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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Administrative data

Endpoint:
fish, juvenile growth test
Type of information:
migrated information: read-across from supporting substance (structural analogue or surrogate)
Adequacy of study:
key study
Reliability:
2 (reliable with restrictions)

Data source

Referenceopen allclose all

Reference Type:
secondary source
Title:
Unnamed
Year:
2006
Reference Type:
publication
Title:
Effects of different ligands on the bioaccumulation and subsequen depuration of dietary Cu and Zn in juvenile rainbow trout (Oncorhynchus mykiss)
Author:
Kjoss, V.A., Wood C.M. and Mc Donald, D.G.
Year:
2006
Bibliographic source:
Canadian Journal of Fisheries and Aquatic Sciences , Vol. 63, 412-422 (2006)

Materials and methods

Test guideline
Qualifier:
no guideline followed
Principles of method if other than guideline:
Juvenile rainbow trout (Oncorhynchus mykiss) were exposed to control food or to food supplemented with different Cu (~400 µg·g–1 food) compounds. Tissue metal accumulation was compared among groups.
GLP compliance:
not specified

Test material

Constituent 1
Chemical structure
Reference substance name:
Copper oxide
EC Number:
215-269-1
EC Name:
Copper oxide
Cas Number:
1317-38-0
Molecular formula:
CuO
IUPAC Name:
copper (II) oxide
Constituent 2
Reference substance name:
CuO
IUPAC Name:
CuO
Details on test material:
CAS number: 1317-38-0
Formula: CuO

Test solutions

Details on test solutions:
Copper oxide was obtained from Aldrich Chemical Co., Milwaukee, Wisconsin, USA. Diet was processed as follows: 110 mL of deionized water with predissolved metal complex were added to 250 g of starter feed and mixed thoroughly with pasta maker. Food was then extruded in small pellets, dried at 60°C and allowed to cool to room temperature prior to being crushed into fine powder by hands.

Test organisms

Test organisms (species):
Oncorhynchus mykiss (previous name: Salmo gairdneri)
Details on test organisms:
Juvenile rainbow trout (mean weight around 200 mg) were obtained from a local trout farm.

Study design

Test type:
flow-through
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
15 d
Post exposure observation period:
15 days

Test conditions

Hardness:
140 mg/L as CaCO3
Test temperature:
12.5°C
Salinity:
Alkalinity = 95 mg/L as CaCO3

Results and discussion

Effect concentrations
Duration:
15 d
Dose descriptor:
NOEC
Effect conc.:
292 800 µg/L
Nominal / measured:
meas. (not specified)
Conc. based on:
element
Remarks:
Copper
Basis for effect:
other: residue
Details on results:
Free ionic copper is considered the active ingredient in inorganic copper salts, and is believed to be repsonsible for adverse effects. The bioavailablity of the copper ion at target sites determines the severity of effects. Both copper oxide and and copper hydroxide nitrate are considered sparingly soluble inorganic copper salts and would be expected to dissociate similarly within the organism.

Fish fed CuO showed no differences in tissue Cu concentrations relative to control fish, suggesting that Cu was not readily available for uptake in this form. In contrast, Cu in the form of CuSO4, Cu-proteinate, or Cu-lysine was much more available for uptake, resulting in substantial increases in liver, gut tissue, and whole-body Cu concentrations during the loading phase and decreases during depuration, although liver and whole-body levels remained elevated after 2 weeks. No differences in tissue Cu accumulation among these three complexes were found. There were no effects on growth.

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
Under the conditions of the test, the NOEL for Copper oxide, using a rainbow trout, was 292 800 µg Cu/L. Based on a content of 53% Copper in Basic Copper Nitrate, the fish NOEL for this substance is estimated to be 552 mg/L.