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EC number: 266-002-0 | CAS number: 65996-69-2 The fused substance formed by the action of a flux upon the gangue of the iron-bearing materials charged to a blast furnace and upon the oxidized impurities in the iron produced. Depending upon the particular blast furnace operation, the slag is composed primarily of sulfur and oxides of aluminum, calcium, magnesium, and silicon.
- 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: oral
Administrative data
- Endpoint:
- sub-chronic toxicity: oral
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- a short-term toxicity study by the oral route does not need to be conducted because an appropriate inhalation study is available and inhalation is the most appropriate route of administration as based on the provided thorough and rigorous exposure assessment
- Justification for type of information:
- JUSTIFICATION FOR DATA WAIVING
-
Repeated dose toxicity study with GGBS (ground granulated blast furnace slag) has been done for inhalation because this is the likely route of human exposure.
GGBS is considered to cover the worst case of slags, ferrous metal and blast furnace as GGBS has the finest particulates, and the marketed products of other slags only contain far smaller proportions of fine particles. GGBS is produced with the highest production volume and is broadly available in the market, also freely accessible for consumers.
In a key study concerning inhalation (Charles River Laboratories, 2015) data suggests that there is no likely acute inhalation hazard due to repeated exposure of rats to GGBS for 4 weeks up to 24 µg/L. There were no deaths or adverse clinical signs during the study period and no evidence of lung injury was seen. Minimal to mild changes noted in BAL (Bronchoalveolar lavage) fluid indicative of macrophage-mediated particle clearance and unspecific findings in the lung reflect the time-dependent physiological response of the body to inhaled mineral particulates of low solubility. There was a trend towards reversibility following a 13 weeks recovery period. At 24 µg/L the histopathological changes in the lung resembled pulmonary macrophage clearance, suggesting that the inhaled particulate is processed by alveolar macrophages and mononuclear inflammatory cells at high level concentration. Based on the results of this study, the No Adverse Effect Level (NOAEL) was determined to be 24 μg/L (target concentration) or 24.9 μg/L (achieved concentration).
In another acute inhalation toxicity study in rats by GGBS conducted by Bayer Healthcare 2012, concentration- and time-related onset of lung changes were monitored up to 90 days after a single short-term exposure to GGBS. The findings showed no likely acute inhalation hazard due to aerosolized GGBS.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to other study
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Reason / purpose for cross-reference:
- assessment report
Reference
- Endpoint:
- sub-chronic toxicity: inhalation
- Remarks:
- Expert Toxicological Opninion IASON 2018
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- a sub-chronic toxicity study (90 days) does not need to be conducted because the substance is unreactive, insoluble and not inhalable and there is no evidence of absorption and no evidence of toxicity in a 28-day 'limit test' and human exposure is limited
- Justification for type of information:
- A sub-chronic toxicity study (90 days) for inhalation does not need to be conducted because the substance (slags) is unreactive, insoluble and not inhalable and there is no evidence of absorption and no evidence of toxicity in a 28 day short-term study and human exposure is limited. See executive summary and conclusion.
- Reason / purpose for cross-reference:
- reference to other study
- Conclusions:
- A sub-chronic toxicity study (90 days) for inhalation does not need to be conducted because the substance (slags) is unreactive, insoluble and not inhalable and there is no evidence of absorption and no evidence of toxicity in a 28 day short-term study and human exposure is limited. There is no need to perform additional animal studies because ferrous slags behave toxicologically similar as natural mineral samples; no further action is required.
- Executive summary:
Ferrous slags are solid UVCB substances (substances of Unknown or Variable composition, Complex reaction products or Biological materials) that resemble natural rocks found in terrestrial and sediment systems. The physicochemical properties are almost identical among ferrous slags, and their benign toxicological and ecotoxicological profiles are very similar. Similarities comprise also the mineralogical composition of the ferrous slags. Importantly, all mineral components of ferrous slags are present in natural rocks; no new component is introduced during steel processing. Ferrous slags demonstrate low extractability in water as metals in slag were found to be generally resistant to leaching. Ferrous slags are virtually free of hazardous fibres. Overall, ferrous slags can be considered artificial volcanic rocks.
The ‘Ferrous Slag Category’ comprises the following 5 slag types: (1) ABS/GBS i.e., Slag, ferrous metal, blast furnace (air cooled or granulated), (2) BOS i.e., Slag, steelmaking, converter (converter slag), (3) EAF C i.e., Slag, steelmaking, elec. furnace (carbon steel production), (4) EAF S i.e., Slag, steelmaking, elec. furnace (stainless/high alloy steel production), and (5) SMS i.e., Slag, steelmaking. No significant hazard to environmental and ecological receptors has been anticipated for these slags.
The pathways of exposure quantitatively evaluated in this assessment were inhalation of suspended airborne ferrous slag particulates, incidental ingestion of ferrous slag, and dermal contact with ferrous slag.
From single-dose toxicity testing in animals via the oral, dermal and inhalation routes it can be concluded that ferrous slags are not acutely toxic. They do not need to be classified as oral, dermal and inhalation toxicants; neither a signal word nor hazard statement is required. Furthermore, ferrous slags exhibit no relevant irritant or sensitising potential, and does not show any mutagenic potential. Extensive testing in rat inhalation studies revealed that the biological responses to inhaled ferrous slag show no correlation to the course of pulmonary toxicity reported for amorphous silica (quartz); quartz dust served as positive control as it is well known to produce irreversible lung damage. Overall, ferrous slag in vivo data differ markedly from those reported for quartz in rats exposed at similar doses.
Supplemental in vitro testing also shows that ferrous slags, alike natural mineral samples, do not cause significant toxicity in cultured alveolar macrophages, nor does the slags induce major reactive oxygen species (ROS) formation and oxidative stress or trigger any inflammation in a biological system. On the contrary, the positive assay control quartz caused consistently evidence for an inflammation response in vitro associated with a significant secretion of the mature forms of pro-inflammatory cytokines from the cells, strong activation of the inflammasome pathway, and impaired phagocytosis functionality of alveolar macrophages.
Taken together the data generated in vivo and in vitro for ferrous slags it can be summarised that ferrous slags behave like natural rock, representing a rather inert category of UVCB substances. As expected biokinetics investigations in rats following inhalation exposure to high concentrations of ferrous slag particulates showed concentration-dependent lung burdens of persistent metals after inhalation exposure of rats to ferrous slags but there was no translocation to other organs of any metal investigated. The animal data suggest that the rat lung was able to get rid of the inhaled solid aerosol via physiological clearance mechanisms.
The toxicology programme for ferrous slags, as documented in the Chemical Safety Report (CSR) as part of the registration dossier of ferrous slags (CSR 2017), can be considered to fulfil information requirements for REACH (Registration, Evaluation, Authorisation and Restriction of Chemical substances) registration at the European Chemicals Agency (ECHA). There is sufficient, adequate and reliable information on hazardous properties for classification and risk assessment of ferrous slags.
The registrant makes use of Annex XI criteria regarding the scientific necessity of information, the technical possibility for testing, and exposure-based waiving to adapt the standard information requirements under REACH. These non-clinical studies are waived based on physico-chemical properties of ferrous slags that resemble natural rocks, mimicking the natural concentration of an element in the environment, and the low solubility in water, low extractability of components from ferrous slags, and lack of toxicological bioavailable fraction / systemic bioavailability of metals. Slag has been utilised in road construction for more than two centuries and wealth of humane experiences are available. Furthermore, ferrous slags have no PBT (persistent, bioaccumulative and toxic) or vPvB (very persistent and very bioaccumulative) properties. It is also of note that no toxicity effects of particular concern were observed in animal inhalation studies that is the likely route of human exposure, and results obtained from suitable in vitro studies demonstrate no certain dangerous property of ferrous slags. Finally, previous risk assessments of slags provide sufficient supporting evidence that toxicity can reliably be excluded.
Data source
Materials and methods
Results and discussion
Applicant's summary and conclusion
- Conclusions:
- A short term-toxicity study by the oral route does not need to be conducted because an appropriate inhalation study is available and inhalation is the most appropriate route of administration as based on the expected uses, exposure assessment and the chemical- and physico properties of the slags.
The inhalation studies are showing no likely toxicity on inhalation; therefore, no oral toxicity is expected. Additional measurements are not recommended for reasons of animal welfare.
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.
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