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EC number: 215-572-9 | CAS number: 1332-65-6
- 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 terrestrial plants
Administrative data
- Endpoint:
- toxicity to terrestrial plants
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Already evaluated by the Competent Authorities for Biocides and Existing Substance Regulations.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Comparison of soil solution speciation and diffusive gradients in thin-films measurement as an indicator of copper bioavailability to plants
- Author:
- Zhao F-J, C.P. Rooney, H. Zhang and S.P. McGrath
- Year:
- 2 006
- Bibliographic source:
- Environ Toxicol Chem., Vol. 25, No. 3, pp. 733-742, 2006
Materials and methods
- Principles of method if other than guideline:
- This study was designed to determine wheter the variation in toxicity effect concentrations (tomato and barley) can be explained by the solubility or speciation of Cu in soil solutions or the diffusive gradients in thinfilms (DGT) measurement.
Test material
- Reference substance name:
- CuCl2
- IUPAC Name:
- CuCl2
Constituent 1
Test organisms
open allclose all
- Species:
- Hordeum vulgare
- Plant group:
- Monocotyledonae (monocots)
- Species:
- Lycopersicon esculentum
- Plant group:
- Dicotyledonae (dicots)
Study design
- Study type:
- laboratory study
Results and discussion
Effect concentrations
- Dose descriptor:
- other: see summary
- Remarks on result:
- other: see summary
Applicant's summary and conclusion
- Conclusions:
- plant bioavailability of Cu in soil depends on Cu speciation, interactions with protective ions (H+) and the resupply from the solid phase. DGT measurement provides a useful indicator of Cu bioavailability in soil.
- Executive summary:
The toxicity effect concentrations of total added Cu derived from barley root elongation and tomato growth assays varied widely among 18 European soils. Zhao et al (2006) investigated whether this variation could be explained by the solubility or speciation of Cu in soil solutions or the diffusive gradients in thinfilms (DGT) measurement. Solubility and Cu speciation varied greatly among the soils tested. However, the EC10 and EC50 of soil solution Cu or free Cu²+ activity varied even more widely than those based on the total added Cu, indicating that solubility or soil solution speciation alone could not explain intersoil variation in Cu toxicity. Estimated EC10 and EC50 of free Cu²+ activity correlated closely and negatively with soil pH, indicating a protective effect of H+, which is consistent with the biotic ligand model concept. The DGT measurement was found to narrow the intersoil variation in EC50 considerably and to be a better predictor of plant Cu concentrations than either soil solution Cu or free Cu²+ activity. The authors conclude that plant bioavailability of Cu in soil depends on Cu speciation, interactions with protective ions (H+) and the resupply from the solid phase, and conclude that the DGT measurement provides a useful indicator of Cu bioavailability in soil.
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