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EC number: 273-769-5 | CAS number: 69012-72-2 Residue from treatment of calcined zinc ore concentrates with antimony trioxide, zinc dust, lead oxide and copper sulfate. Consists primarily of zinc and a composite of metallics: cobalt, copper and lead.
- 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 aquatic algae and cyanobacteria
Administrative data
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- other: read accross of critical study record from specific substance (CdO) driving classification
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- yes
- Remarks:
- Modified algal medium is used (composition is reported)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- see original report (no reference number)
Test material
- Reference substance name:
- Cadmium oxide
- EC Number:
- 215-146-2
- EC Name:
- Cadmium oxide
- Cas Number:
- 1306-19-0
- IUPAC Name:
- oxocadmium
- Details on test material:
- purity > 99.5%
mean diameter: 0.5 µm; rel. density: 7.95 – 8.15
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- MONITORING OF TEST SUBSTANCE CONCENTRATION: at O hours and end of the test (72h). by IPAC.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- - the three test solutions obtained from the transformation/dissolution test (LISEC) were, after filtration (0.2 µm) used as stock solutions for this test. Test solutions were prepared by appropriate dilution of the stock with the necessary nutrients (from modified OECD 201 medium with omission of EDTA) and modified ISO 6341 to obtain the test concentrations. All test solutions were spiked with 3.25 ml algal suspension. Test solutions were buffered at pH 8 by passing continuously a stream of 0.033% CO2 over the solutions.
Test organisms
- Test organisms (species):
- Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- - Strain/source: Scenedesmus subspicatus (CCAP; strain 278/4) from the Culture Collection of Algae and Protozoa, UK.
- Breeding method: according to OECD guideline.
- Age: not reported.
- Control: yes.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
Test conditions
- Details on test conditions:
- TEST SYSTEM:
- Concentration tested (total Cd): 0, 9.5; 21; 48; 104 and 223 µg Cd/L
- Renewal of test solution: no.
- Exposure vessel type: 250 ml glass flasks covered with a stop.
- Number of replicates, individuals per replicate: three replicates with test substance, three controls containing only algae and medium and one reference test vessel for each test concentration containing algal medium and the test substance.
Vessels are shaken once a day.
- Test temperature: in general: 21 – 25 °C but sometimes outside and varying by more than 2°C
- pH: 7.54 – 9.88 range in one flask per concentration and control.
- Hardness: Hc: 49mg CaCO3/L
- Intensity of irradiation: 6500 lux
Photoperiod: continuous uniform illumination.
Cell density is measured by spectrophotometry (720.0 nm) at 0, 24, 48 and 72 hours. The algal medium with test substance at the different test concentrations were used as a blank.
Results and discussion
Effect concentrations
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 18 µg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- dissolved
- Basis for effect:
- growth rate
- Details on results:
- EC50 (0-72h) for growth rate after 72h, is lower (i.e. 79 µg Cd/L, 95% confidence interval: 71-88 µg Cd/L) than the dissolved cadmium concentration measured after transformation/dissolution (185-307 µg Cd/L).
The objective of the study was to determine the effect of the test substance cadmium oxide, transformed/dissolved in buffered (pH 8) modified ISO 6431 medium during 7 days at a loading of 100 mg CdO/L, on the growth of algae.
CONTROL: growth curve conform to guideline: validity criterion was met: cell conc in the control cultures increased with a factor of 79 within 3 days - Reported statistics and error estimates:
- the concentration-effect curve fittings and EC50 were based on the model of Bruce and Versteeg (1992). SAS Procedure NLIN was used to fit the model to data
Any other information on results incl. tables
no
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- cell conc in the control cultures increased with a factor of 79 within 3 days
- Conclusions:
- Tests done according to standard protocol. Good quality and considered useful for setting the reference value for acute aquatic ecotoxicity.
- Executive summary:
Tests done according to standard protocol. Good quality and considered useful for setting the reference value for acute aquatic ecotoxicity. Study used for that purpose in the EU risk assessment process on cadmium (ECB 2008). Culture medium, test water conditions well described and relevant the purpose of setting reference value.
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