water taken from the Thunder Bay was used.
Fish were not fed during the test.
Water and acetone (79-198 mg/l) controls were employed.
No aeration was used during the test.
30 litre aquaria, 10 fish per aquarium, flow rate 6 litres/hour
Reference substance (positive control):
not specified
Duration:
96 h
Dose descriptor:
LC50
Effect conc.:
28.3 mg/L
Nominal / measured:
meas. (not specified)
Conc. based on:
test mat.
Basis for effect:
mortality (fish)
Endpoint:
short-term toxicity to fish
Type of information:
experimental study
Adequacy of study:
key study
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Non-GLP, non-guideline study, adequate for assessment
Principles of method if other than guideline:
96h LC50 was determined by the method of Doudoroff et. al. (1951)
GLP compliance:
no
Analytical monitoring:
yes
Vehicle:
not specified
Details on test solutions:
solutions not aerated
Test organisms (species):
Limanda limanda
Details on test organisms:
5 dab (Limanda limanda, marine fish) used, 15-20 cm long
Test type:
flow-through
Water media type:
saltwater
Limit test:
no
Total exposure duration:
96 h
Nominal and measured concentrations:
Measured concentrations
Details on test conditions:
glass flow-through apparatus
Duration:
96 h
Dose descriptor:
LC50
Effect conc.:
16 mg/L

Description of key information

The lowest acute toxicity value for freshwater fish was the 96h LC50 for American flagfish, Jordanella floridae which was 28.3 mg/l.

For marine water fish the lowest toxicity value was the 96h LC50 16 mg/l found in Limanda limanda.

Key value for chemical safety assessment

Fresh water fish

Fresh water fish
Effect concentration:
28.3 mg/L

Marine water fish

Marine water fish
Effect concentration:
16 mg/L

Additional information

Several studies with both freshwater and marine fish are available. For the freshwater compartment a flow-through study with the American flagfish Jordanella floridae, conducted according to the EPA-660/3-75-00 guideline was found to be the most critical (Smithet al.1991). The 96-h LC50 was 28.3 mg/l. For the marine compartment a flow-through study with the dabLimanda limanda, was found to be most critical (Pearsonet al.1975). Although this study was not conducted according to an accepted guideline the study was a well conducted near-guideline study, the 96-h LC50 was 16 mg/l. Other studies were less critical and/or not reliable.