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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

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Diss Factsheets

Ecotoxicological information

Short-term toxicity to fish

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Administrative data

Link to relevant study record(s)

short-term toxicity to fish
Type of information:
experimental study
Adequacy of study:
key study
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: GLP status unknown, guideline unknown, limitations in reporting but otherwise acceptable for assessment.
Principles of method if other than guideline:
A guideline was not specified. The test was a 96-hour static renewal test. The US EPA 2002 guideline EPA-821/R-02-012 is referenced during the description of the method, but the text does not state its use unambiguously.
GLP compliance:
not specified
Specific details on test material used for the study:
Details on properties of test surrogate or analogue material (migrated information):
Not applicable
Analytical monitoring:
Details on sampling:
Samples collected at 0, 48 and 96 hours and immediately acidified. Samples were analysed immediately after each test.
Details on test solutions:
Dechlorinated tap water
Test organisms (species):
Pimephales promelas
Details on test organisms:
< 24 h obtained from Aquatic Biosytems, Fort Collins, CO, USA. Held in University of Miami dechlorinated tap water for 7days prior to testing (reference water) or less dependent on age at time of testing (experimental variable). Various life stages: 1, 4, 7, 27 and 41 days old.
Test type:
Water media type:
Limit test:
Total exposure duration:
96 h
Post exposure observation period:
76 mg/L CaCO3
Test temperature:
Dissolved oxygen:
No data reported
Not applicable
Nominal and measured concentrations:
6 to 7 concentrations - unspecified
Details on test conditions:
Three replicates, ten fish added to each replicate. 1,000 mL plastic beaker containing 500 mL test solution, test solutions renewed at 48 hours (fed Artemia nauplii before solution renewal at 48 hours). Different ages of fish were assessed, ranging from 1-4 days to 41 days at start of test.
Reference substance (positive control):
96 h
Dose descriptor:
Effect conc.:
1.2 µg/L
Nominal / measured:
not specified
Conc. based on:
Basis for effect:
mortality (fish)
Remarks on result:
other: 95% CI 0.72 - 2.07 µg dissolved Ag/L. Fish aged 1-4 day at start of test.
Details on results:
Other LC50 values: 3.37 (7 d old), 5.9 (27 d old), 10.4 (41 d old) µg/L dissolved Ag.
Results with reference substance (positive control):
Not applicable
Reported statistics and error estimates:
Trimmed Spearman Karber analysis was used to estimate 48- and 96-h LC50s.
Validity criteria fulfilled:
not applicable
The 96 hour LC50 for fish aged 1-4 days was 1.2 µg dissolved Ag/L. Other LC50 values were: 3.37 (7 d old), 5.9 (27 d old), 10.4 (41 d old) µg dissolved Ag/L. Silver toxicity varied with age and size of P. promelas. As fish aged and mass increased, 96 hour LC50 values increased (organism sensitivity decreased).
Executive summary:

The toxicity of silver toP. promelaswas assessed in a flow through test. For fish aged 1 -4 days, the 96 hour LC50 is 1.5 µg/L dissolved Ag. Other LC50 values were: 3.37 (7 d old), 5.9 (27 d old), 10.4 (41 d old) µg dissolved Ag/L. Silver toxicity varied with age and size of fish. As fish aged and mass increased 96 h LC50 values increased (organism sensitivity decreased). The GLP status of this study is unknown and it is unclear which guideline was followed. However, there is sufficient information for an assessment to be made and the study is considered suitable for use for this endpoint.

Description of key information

The most sensitive data reported is a 96 hour LC50 of 1.2 μg Ag/L for Pimephales promelas (Bielmeyer et al. 2007).

Key value for chemical safety assessment

Fresh water fish

Fresh water fish
Dose descriptor:
Effect concentration:
1.2 µg/L

Marine water fish

Marine water fish
Dose descriptor:
Effect concentration:
331 µg/L

Additional information

The most sensitive 96-hour LC50 is reported by Bielmeyer et al. (2007) for fathead minnow. Similar LC50 values are reported by other authors (e.g. Karen et al. 1999).

Data on the toxicity of silver to marine fish are more limited. However, the data indicate that marine fish are considerably less sensitive to silver than freshwater species. The most sensitive 96-hour LC50 for marine fish is 331 μg Ag/L for Oligocottus maculosus (Shaw et al. 1988).