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Diss Factsheets
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EC number: 701-480-0 | 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
Repeated dose toxicity: inhalation
Administrative data
- Endpoint:
- sub-chronic toxicity: inhalation
- Remarks:
- other: calculation based on classification
- Type of information:
- calculation (if not (Q)SAR)
- Remarks:
- Migrated phrase: estimated by calculation
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Automatic calculation with MeClas tool
Cross-reference
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- other: software
- Title:
- Unnamed
- Year:
- 2 019
Materials and methods
- Principles of method if other than guideline:
- The potential of the UVCB substance to cause specific target organ toxicity following repeated exposure by oral route was established by classifying the complex metal substance according to rules for classification of mixtures for STOT RE (EU CLP guidance section 3.9.3 pg 382ff). The classification criteria (as set out in EU CLP Annex I: 3.9.3.4.1.) can be used to estimate effects derived from that classification/hazard.
Test material
- Reference substance name:
- Iron silicate, copper smelting and refining
- EC Number:
- 701-480-0
- Cas Number:
- 67711-92-6
- IUPAC Name:
- Iron silicate, copper smelting and refining
- Details on test material:
- Typical across industry as defined in IUCLID 1.2;
See IUCLID Section 1.4, for company specific elemental composition; and representative sample for mineralogical information (IUCLID Section 4.23 -Outotec report)
Constituent 1
Administration / exposure
- Route of administration:
- inhalation: dust
- Duration of treatment / exposure:
- 90 days
Results and discussion
Effect levels
- Dose descriptor:
- conc. level:
- Effect level:
- > 2 mg/L air (nominal)
- Based on:
- dissolved
- Remarks on result:
- not measured/tested
- Remarks:
- calculated
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
The calculated classification via rules for mixtures (Lower Tier) resulted in “STOT repeated : Category 2 ”triggered by Pb compounds at actual levels above 0,5%.
Consideration of reduced bio-accessibility of Pb (Higher Tier) resulted in” STOT repeated :: Not classified”
Based on this result, the related criteria provided theestimated dose/concentration value at or below which nosignificant toxic effects would be observed in a 90-day repeated-dose studyby inhalation route (see EU CLP Guidance Annex IAnnex 3.9.2.9.7,Table 3.9.3) : Inhalation rat dust/mist/fume , dose /concentration >2 mg/litre/6h/day
For more details, see "Human Health classification of C1 copper slag", attachment in Section7 "Summary record Toxicological information”
Applicant's summary and conclusion
- Conclusions:
- Study can be used to predict the single organ toxicity effect by inhalation route and to determine hazard/classification of the UVCB substance
- Executive summary:
The study provided a conservative estimate of the Single organ toxicity effect, derived on basis of the Classification outcome by applying the rules for mixtures of a Typical (across industry) copper slag.
Chemistry of the substance (see IUCLID section 4.23 chemical and mineralogical characterization) shows that copper slag does contain only minor constituents classified as a STOT RE Cat 1 (Ni compounds) at actual levels max 0.21 % (in representative samples and maximum levels across industry. It can be also demonstrated that copper slag contains minor constituents classified as STOT RE Cat 2 ( ex.Pb compounds) above 0.5% which trigger classification.
Copper slag stones do not contain inhalable fraction (particles less than 100 μm) .Copper slag granules do contain small inhalable fraction between 1.4 and 15% but do not contain particles smaller than 20 μm.Copper slag powders contain 100% inhalable fraction (particles less than 100 μm), which is capable of entering the respiratory tract under realistic breathing conditions. Further particles smaller than 20 μm present (16 to 40%), which constitute the “thoracic” fraction and are capable of penetrating to the trachea bronchial regions of the lung or deeper.
Therefore inhalation route is relevant for copper slag due to possibility of exposure to particles of an inhalable size.
Lead particles have systemic mode of action so resorption of dissolved lead particles can take place from deposition locations in the entire respiratory tract and contribute to systemic toxicity.
An acute inhalation toxicity study conducted with lead oxide powder (MMAD= 5.8µm)showed that deep lung penetration would be minimal and upper respiratory tract deposition would predominate ( Ref, Lead voluntary risk assessment)/ Upper respiratory tract deposition would in turn be followed by clearance to the gastrointestinal tract. Pulmonary deposition modelling further showed that deposition patterns for all thirteen lead compounds modeled will be rather similar. No signs of any respiratory irritation or any other clinical observations.
Thus, systemic lead uptake from slag is predicted to be similar to that for lead oxide.
Finally, a conservative assumption is made that all lead containing particles in the slag will deposit in the upper airways, such particles will than enter thegastrointestinal tract,where further uptake of all dissolved particles will take place.
In vitro measurements of bio-accessibility in solvent that resembles gastric fluid performed according to ASTM D5517.07.(pH 1.5) Results demonstrate low relative bio-accesabilty of metals(Cu 0.06 – 0.2, Ni 0.09 – 0.33) and medium bioaccesability of Pb (0.13 – 0.74)
The measurements allowed to demonstrate that the maximum level of bio-accessible Pb in copper slag is below 0.5% (based on worst case release rate per different sample type)
Based on the above it is concluded that slag, copper smelting does not need classification for STOT repeated exposure by inhalation route. Therefore estimated dose/concentration value at or below which no significant toxic effects would be observed in a 90-day repeated-dose studyis : Inhalation rat dust/mist/fume dose/concentration >2 mg/litre/6h/day
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