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EC number: 273-728-1 | CAS number: 69012-28-8 By-product of the manufacture of ferromanganese alloy containing primarily oxides of aluminum, manganese 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

Particle size distribution (Granulometry)
Administrative data
Link to relevant study record(s)
- Endpoint:
- particle size distribution (granulometry)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 22 December 2008 to 20 February 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted to current guideline and GLP.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 110 (Particle Size Distribution / Fibre Length and Diameter Distributions)
- Deviations:
- yes
- Remarks:
- (The study is only applicable to materials less than 100 µm. The sieve method was used to satisfy the guideline as the result obtained determines whether or not the material is suitable for the full study.)
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- other: sieve
- Type of distribution:
- volumetric distribution
- Percentile:
- D50
- Remarks on result:
- other: No source field for Standard deviation.
- No.:
- #1
- Size:
- < 100 µm
- Distribution:
- 3.3 %
- Conclusions:
- From a sub-sample of the test material the percentage of material with a particle size less than 100 µm was determined to be 3.3% by sieve analysis. This indicated that the test material was of a particle size that was essentially non-inhalable. It must be noted that this value is a significant overestimate of the true fine particle fraction of the test material due to the sampling procedure.
- Executive summary:
The particle size of the test material was determined following the screening study as outlined in the standardised guideline OECD 110.
On visual assessment the test material was observed to be composed of rocks of various sizes from approximately 10 cm to <1 cm plus some dust. To represent a worst case scenario for potential inhalation risk the larger particles were removed and only smaller particles and dust were sub-sampled. From this sub-sample the percentage of test material with a particle size of <100 µm was calculated by sieve analysis. A representative portion of this sub-sample (14.41 g) was sieved for approximately 30 minutes on an Inclyno sieve shaker using a 100 µm sieve. The mass of the test material passing through the sieve was measured.
From a sub-sample of the test material the percentage of material with a particle size less than 100 µm was determined to be 3.3%. This indicated that the test material was of a particle size that was essentially non-inhalable. It must be noted that this value is a significant overestimate of the true fine particle fraction of the test material due to the sampling procedure.
Reference
The results of the sieving procedure are shown in the following table:
Sieve aperture size (µm) |
100 |
Mass of test material transferred to sieve (g) |
14.41 |
Mass of test material passed through sieve (g) |
0.48 |
Test material less than sieve aperture size (%) |
3.3 |
Description of key information
The proportion of test material having an inhalable particle size less than 100 µm was below 3.3 % w/w, OECD 110 sieve method, Butler & O'Connor (2009)
Additional information
The particle size of the test material was determined following the screening study as outlined in the standardised guideline OECD 110.
On visual assessment the test material was observed to be composed of rocks of various sizes from approximately 10 cm to <1 cm plus some dust. To represent a worst case scenario for potential inhalation risk the larger particles were removed and only smaller particles and dust were sub-sampled. From this sub-sample the percentage of test material with a particle size of <100 µm was calculated by sieve analysis. A representative portion of this sub-sample (14.41 g) was sieved for approximately 30 minutes on an Inclyno sieve shaker using a 100 µm sieve. The mass of the test material passing through the sieve was measured.
From a sub-sample of the test material the percentage of material with a particle size less than 100 µm was determined to be 3.3%. This indicated that the test material was of a particle size that was essentially non-inhalable. It must be noted that this value is a significant overestimate of the true fine particle fraction of the test material due to the sampling procedure.
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