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EC number: 294-409-3 | CAS number: 91722-09-7 Substance formed during processing of liquid steel or during production of iron castings. Consists primarily of fused silicates and trace elements as oxides as well as trace of alloying elements.
- 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 soil microorganisms
Administrative data
Link to relevant study record(s)
Description of key information
Ferrous slags are not inhibitory to key metabolic activities of soil microorganisms.
Key value for chemical safety assessment
- Long-term EC10 or NOEC for soil microorganisms:
- 10 000 mg/kg soil dw
Additional information
It was shown by laboratory and field studies that ferrous slags are not inhibitory to key metabolic activities of soil microorganisms i.e. respiration. Nitrogen metabolism and cellulose degradation were also shown not to be inhibited, but even slightly activated.
Laboratory guideline study
To test the effects of slags, ferrous metal, blast furnace (air-cooled – ABS) on the soil microflora as an indicator for conservation of soil fertility, the metabolic activity of microbial biomass and its nitrogen conversion potential were determined. The tests were performed according to C.22 (Soil Microorganisms: Carbon Transformation Test)(identical to OECD-Guideline No. 217) and C.21 (Soil Microorganisms: Nitrogen Transformation Test) of the EU-Regulation440/2008 (identical to OECD-Guideline 216). The metabolic activity of the microbial biomass was influenced only temporarily by the slag in the acclimatisation phase. The respiratory activity (carbon transformation test) in the soil mixtures treated with 10 g test item / kg of soil (dry matter) was negatively affected only at the start of the incubation period t0 (28% reduction). At the later time points, the differences between slag-incubated and control soils were less than ± 25 %. After 28 d, the microbial respiration of the soil was slightly increased in the treatment with 10 g/kg soil dry matter in comparison to the controls.
The nitrogen conversion (ammonification and nitrification) of lucerne meal (alfalfa) which was added to the soil, was not negatively influenced by the slags applied at a dose of 10 g / kg (dry matter). In general, the deviations of the NO3-- and NO2--nitrogen values of the treated samples from the untreated ones were <25%. In regard to nitrogen metabolism, ABS served as a fertilizer.
Slags, ferrous metal, blast furnace (air-cooled – ABS) had no relevant effect on the activity of the soil microflora even in the highest concentration tested (10 g/kg) for 28 d (SGS 2010).
Extended laboratory study
To evaluate the effects of steelmaking slags (SMS) on soil microorganisms, in laboratory experiments SMS was added to oxisol soil at concentrations of up to 21.2 t/ha. The pH varied between 4.8 (controls) and 7.4 (SMS, 21.2 t/ha, no pH controls done). Dry matter production, pH and metal uptake into Sorghum bicolor plants raised in parallel experiments in pot were plotted against each other and a correlation analysis was performed.
The dry matter production of Sorghum bicolor was highest when the concentration of SMS added to oxisol was approximately 9.6 t/ha. Uptake of Ca, Mg, Fe, Mn and Zn shows a flat maximum at 7 -10 t/ha in regard to the concentration of slag in the oxisol (controls not reported). The uptake of Cu was independent of the slag concentration whereas the Ni content was low but increased with increasing concentration of slag in the range tested, and in parallel to the pH.
Minimum of microbial respiration occured at a SMS concentration of approximately 10 t/ha. This minimum is explained by the authors by pH controlled availability of metal ions. Although this hypothesis cannot be verified, it is apparent that the inhibition of microbial respiration is not caused by high slag concentration in the soil, as the microbial respiration recovered at the highest slag concentration tested (Costa et al. 1992).
Field studies
To assess the applicability of slags as agricultural fertilizers in regard to soil microorganims, agricultural research done at the Sommerland Agricultural Research Station was reviewed. The metabolic potential of soil microorganisms had been measured as respiration rate and cellulose degradation with the ferrous slags ABS
(slags, ferrous metal, blast furnace, air-cooled) and BOS (slags, steelmaking, converter).
The agricultural yields was highest in slag treated fields (approximately 5 % above controls), The soil respiration in controls was 420 mg CO2/kg soil. It was highest in lime-treated fields (580 mg CO2/kg soil), and 490 and 550 mg CO2/kg soil in ABS- and BOS-treated fields, respectively. Microbial cellulose degradation was lowest in control soils (1.4 mg/cm2) and highest in the slags: ABS 2 mg/cm2, and BOS 2.3 mg/cm2.
The ferrous slags ABS (slags, ferrous metal, blast furnace, air-cooled) and BOS (slags, steelmaking, converter) did not inhibit the microbial respiration and cellulose degradation potential of soils.
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