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EC number: 215-582-3 | CAS number: 1333-22-8
- 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
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Genetic toxicity: in vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in bacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Experimental phase: 25 March 1994 to 12 April 1994. Report issued: 21 June 1994.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 994
- Report date:
- 1994
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.13/14 (Mutagenicity - Reverse Mutation Test Using Bacteria)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Copper sulphate
- EC Number:
- 231-847-6
- EC Name:
- Copper sulphate
- Cas Number:
- 7758-99-8
- Molecular formula:
- CuSO4.5H2O
- Test material form:
- solid: crystalline
Constituent 1
Method
- Target gene:
- Histidine
Species / strain
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98, TA 100 and TA 102
- Metabolic activation:
- with and without
- Metabolic activation system:
- Aroclor 1254-induced rat liver post-mitochondrial fraction (S9)
- Test concentrations with justification for top dose:
- Toxicity and range-finder experiment: 0, 8, 40, 200, 1000 and 5000 µg/plate (+/- S9)
Mutation experiment 1: 0, 1.6, 8, 40, 200 and 1000 µg/plate (+/- S9)
Mutation experiment 2: 0, 50, 100, 200, 400 and 800 µg/plate (+/- S9) - Vehicle / solvent:
- Sterile distilled water
Controlsopen allclose all
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- Positive controls:
- yes
- Positive control substance:
- 2-nitrofluorene
- Remarks:
- For Strain TA98
- Positive controls:
- yes
- Positive control substance:
- sodium azide
- Remarks:
- For strains TA100 and TA1535
- Positive controls:
- yes
- Positive control substance:
- 9-aminoacridine
- Remarks:
- For strain TA1537
- Positive controls:
- yes
- Positive control substance:
- other: Glutaraldehyde
- Remarks:
- For strain TA102
- Positive controls:
- yes
- Positive control substance:
- other: 2-aminoanthracene
- Remarks:
- For 1 strain with S9
- Details on test system and experimental conditions:
- METHOD OF APPLICATION:
In agar using plate incorporation for experiment 1 and preincubation for experiment 2 (preincubation used as the result of the first experiment was negative)
DURATION
- Preincubation period: 1 hour (experiment 2 only)
- Exposure duration: 72 hours
- Evaluation criteria:
- Acceptance criteria
The assay was considered valid if the following criteria were met:
i) the mean negative control counts fell within the normal ranges for the laboratory
ii) the positive control chemicals induced clear increases in revertant numbers confirming discrimination between different strains, and an active S-9 preparation
iii) no more than 5%, of the plates were lost through contamination or some other unforeseen event.
Evaluation criteria
A test compound was considered to be mutagenic if:
i) the assay was valid as per acceptance criteria above
ii) Dunnett's test gave a significant response (p ≤ 0.01), and the data set showed a significant dose-correlation
iii) the positive responses described in (ii) were reproducible. - Statistics:
- Dunnett's test
Results and discussion
Test resultsopen allclose all
- Key result
- Species / strain:
- S. typhimurium TA 98
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 102
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 1535
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 1537
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
Any other information on results incl. tables
Toxicity and dose selection
An initial range-finder experiment was carried out in strain TA100 only, using final concentrations of copper II sulphate pentahydrate at 8, 40, 200, 1000 and 5000 μg/plate. Toxicity was observed following all these treatments of 5000 μg/plate, with further evidence of toxicity (as indicated by a thinning of the background bacterial lawn and/or a marked reduction in revertant numbers) also observed fallowing treatments of 1000 μg/plate.
Due to the toxicity observed in the range-finder experiment, the maximum test dose for treatments of the remaining test strains in Experiment 1 was reduced ta 1000 μg/plate, this being an estimate of the lower limit of toxicity. Evidence of toxicity was again observed following all Experiment 1 treatments of 1000 μg/plate. Some evidence of toxicity was also observed following strain TA102 treatments of 200 μg/plate in the presence of S-9 only.
For Experiment 2 treatments, a maximum test dose of 800 μg/plate was used, this dose being a revised estimate of the lower limit of toxicity. All Experiment 2 treatments were performed utilising a narrowed dose range, in order to more closely examine those doses of copper II sulphate pentahydrate most likely to exhibit a mutagenic response. Additionally, all Experiment 2 treatments in the presence of s-9 were performed using a pre-incubation step. Evidence of toxicity (and in some cases complete toxicity) was observed fallowing all Experiment 2 treatments of 800 μg/plate. Some treatments in the presence of S9 at lower test doses also produced evidence of toxicity. The higher degree of toxicity observed with Experiment 2 treatments in the presence of S9 was attributed to the use of a pre-incubation step, which allowed an enhanced exposure of the bacteria to the test chemical.
Applicant's summary and conclusion
- Conclusions:
- It was concluded that copper II sulphate pentahydrate was unable to induce mutation in 5 strains of Salmonella typhimurium, when tested at concentrations extending into the toxic range, in both the absence and presence of a rat liver metabolic activation system (S-9).
- Executive summary:
Introduction
Copper II sulphate pentahydrate was assessed for its mutagenic potential in bacteria using the following test guidelines:
i) OECD Test Guideline 471
ii) EEC Annex V Test B14
Method
Following a range-finding experiment five histidine requiring strains (TA98, TA100, TA1535, TA1537 and TA102) of Salmonella typhimurium were treated with copper II sulphate pentahydrate at concentrations ranging between 1.6 and 1000 μg/plate both in the absence and presence of S9 metabolic activation in two separate experiments. Negative ( solvent) and positive control treatments were included for all strains in both experiments. The mean numbers of revertant colonies on negative control plates all fell within acceptable ranges, and were significantly elevated by positive control treatments.
Results
No copper II sulphate pentahydrate treatment of any of the test strains, in either the absence or presence of S9, resulted in an increase in revertant numbers that was statistically significant when analysed using Dunnett's test.
Conclusion
It was concluded that copper II sulphate pentahydrate was unable to induce mutation in five strains of Salmonella typhimurium, when tested at concentrations extending into the toxic range, in both the absence and presence of a rat liver metabolic activation system (S9).
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