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EC number: 701-372-3 | 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 979
- Report date:
- 1979
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 980
- Report date:
- 1980
- Reference Type:
- other: expert judgement
- Title:
- Unnamed
- Year:
- 1 980
- Report date:
- 1980
Materials and methods
- Objective of study:
- distribution
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- The study examined, whether or not systemic absorption of copper occured after 90-day high dose feed exposure to the test material. Copper analyses were conducted in livers and kidneys of the animals.
- GLP compliance:
- no
Test material
- Test material form:
- solid: particulate/powder
- Details on test material:
- - Name of test material (as cited in study report): Phthalocyanine Blue
- Analytical purity: 99.55 %
- Storage condition of test material: room temperature
Constituent 1
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): Pigment Blue 15B
- Analytical purity: The chemical analysis, performed at Midwest Research Institute indicated that the purity was 104.7 % +- 1.1 % (elemental analysis)
- Elemental analysis indicated that the compound contained less than 0.01 % chlorine. - Radiolabelling:
- no
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Industries
- Weight at study initiation: males: 70 - 105 g; females: 70 - 100 g
- Housing: polycarbonate cages: groups of 5 rats per cage
- Diet: weighed portions of Purina Lab Chow in meal form, mixed together with weighed portions of the test material (see details at "doses/concentrations")
- Water: ad libitum
- Acclimation period: 15 days
ENVIRONMENTAL CONDITIONS
- Temperature: 21 - 23 °C
- Humidity: 40 - 60 %
- Air changes: at least 15 per hour
- Photoperiod: 12 hrs dark / 12 hrs light
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- other: 12 % water was added to the test material as a dust control agent
- Duration and frequency of treatment / exposure:
- 90 days
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0.3 other: % in the diet
- Dose / conc.:
- 0.6 other: % in the diet
- Dose / conc.:
- 1.25 other: % in the diet
- Dose / conc.:
- 2.5 other: % in the diet
- Dose / conc.:
- 5 other: % in the diet
- No. of animals per sex per dose / concentration:
- 10 males per dose and 10 females per dose
- Control animals:
- yes, plain diet
- Details on study design:
- The concentrations of the chemical mixture were the same for male and female rats. All dose levels were prepared on a weight per weight basis. There were 5 dose level groups with 10 individuals of each sex in each dosage and control group. Each dosed group received 90 consecutive days of dosed feed mixture. After one day of observation, the animals were necropsied. Animals were observed twice each day for clinical signs, with at least 6 hours between observations. All observations were recorded daily. Additionally, blood sampling was conducted from 10 control rats, 6 males and 4 females.
Copper analyses were completed in the liver and kidney tissues and the formalin preserving those tissues from male rats in the highest dose group (5 % w/w) and control groups:
- Tissue samples were prepared for analysis by digesting in 10 ml of concentrated nitric acid until most of the organic material was destroyed. Perchloric acid was then added and the solutions were evaporated to strong fumes, additional nitric acid being added as required. The solutions were then fumed to dryness, the residues were dissolved in 5 % nitric acid and the solutions were diluted to 10 ml.
- Formalin samples were filtered through a Millex-GS 0.22 µm filter unit and 5 ml portions of each sample were prepared for analysis by the procedure used to prepare the tissue samples.
- The samples were then subjected to atomic absorption spectrophotometry to determine copper content:
A Perkin-Elmer Model 5000 atomic absorption spectrophotometer was utilized for the work. A series of 10 ml standard solutions, ranging from 0.05 to 2.0 ppm were prepared in 5 % nitric acid by dilution of a certified standard copper stock solution. These solutions were used to calibrate the instrument, which was programmed to print out data as total microgramms of copper per sample. The prepared sample solutions were used in the same manner as the standards. Concentrations of copper in the tissue samples were calculated by dividing the total microgramms found by the weight of the sample. Concentrations of copper in the formalin samples were calculated on a volume basis. - Details on dosing and sampling:
- PHARMACOKINETIC STUDY (distribution)
- Tissues and body fluids sampled: liver and kidneys - Statistics:
- Student´s T-test (alpha = 0.05) was used to compare the highest dose group results with control results.
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- Considering the lack of accumulation of copper in kidney and liver, no absorption has taken place.
- Details on distribution in tissues:
- Copper content of liver: 2.82 ppm +- 0.34 ppm (Test group) and 2.78 ppm +- 0.51 ppm (control group)
Content of kidney: 5.62 ppm +- 0.49 ppm (Test group) and 5.30 ppm +- 0.83 ppm (control group)
From all the formalin analyses performed, the authors drawed the conclusion that no detectable levels of copper were leached from the preserved tissue into the formalin bath.
Metabolite characterisation studies
- Metabolites identified:
- not measured
- Details on metabolites:
- No data given.
Any other information on results incl. tables
Table 1: Copper determinations in tissues and formalin of male rats from the subchronic study, treated with the test material for 90 days
male animal # |
ppm copper |
|
||
|
liver |
kidney |
formalin |
remark |
highest dose group (5 % w/w) |
|
|
|
|
1 |
4.6 - 4.3* |
8.4 |
0.1 |
* results of 2 analyses |
2 |
5.9 |
12.3 |
0.1 |
|
3 |
4.1 - 4.4* |
8.6 - 10.1* |
0.1 |
* results of 2 analyses |
4 |
6.4 |
7.7 |
0.1 |
|
5 |
3.2 |
6.7 |
0.1 |
|
6 |
3.5 |
5.8 |
0.1 |
|
7 |
3.7 |
8.1 |
0.1 |
|
8 |
3.5 - 4.1 |
8.1 |
0.1 |
|
9 |
3.1 |
8.7 - 8.6* |
0.1 |
* results of 2 analyses |
10 |
4.6 - 4.5 |
7.2 |
0.1 |
|
control |
|
|
|
|
1 |
3.1 |
3.7 - 4.0* |
0.1 |
* results of 2 analyses |
2 |
3.3 |
4.1 |
0.1 |
|
3 |
3.2 |
4.9 - 4.6* |
0.1 |
* results of 2 analyses |
4 |
3.7 - 4.0* |
5.1 |
0.1 |
* results of 2 analyses |
5 |
3.0 |
4.1 |
0.1 |
|
6 |
2.8 |
5.4 |
0.1 |
|
7 |
2.9 |
2.9 - 3.4* |
0.1 |
* results of 2 analyses |
8 |
2.6 |
5.5 |
0.1 |
|
9 |
2.6 |
5.4 |
0.1 |
|
10 |
3.3 - 3.6* |
5.4 |
0.1 |
* results of 2 analyses |
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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