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EC number: 948-085-1 | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Short-term toxicity to fish
Administrative data
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 07.Ag.2008 - 04.Apr. 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- OECD Guideline for the Testing of Chemicals, No. 203, Fish, Acute Toxicity Test, 1992.
- Qualifier:
- according to guideline
- Guideline:
- other: Directive 92/69/EEC
- Version / remarks:
- EU Commission Directive 92/69/EEC, C.1: Acute Toxicity for Fish, 1992.
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Copper di-D-gluconate
- EC Number:
- 208-408-2
- EC Name:
- Copper di-D-gluconate
- Cas Number:
- 527-09-3
- Molecular formula:
- C12H22CuO14
- IUPAC Name:
- copper(2+) bis(2,3,4,5,6-pentahydroxyhexanoate)
- Reference substance name:
- Sodium sulphate
- EC Number:
- 231-820-9
- EC Name:
- Sodium sulphate
- Cas Number:
- 7757-82-6
- Molecular formula:
- H2O4S.2Na
- IUPAC Name:
- disodium sulfate
- Reference substance name:
- Copper sulphate
- EC Number:
- 231-847-6
- EC Name:
- Copper sulphate
- Cas Number:
- 7758-98-7
- Molecular formula:
- CuSO4
- IUPAC Name:
- copper(2+) ion sulfate
- Test material form:
- liquid
Constituent 1
Constituent 2
Constituent 3
Sampling and analysis
- Analytical monitoring:
- not specified
- Details on sampling:
- Dosage
A concentrated stock solution of nominal 500 mg/L was daily prepared by completely dissolving test item in test water using ultrasonic treatment for 10 minutes and stirring for 10 minutes at room temperature. The following test item amounts were weighed into the test water:
Weighed amount of test item (mg) Amount of test water (mL)
2251.2 4500
750.3 1500
99.9 200
99.8 200
Adequate volumes of this intensively stirred stock solution were added to the test water in the test vessels and were intensively mixed to prepare the test media with the test concentrations as stated above.
The test media were daily freshly prepared just before introduction of the fish (= start of the test) and before each test medium renewal.
Test solutions
- Vehicle:
- not specified
- Details on test solutions:
- Study Design
The following nominal concentrations of Sergomil L60 were tested: 0.32, 1.0, 3.2, 10, 32 and 100 mg/L. Additionally, a control (test water without test item) was tested in parallel.
A semi-static test procedure was chosen. The test media were renewed daily to keep the concentrations of Sergomil L60 in the test media as constant as possible during the test period of 96 hours.
During this semi-static test, the test fish were daily placed into a new test vessel with freshly prepared test medium of the corresponding treatment.
The selection of the test concentrations was based on the results of a range-finding test (non- GLP).
At the start of the test, 7 fish were introduced into each test vessel in a random order. The loading rate was 0.64 g fish wet weight per liter test medium. Thus, the requirement of a loading rate of less than 1 g fish/L was fulfilled.
Test organisms
- Test organisms (species):
- Oncorhynchus mykiss (previous name: Salmo gairdneri)
- Details on test organisms:
- TEST ORGANISM
- Common name: rainbow trout
- Strain: Oncorhynchus mykiss
- Source:
- Age at study initiation (mean and range, SD): juvenile
- Length at study initiation (length definition, mean, range and SD):
- Weight at study initiation (mean and range, SD):
- Method of breeding:
- Maintenance of the brood fish:
ACCLIMATION
- Acclimation period:
- Acclimation conditions (same as test or not):
- Type and amount of food during acclimation:
- Feeding frequency during acclimation:
- Health during acclimation (any mortality observed):
QUARANTINE (wild caught)
- Duration:
- Health/mortality:
FEEDING DURING TEST
- Food type:
- Amount:
- Frequency:
Study design
- Test type:
- semi-static
- Water media type:
- other: Local tap water (non chlorinated well water of drinking water quality)
- Total exposure duration:
- 96 h
Test conditions
- Hardness:
- The total hardness of the test water was 214 mg/L as CaCO3.
- Test temperature:
- The water temperature in the test vessels was maintained at 14-15 °C (Table 5).
- pH:
- The pH values in the test media and the control ranged from 8.0 to 8.4 (Table 3).
- Dissolved oxygen:
- The oxygen concentration was always 9.1 mg/L or higher (Table 4), and thus higher than 60% oxygen saturation.
- Salinity:
- Not specify
- Conductivity:
- Not specify
- Nominal and measured concentrations:
- The nominal test item concentrations tested were 0.32, 1.0, 3.2, 10, 32 and 100 mg/L. Additionally, a control group was tested in parallel.
- Details on test conditions:
- Experimental Conditions
The water temperature in the test vessels was maintained at 14-15 °C (Table 5). The test vessels were slightly aerated during the test period.
A 16-hour light to 8-hour dark photoperiod, with a 30-minute transition period was used (light intensity during the light period was approximately within the range of 100 to 600 Lux).
The test duration was 96 hours and the fish were not fed during the test. - Reference substance (positive control):
- not specified
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- not specified
- Basis for effect:
- not specified
- Duration:
- 96 h
- Dose descriptor:
- LC0
- Effect conc.:
- 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- not specified
- Basis for effect:
- not specified
- Duration:
- 96 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- not specified
- Basis for effect:
- not specified
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Remarks:
- 95% confidence interval of 1.0-3.2 mg/L.
- Effect conc.:
- 1.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- not specified
- Basis for effect:
- not specified
- Duration:
- 96 h
- Dose descriptor:
- LC100
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- not specified
- Basis for effect:
- not specified
- Details on results:
- RESULTS AND DISCUSSION
No analytical work was performed in agreement with the Sponsor. The reported biological results were based on the nominal concentrations of the test item.
The biological results (observations for visible abnormalities in the test fish, mortalities and the LC50 values) are listed in Table 1. In the control and at the test concentrations up to and including 1.0 mg/L, all fish survived until the end of the test and no visible abnormalities were observed in the test fish. At all higher test concentrations, all fish were dead already after 24 to 48 hours of test duration.
Thus, the 96-hour NOEC and the 96-hour LC0 of test item to rainbow trout were both determined to be 1.0 mg/L. The 96-hour LOEC was 3.2 mg/L.
The 96-hour LC50 of test item was calculated to be 1.8 mg/L with a 95% confidence interval of 1.0-3.2 mg/L. The 96-hour LC100 was 3.2 mg/L. Thus, the concentration-effect relationship of the test item was rather steep.
No remarkable observations were made concerning the appearance of the test media. All test media were clear solutions colored by the test item at the highest test concentration of 100 mg/L throughout the entire test duration (Table 2).
The pH values in the test media and the control ranged from 8.0 to 8.4 (Table 3). The oxygen concentration was always 9.1 mg/L or higher (Table 4), and thus higher than 60% oxygen saturation. The water temperature was 14-15 °C during the test (Table 5). - Results with reference substance (positive control):
- The biological test results after 96 hours of test duration:
– 96-hour LC50: 1.8 mg/L
(95% confidence interval: 1.0-3.2 mg/L)
– 96-hour LC0: 1.0 mg/L
– 96-hour LC100: 3.2 mg/L
– 96-hour NOEC: 1.0 mg/L
– 96-hour LOEC: 3.2 mg/L
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Substance presents no acute toxicity for fish in 96h.
- Executive summary:
The acute toxicity of the test item to rainbow trout (Oncorhynchus mykiss) was determined in a 96-hour semi-static test with a daily test medium renewal according to the EU Commission Directive 92/69/EEC, Part C.1 and the OECD Guideline for Testing of Chemicals No. 203, (1992).
The nominal test item concentrations tested were 0.32, 1.0, 3.2, 10, 32 and 100 mg/L. Additionally, a control group was tested in parallel.
No analytical work was performed in agreement with the Sponsor. The reported biological results were based on the nominal concentrations of the test item.
The biological test results after 96 hours of test duration:
– 96-hour LC50: 1.8 mg/L
(95% confidence interval: 1.0-3.2 mg/L)
– 96-hour LC0: 1.0 mg/L
– 96-hour LC100: 3.2 mg/L
– 96-hour NOEC: 1.0 mg/L
– 96-hour LOEC: 3.2 mg/L
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