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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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
Description of key information
ABS: Vibrio fischeri Microtox: 30 min-EC50 > 80 g/L
Key value for chemical safety assessment
- EC50 for microorganisms:
- 80 g/L
- EC10 or NOEC for microorganisms:
- 80 g/L
Additional information
In two acute toxicity tests according to the Microtox procedure, undiluted, neutralized leachate of ABS (DIN 38414 -4/DEV-S4, L/S 10/1) had no effect on the bioluminescence of the marine proteobacterium, Vibrio fischeri. After 30 min of incubation there was no decrease in biofluorescence, and the EC50 is larger than 80 g/L (nominal), the highest concentration tested (BfG 2008).
In an acute toxicity test according to the Microtox procedure, undiluted, neutralized leachate of ABS (L/S 10/1) had no effect on the bioluminescence of the marine proteobacterium, Vibrio fischeri. After 30 min of incubation, there was no decrease in biofluorescence, and the NOEC was >= 90 g/L, and the EC50 was larger than 90 g/L (nominal), the highest concentration tested (LECES 1999).
Leachate of air-cooled blast furnace slag (ABS, subtype toploader kiln slag) is not inhibitory on the bioluminecence of the marine bacterium, Vibrio fischeri, in a test according to ISO 11348. The 30 min-IC0 is >= 100 mg/L (nominal, highest concentration tested), the IC50 is > 100 mg/L (Hygiene-Institut des Ruhrgebiets 2008).
This value is disregarded for assessment because the insolubility of the slag is a desired property of the slag for its use in construction. The low solubility was the reason why the experiments were ordered to be made with extrem low concentrations instead of concentrations relevant for the environment.
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