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EC number: 701-480-0 | 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

Particle size distribution (Granulometry)
Administrative data
Link to relevant study record(s)
- Endpoint:
- particle size distribution (granulometry)
- Remarks:
- Dustiness
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- DIN 55992-1 (Determination of a parameter for the dust formation of pigments and extenders - Part 1: Rotation method)
- Version / remarks:
- 2006
- Deviations:
- yes
- Remarks:
- The Heubach dust meter was connected to a seven stage cascade impactor.
- Qualifier:
- according to guideline
- Guideline:
- other: other: DIN EN 481
- Principles of method if other than guideline:
- The Heubach dust meter is modified in a way that a seven stage cascade impactor is connected to the system. This involves an additional air fed of 20L/min via the coarse dust seperator needed to supply the cascade impactor with 40L/min air current as specified in the manufacturer's specifications.
The calculation report: EBRC (2022)
The Multiple-Path Particle Dosimetry Model (MPPD, v3.01; ARA (2015)) was used to predict this fractional deposition behaviour for workers.
The model algorithms calculate the deposition (and clearance) of mono-disperse and polydisperse aerosols in the respiratory tract for particles ranging from ultra-fine (0.01 microns) to coarse (20 microns) sizes. Within each airway, the deposition is calculated using theoretically derived efficiencies for deposition by diffusion, sedimentation and impaction within the airway or airway bifurcation. Filtration of aerosols by the head is determined using empirical efficiency functions. - GLP compliance:
- no
- Type of method:
- rotating drum method
- Remarks:
- The Heubach dust meter was connected to a seven-stage cascade impactor.
- Type of particle tested:
- primary particle
- Type of distribution:
- volumetric distribution
- Specific details on test material used for the study:
- Substance density: 4.0312 ± 0.0025 g/cm³ (determined by DMT)
Substance humidity: 0.04 % (determined by DMT) - Mass median aerodynamic diameter:
- 21.5 µm
- Geometric standard deviation:
- 2.5
- Remarks on result:
- other: P50 MMAD and P50 GSD
- Remarks on result:
- not measured/tested
- Conclusions:
- Total Dustiness (airborne fraction): 61.12 mg/g (experimental results, DMT Report).
Mass median aerodynamic diameter of airborne fraction: P50 MMAD= 21.50 µm (distribution fitted to cascade impactor data). Geometric standard deviation of P50 MMAD: P50 GSD= 2.50
Fractional deposition in human respiratory tract (MPPD model, based on calculated MMAD):
Head (ET): 55.29 %
Tracheobronchial (TB): 0.48 %
Pulmonary (PU): 0.66 % - Endpoint:
- particle size distribution (granulometry)
- Remarks:
- Dustiness
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- DIN 55992-1 (Determination of a parameter for the dust formation of pigments and extenders - Part 1: Rotation method)
- Version / remarks:
- 2006
- Deviations:
- yes
- Remarks:
- The Heubach dust meter was connected to a seven stage cascade impactor.
- Qualifier:
- according to guideline
- Guideline:
- other: other: DIN EN 481
- Principles of method if other than guideline:
- The Heubach dust meter is modified in a way that a seven stage cascade impactor is connected to the system. This involves an additional air fed of 20L/min via the coarse dust seperator needed to supply the cascade impactor with 40L/min air current as specified in the manufacturer's specifications.
The calculation report: EBRC (2022)
The Multiple-Path Particle Dosimetry Model (MPPD, v3.01; ARA (2015)) was used to predict this fractional deposition behaviour for workers.
The model algorithms calculate the deposition (and clearance) of mono-disperse and polydisperse aerosols in the respiratory tract for particles ranging from ultra-fine (0.01 microns) to coarse (20 microns) sizes. Within each airway, the deposition is calculated using theoretically derived efficiencies for deposition by diffusion, sedimentation and impaction within the airway or airway bifurcation. Filtration of aerosols by the head is determined using empirical efficiency functions. - GLP compliance:
- no
- Type of method:
- rotating drum method
- Remarks:
- The Heubach dust meter was connected to a seven-stage cascade impactor.
- Type of particle tested:
- primary particle
- Type of distribution:
- volumetric distribution
- Specific details on test material used for the study:
- Substance density: 3.4701 ± 0.0011 g/cm³ (determined by DMT)
Substance humidity: 0.01 % (determined by DMT) - Mass median aerodynamic diameter:
- 28.14 µm
- Geometric standard deviation:
- 1.56
- Remarks on result:
- other: P50 MMAD and P50 GSD
- Remarks on result:
- not measured/tested
- Conclusions:
- Total Dustiness (airborne fraction): 8.67 mg/g (experimental results, DMT Report).
Mass median aerodynamic diameter of airborne fraction: P50 MMAD= 28.14 µm (distribution fitted to cascade impactor data). Geometric standard deviation of P50 MMAD: P50 GSD= 1.56
Fractional deposition in human respiratory tract (MPPD model, based on calculated MMAD):
Head (ET): 48.59 %
Tracheobronchial (TB): 0.06 %
Pulmonary (PU): 0.01 % - Endpoint:
- particle size distribution (granulometry)
- Remarks:
- Dustiness
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- DIN 55992-1 (Determination of a parameter for the dust formation of pigments and extenders - Part 1: Rotation method)
- Version / remarks:
- 2006
- Deviations:
- yes
- Remarks:
- The Heubach dust meter was connected to a seven stage cascade impactor.
- Qualifier:
- according to guideline
- Guideline:
- other: other: DIN EN 481
- Principles of method if other than guideline:
- The Heubach dust meter is modified in a way that a seven stage cascade impactor is connected to the system. This involves an additional air fed of 20L/min via the coarse dust seperator needed to supply the cascade impactor with 40L/min air current as specified in the manufacturer's specifications.
The calculation report: EBRC (2022)
The Multiple-Path Particle Dosimetry Model (MPPD, v3.01; ARA (2015)) was used to predict this fractional deposition behaviour for workers.
The model algorithms calculate the deposition (and clearance) of mono-disperse and polydisperse aerosols in the respiratory tract for particles ranging from ultra-fine (0.01 microns) to coarse (20 microns) sizes. Within each airway, the deposition is calculated using theoretically derived efficiencies for deposition by diffusion, sedimentation and impaction within the airway or airway bifurcation. Filtration of aerosols by the head is determined using empirical efficiency functions. - GLP compliance:
- no
- Type of method:
- rotating drum method
- Remarks:
- The Heubach dust meter was connected to a seven-stage cascade impactor.
- Type of particle tested:
- primary particle
- Type of distribution:
- volumetric distribution
- Specific details on test material used for the study:
- Substance density: 4.31 g/cm³ (determined by DMT)
Substance humidity: 0.13 % (determined by DMT) - Mass median aerodynamic diameter:
- 25.38 µm
- Geometric standard deviation:
- 1.54
- Remarks on result:
- other: P50 MMAD and P50 GSD
- Remarks on result:
- not measured/tested
- Conclusions:
- Total Dustiness (airborne fraction): 3.67 mg/g (experimental results, DMT Report).
Mass median aerodynamic diameter of airborne fraction: P50 MMAD= 25.38 µm (distribution fitted to cascade impactor data). Geometric standard deviation of P50 MMAD: P50 GSD= 1.54
Fractional deposition in human respiratory tract (MPPD model, based on calculated MMAD):
Head (ET): 53.60 %
Tracheobronchial (TB): 0.08 %
Pulmonary (PU): 0.01 % - Endpoint:
- particle size distribution (granulometry)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Well documented study performed according to EU acceptable method
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 110 (Particle Size Distribution / Fibre Length and Diameter Distributions)
- GLP compliance:
- no
- Other quality assurance:
- other: Outotec Research Oy has a certified Quality system ISO 9001:2000, Environmental system ISO14001 and Occupational Health and Safety system ISO18001 and Laboratory accreditation according to ISO/IEC 17025
- Type of method:
- sieving
- Type of distribution:
- counted distribution
- Key result
- Percentile:
- D50
- Mean:
- >= 741 - <= 2 426 µm
- Remarks on result:
- other: Granules
- Key result
- Percentile:
- D50
- Mean:
- >= 1 316 - <= 2 029 µm
- Remarks on result:
- other: Massive (stones)
- Key result
- Percentile:
- D50
- Mean:
- >= 30 - <= 79 µm
- Remarks on result:
- other: Powder/fines
- Conclusions:
- Copper slags are presented in the form of granules, massive(stones) or powder.
Partcle size distribution was determined for the three different forms of slag.
Granules and powders were tested in their original partcile size as placed on the market. Stones were crushed to less than 5 mm before testing
D50 of parcle size for the slag granules is measured in the range of 741 - 2426 µm
D50 of parcle size for the slag stones is measured in the range of 1316 - 2029 µm
D50 of parcle size for the slag fines is measured in the range of 30 - 70 µm - Executive summary:
Copper slags are presented in the form of granules, massive(stones) or powder.
Particle size distribution was determined for the three different forms of slag.
Granules and powders were tested in their original particle size as placed on the market. Stones were crushed to less than 5 mm before testing
D50 of particle size for the slag granules is measured in the range of 741 - 2426 µm
D50 of particle size for the slag stones is measured in the range of 1316 - 2029 µm
D50 of particle size for the slag fines is measured in the range of 30 - 70 µm
Referenceopen allclose all
Total dustiness (airborne fraction): 61.12 mg/g.
In the original study report by DMT, a calculation of the mass median diameter was not conducted. Since the deposited fractions were provided for each of the cascade impactor stages, it was possible to fit a monomodal lognormal distribution to the data by standard non-linear regression procedure. As a result, the MMAD and GSD are calculable and reported P50 MMAD = 21.50 µm, GSD = 2.50.
As the cascade impactor already takes aerodynamic characteristics of the particles into account, the reported mass median diameter can be interpreted as the mass median aerodynamic diameter.
This figure and the corresponding GSD were used as distribution parameters for the MPPD model enabling an estimation of deposited dust fractions in the human respiratory tract: These fractions were estimated as follows:
Head (ET): 55.29 %
Tracheobronchial (TB): 0.48%
Pulmonary (PU): 0.66 %
Total dustiness (airborne fraction): 8.67 mg/g.
In the original study report by DMT, a calculation of the mass median diameter was not conducted. Since the deposited fractions were provided for each of the cascade impactor stages, it was possible to fit a monomodal lognormal distribution to the data by standard non-linear regression procedure. As a result, the MMAD and GSD are calculable and reported P50 MMAD = 28.14 µm, GSD = 1.56.
As the cascade impactor already takes aerodynamic characteristics of the particles into account, the reported mass median diameter can be interpreted as the mass median aerodynamic diameter.
This figure and the corresponding GSD were used as distribution parameters for the MPPD model enabling an estimation of deposited dust fractions in the human respiratory tract: These fractions were estimated as follows:
Head (ET): 48.59 %
Tracheobronchial (TB): 0.06%
Pulmonary (PU): 0.01 %
Total dustiness (airborne fraction): 3.67 mg/g.
In the original study report by DMT, a calculation of the mass median diameter was not conducted. Since the deposited fractions were provided for each of the cascade impactor stages, it was possible to fit a monomodal lognormal distribution to the data by standard non-linear regression procedure. As a result, the MMAD and GSD are calculable and reported P50 MMAD = 25.38 µm, GSD = 1.54.
As the cascade impactor already takes aerodynamic characteristics of the particles into account, the reported mass median diameter can be interpreted as the mass median aerodynamic diameter.
This figure and the corresponding GSD were used as distribution parameters for the MPPD model enabling an estimation of deposited dust fractions in the human respiratory tract: These fractions were estimated as follows:
Head (ET): 53.60 %
Tracheobronchial (TB): 0.08%
Pulmonary (PU): 0.01 %
Sample |
Slag |
Slag |
Slag |
Slag |
|
|
|
|
Slag |
Slag |
Slag |
Slag |
Slag |
Slag |
Slag |
Slag |
Outotec code |
09TT02641 |
09TT02988 |
09TT03512 |
09TT05246 |
|
|
|
|
09TT02986 |
09TT02987 |
09TT03177 |
09TT03821 |
09TT03989 |
09TT05245 |
09TT03503 |
09TT03181 |
Granulometry |
Granular |
Granular |
Granular |
Granular |
|
|
|
|
Granular |
Powder |
Granular |
Granular |
Powder |
Stones |
Stones |
Stones |
D80, µm |
2168 |
>3360 |
1284 |
1975 |
|
|
|
|
2030 |
>106 |
1436 |
2289 |
71 |
2101 |
>2380 |
2023 |
D50, µm |
1390 |
2426 |
741 |
1125 |
|
|
|
|
1051 |
79 |
947 |
1189 |
30 |
1316 |
2029 |
1421 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Particle size distribution, granulated slags
Sample |
|
09TT02641 |
|
09TT02988 |
|
09TT03512 |
|
09TT05246 |
|
09TT02986 |
|
09TT03177 |
|
09TT03821 |
|
Size |
|
Retained |
|
Retained |
|
Retained |
|
Retained |
|
Retained |
|
Retained |
|
Retained |
|
mesh |
mm |
g |
% |
g |
% |
g |
% |
g |
% |
g |
% |
g |
% |
g |
% |
6 |
3.360 |
|
|
24.50 |
25.79 |
|
|
1.47 |
1.10 |
|
|
|
|
|
|
8 |
2.380 |
14.39 |
11.69 |
24.10 |
25.37 |
1.59 |
1.28 |
8.75 |
6.54 |
14.50 |
11.66 |
1.37 |
0.76 |
21.32 |
17.73 |
16 |
1.190 |
56.45 |
45.88 |
30.30 |
31.89 |
25.7 |
20.77 |
51.07 |
38.18 |
38.60 |
31.03 |
45.94 |
25.40 |
38.73 |
32.21 |
20 |
0.841 |
23.34 |
18.97 |
8.30 |
8.74 |
24 |
19.39 |
28.36 |
21.20 |
22.60 |
18.17 |
59.76 |
33.04 |
24.07 |
20.02 |
30 |
0.595 |
16.66 |
13.54 |
4.90 |
5.16 |
25.3 |
20.44 |
21.79 |
16.29 |
21.70 |
17.44 |
43.21 |
23.89 |
20.12 |
16.73 |
40 |
0.420 |
6.59 |
5.36 |
1.80 |
1.89 |
17.63 |
14.25 |
10.62 |
7.94 |
14.30 |
11.50 |
18.58 |
10.27 |
8.11 |
6.74 |
50 |
0.297 |
0.09 |
0.07 |
0.50 |
0.53 |
9.8 |
7.92 |
5.26 |
3.93 |
6.80 |
5.47 |
7.44 |
4.11 |
3.42 |
2.84 |
100 |
0.149 |
|
|
0.60 |
0.63 |
|
|
6.44 |
4.81 |
4.20 |
3.38 |
|
|
|
|
140 |
0.106 |
4.89 |
3.97 |
|
|
14.36 |
11.60 |
|
|
0.60 |
0.48 |
4.28 |
2.37 |
3.21 |
2.67 |
200 |
0.075 |
0.16 |
0.13 |
|
|
1.78 |
1.44 |
|
|
1.10 |
0.88 |
0.30 |
0.17 |
0.35 |
0.29 |
270 |
0.053 |
|
|
|
|
3.59 |
2.90 |
|
|
|
|
|
|
|
|
325 |
0.045 |
0.29 |
0.24 |
|
|
|
|
|
|
|
|
|
|
0.31 |
0.26 |
|
0.020 |
0.18 |
0.15 |
|
|
|
|
|
|
|
|
|
|
0.37 |
0.31 |
|
-0.020 |
0.01 |
0.01 |
|
|
|
|
|
|
|
|
|
|
0.24 |
0.20 |
Sum |
|
123.05 |
100.00 |
95.00 |
100.00 |
123.75 |
100 |
133.76 |
100 |
124.40 |
100.00 |
180.88 |
100.00 |
120.25 |
100 |
Particle size distribution, slag stones
Sample |
|
09TT05245 |
|
09TT03503 |
|
09TT03181 |
|
||
Size |
|
Retained |
|
Retained |
|
Retained |
|
|
|
mesh |
mm |
g |
% |
g |
% |
g |
% |
|
|
6 |
3.360 |
1.25 |
0.90 |
|
|
|
|
|
|
8 |
2.380 |
11.66 |
8.42 |
55.59 |
41.74 |
0.80 |
0.65 |
|
|
16 |
1.190 |
62.97 |
45.47 |
37.68 |
28.29 |
73.30 |
59.89 |
|
|
20 |
0.841 |
17.31 |
12.50 |
9.08 |
6.82 |
12.50 |
10.21 |
|
|
30 |
0.595 |
12.84 |
9.27 |
7.72 |
5.80 |
8.80 |
7.19 |
|
|
40 |
0.420 |
32.46 |
23.44 |
5.43 |
4.08 |
6.60 |
5.39 |
|
|
50 |
0.297 |
|
|
3.75 |
2.82 |
4.70 |
3.84 |
|
|
100 |
0.149 |
|
|
7.39 |
5.55 |
|
|
|
|
140 |
0.106 |
|
|
6.34 |
4.91 |
8.70 |
7.11 |
|
|
200 |
0.075 |
|
|
|
|
1.10 |
0.90 |
|
|
270 |
-0.075 |
|
|
|
|
|
|
|
|
325 |
0.045 |
|
|
|
|
|
|
|
|
|
0.020 |
|
|
|
|
|
|
|
|
|
-0.020 |
|
|
|
|
|
|
|
|
Sum |
|
138.49 |
100 |
133.18 |
100.00 |
122.40 |
100.00 |
|
Particle size distribution, slag fines
Sample |
|
09TT03989 |
|
09TT02987 |
|
Size |
|
Retained |
|
Retained |
|
mesh |
mm |
g |
% |
g |
% |
100 |
|
|
|
|
|
140 |
0.106 |
6.62 |
5.35 |
42.30 |
34.42 |
200 |
0.075 |
15.07 |
12.18 |
22.40 |
18.23 |
270 |
-0.075 |
|
|
15.00 |
12.21 |
325 |
0.045 |
25.4 |
20.53 |
4.70 |
3.82 |
|
0.020 |
26.54 |
21.45 |
17.80 |
14.48 |
|
-0.020 |
50.12 |
40.50 |
20.70 |
16.84 |
Sum |
|
123.75 |
100 |
122.90 |
100.00 |
Description of key information
Partcle size distribution was determined for the three different forms of slag (granules, massive(stones) or powder):
D50 of parcle size for the slag granules is measured in the range of 741 - 2426 µm
D50 of parcle size for the slag stones is measured in the range of 1316 - 2029 µm
D50 of parcle size for the slag fines is measured in the range of 30 - 70 µm
The dustiness was determined from three copper slags (Copper slag 5, Copper slag 6 and 9):
Copper slag 5:
Total Dustiness (airborne fraction): 3.67 mg/g
MMAD= 25.38 µm, GSD= 1.54
Head (ET): 53.60 %
Tracheobronchial (TB): 0.08 %
Pulmonary (PU): 0.01 %
Copper slag 6:
Total Dustiness (airborne fraction): 8.67 mg/g
MMAD= 28.14 µm, GSD= 1.56
Head (ET): 48.59 %
Tracheobronchial (TB): 0.06 %
Pulmonary (PU): 0.01 %
Copper slag 9:
Total Dustiness (airborne fraction): 61.12 mg/g
MMAD= 21.50 µm, GSD= 2.50
Head (ET): 55.29 %
Tracheobronchial (TB): 0.48 %
Pulmonary (PU): 0.66 %
Additional information
Partcle size distribution
Copper slags are presented in the form of granules, massive(stones) or powder.
Partcle size distribution was determined for the three different forms of slag.
Granules and powders were tested in their original partcile size as placed on the market. Stones were crushed to less than 5 mm before testing
D50 of parcle size for the slag granules is measured in the range of 741 - 2426 µm
D50 of parcle size for the slag stones is measured in the range of 1316 - 2029 µm
D50 of parcle size for the slag fines is measured in the range of 30 - 70 µm
Dustiness
Copper slag 5: Total Dustiness (airborne fraction): 3.67 mg/g (experimental results, DMT Report).
Mass median aerodynamic diameter of airborne fraction: P50 MMAD= 25.38 µm (distribution fitted to cascade impactor data). Geometric standard deviation of P50 MMAD: P50 GSD= 1.54
Fractional deposition in human respiratory tract (MPPD model, based on calculated MMAD):
Head (ET): 53.60 %
Tracheobronchial (TB): 0.08 %
Pulmonary (PU): 0.01 %
Copper slag 6: Total Dustiness (airborne fraction): 8.67 mg/g (experimental results, DMT Report).
Mass median aerodynamic diameter of airborne fraction: P50 MMAD= 28.14 µm (distribution fitted to cascade impactor data). Geometric standard deviation of P50 MMAD: P50 GSD= 1.56
Fractional deposition in human respiratory tract (MPPD model, based on calculated MMAD):
Head (ET): 48.59 %
Tracheobronchial (TB): 0.06 %
Pulmonary (PU): 0.01 %
Copper slag 9: Total Dustiness (airborne fraction): 61.12 mg/g (experimental results, DMT Report).
Mass median aerodynamic diameter of airborne fraction: P50 MMAD= 21.50 µm (distribution fitted to cascade impactor data). Geometric standard deviation of P50 MMAD: P50 GSD= 2.50
Fractional deposition in human respiratory tract (MPPD model, based on calculated MMAD):
Head (ET): 55.29 %
Tracheobronchial (TB): 0.48 %
Pulmonary (PU): 0.66 %
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