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EC number: 227-030-9 | CAS number: 5610-94-6
- 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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test (Carbon and Ammonium Oxidation))
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Vehicle:
- no
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- Municipal sewage treatment plant of 31137 Hildesheim, Germany
- Test type:
- static
- Water media type:
- other: synthetic waste water
- Remarks:
- according to OECD 209
- Limit test:
- yes
- Total exposure duration:
- 3 h
- Test temperature:
- nominal 18 - 22 °C, actually measured 19.6 °C
- pH:
- The pH value of the activated sludge was determined prior to test start. The pH value of the synthetic waste water was determined prior to use and adjustment to 7.5 +/- 0.5 was not necessary.
- Dissolved oxygen:
- After 3 h incubation, the oxygen concentration of each control, reference item and test item replicate was determined by means of oximeter every 5 seconds after transferring the solution to the measuring chamber and the oxygen depletion was recorded for at least 5 minutes with the software PreSens Measurement Studio 2.
- Details on test conditions:
- Preparation of the Test Vessels:
Based on the results of the preliminary test it was concluded that the heterotrophic respiration as well as the nitrification are not inhibited. Therefore, the definitive study was carried out with the concentration of 1000 mg a.i./L in 3 replicates (limit test to determine the NOEC). The concentration was weighed out directly in Erlenmeyer flasks and stirred overnight.
Triplicates of the control without test item were included at the beginning and at the end of the test.
The reference item was tested with three concentrations within the concentration range 58 - 180 mg/L and a dilution factor of approx. 1.8.
A fresh sample of activated sludge taken from the sewage plant Hildesheim was used for the test procedure. It was washed twice and adjusted with chlorine free tap water to a dry sludge concentration of 3.0 g/L +/- 10 %.
The oxygen uptake rates of all samples were determined following an incubation period of 3 h. - Reference substance (positive control):
- yes
- Remarks:
- Copper (II) sulphate pentahydrate p.a.
- Key result
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks on result:
- other:
- Remarks:
- based on test item concentration
- Validity criteria fulfilled:
- yes
- Conclusions:
- The NOEC of the test item is >= 1000 mg a.i./L.
- Executive summary:
A study was performed according to OECD 209 guideline and GLP principles. In the study, the test item caused no inhibiting effects on activated sludge of a municipal sewage treatment plant at the limit test item concentration of 1000 mg a.i./L.
Reference
From the oxygen depletion the oxygen uptake rates were calculated in mg O2/L * h, additionally the specific respiration rates based on the dry sludge concentration were calculated in mg O2/g * h. The inhibition of the oxygen uptake rates of the test item concentrations in % was calculated in comparison to the oxygen uptake rates of the control. The results are listed in Table 3 to Table 4.
Table 3: Oxygen Uptake Rates of the Control Replicates
Repl. | Oxygen Concentration* [mg/O2/L] | Oxygen Uptake Rate R [mg O2/(L x h)] | Specific Respiration Rate Rs [mg O2/gxh] | |
1 2 3 4 5 6 |
7.18 7.24 7.44 7.19 7.52 7.17 |
27.0 29.3 29.3 32.7 34.0 33.9 |
18.6 20.2 20.2 22.6 23.4 23.4 |
|
Mean value | 31.0 | 21.4 | ||
Standard deviation | 2.65 | |||
CV [%] | 8.55 |
*) determined at start of the measurement
Repl. = Replicate
CV = Coefficient of variation
Table 4: Oxygen Uptake Rates and Inhibition of the Respiration of the Test Item Concentration
Test item Concentration [mg a.i./L] | Repl. | Oxygen Concentration* [mg O2/L] | Oxygen Uptake Rate R [mg O2/(Lxh)] | Inhibition [%] | Mean Inhibition [%] |
1000 | 1 2 3 |
5.59 6.19 5.19 |
30.8 30.7 30.5 |
1 1 2 |
1 |
*) determined at start of the measurement
Repl. = Replicate
In the reference test the EC50 value for copper (II) sulphate pentahydrate was determined with EC50 = 105 mg/L, 95 % Confidence Interval = 99.1 - 111 mg/L. This is the recommended range of validity of 53 - 155 mg/L.
Description of key information
A study was performed according to OECD 209 guideline and GLP principles. In the study, the test item caused no inhibiting effects on activated sludge of a municipal sewage treatment plant at the limit test item concentration of 1000 mg a.i./L.
Key value for chemical safety assessment
Additional information
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