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Diss Factsheets
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EC number: - | 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
Toxicity to soil macroorganisms except arthropods
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to soil macroorganisms except arthropods: short-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2006
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study without detailed documentation
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 207 (Earthworm, Acute Toxicity Tests)
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
not reported - Analytical monitoring:
- not required
- Details on sampling:
- weighted before start of experiment
- Vehicle:
- no
- Details on preparation and application of test substrate:
- The sample was prepared as a leachate with L/S 4/1 (1000 ml of deionized sterile water to 250g of solid material) by shaking at 30 rpm for 20 h, followed by decantation for 1h in order to obtain a concentration of 100 %.
The 100 % stock solution was mixed with soil equivalent to 100 % solution to obtain the following final test concentrations: 2.08 %, 4.16 %, 8.33 %, 16.66 % and 33.33 % L/kg. The soil (in total 750 g) was placed in 2 L plastic flasks. - Test organisms (species):
- Eisenia fetida
- Animal group:
- annelids
- Details on test organisms:
- Each 10 healthy annelids were given in each test containers and acclimatised in humid soil under test temperature and photoperiod conditions for 24 h.
- Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- no
- Total exposure duration:
- 14 d
- Post exposure observation period:
- not required
- Test temperature:
- According to OECD guideline 207
- pH:
- presumably basic
- Details on test conditions:
- Four replicates were made for each treatment. Mortality, mobility and any other irregularities were evaluated after 7 and 14 d after the beginning of the incubation.
- Nominal and measured concentrations:
- nominal
- Reference substance (positive control):
- not specified
- Duration:
- 14 d
- Dose descriptor:
- LC50
- Effect conc.:
- ca. 83 other: g/kg soil
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: mortality and behaviour
- Results with reference substance (positive control):
- Positive control not reported but GLP and comparison with crushed natural stone (LC50 83g/kg soil)
- Reported statistics and error estimates:
- Fisher´s Exact Proof
- Validity criteria fulfilled:
- yes
- Conclusions:
- SMS: OECD 207, Eisenia fetida: 14 d-LC50 approximately 83 g/kg/soil (not neutralized, nominal)
- Executive summary:
To check the toxicity of slags to earthworms, slags, steelmaking (SMS) were tested on the annelid Eisenia fetida according to OECD TG 207. Tests were performed using a L/S (liquid/solid) of 4/1 leachate (0.25 kg of slag/L of leaching medium). The leachates were neither neutralized nor filtered. The leachates were mixed with artifical soil to obtain 5 concentrations 2.08 %, 4.16 %, 8.33 %, 16.66 % and 33.33 % L/kg soil.
Basic leachates of SMS are not toxic to Eisenia fetida in an acute earth worm test according to OECD TG 207. The 14 d-LC50 is approximately 83 g/L (nominal).
As verms tolerate only a limited pH range, these experiments indicate some pH influence. However, the results confirm that slags exert no acute toxicity to earthworms.
Reference
Description of key information
Aquatic toxicity studies are not available for Slag, pig iron ladle refining, non-granulated, water-cooled. Read-across to the assessment entity (analogue approach) to slags, steelmaking is applied for the assessment of Slag, Pig Iron ladle refining, non-granulated, water-cooled since the solved metal ion concentrations determine its fate and toxicity in the environment. Based on result of a leaching experiment performed with the target substance (i.e., Slag, pig iron ladle refining, non-granulated, water-cooled) and the source substance (i.e., slags steelmaking) solved metal ion concentrations of the target substance are similar to the solved metal concentrations of the source substance. Read-across is fully justified and discussed in detail in the RAAF document attached on IUCLID section 13.
ABS: Eisenia fetida OECD 207: 14 d-LC0 = 100 g/kg (highest concentration tested) ABS: Eisenia fetida ISO 11268-1: 14 d-LC50 = 770 g/kg (highest concentration tested)
Key value for chemical safety assessment
Additional information
In an earthworm acute toxicity test performed according to OECD 207 and GLP, powdered air-cooled blast furnace slag (ABS) did not affect survival or body fresh weight of the earthworm Eisenia fetida during 2 weeks incubation in soil with a maximum concentration of 100 g of the slag per kg of artificial OECD soil (highest concentration tested, NERI 2008).
The effects of slags on earthworms were measured in a 14 d test according to ISO 11268-1 (Effects of Pollutants on Earthworms. 1. Determination of Acute Toxicity Using Artificial Soil Substrate). ABS was not toxic against Eisenia fetida within 14 days. The LC50 was 770 g/kg (highest concentration tested, LECES 1999).
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