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EC number: 266-966-2 | CAS number: 67711-90-4 Solids recovered from exhaust gas streams found in furnaces, flues and settling chambers as a result of roasting, smelting and converting operations. Constituents found as end products are dependent upon the materials used during various operations.
- 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
Additional physico-chemical information
Administrative data
- Endpoint:
- other: representative mineralogy
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: No GLP study but other quality assurance
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
Materials and methods
- Principles of method if other than guideline:
- Chemistry /elemental analysis was determined using ICP (inductively Coupled Plasma spectroscopy). Metal speciation/metal mineralogy was assessed from Sequential extraction/metal analysis and mineralogical analysis (XRD and microscopes equipped with EDS (Energy Dispersive Spectrometry) and WDS (Wavelength Dispersive Spectrometry) analysers. The interpretation of the overall results was performed by expert (with profound knowledge of metal particularities).
- GLP compliance:
- no
- Remarks:
- but equivalent Quality Assurance
Test material
- Reference substance name:
- Flue dust, copper-refining
- EC Number:
- 266-966-2
- EC Name:
- Flue dust, copper-refining
- Cas Number:
- 67711-90-4
- IUPAC Name:
- flue dust, copper refining
- Details on test material:
- Sample collection made according to ECI/REACH Copper Consortium Standards Protocols (see IUCLID section 1.4).
Constituent 1
Results and discussion
- Results:
- The tested materials were characterized (physico-chemical and mineralogical properties) in view of the upcoming REACH registrations of copper intermediates and copper slags by the Copper Consortium.
Any other information on results incl. tables
Sample |
Flue dust |
Flue dust |
Flue dust |
Sample |
B11 |
B11 |
B11 |
Outotec code |
09TT03192 |
09TT03513 |
09TT03514 |
The studied flue dust samples are fine- grained, the D50 value is for all samples below 20µm. They contain 9.18- 51.0% lead, 0.52- 9.58% copper, 6.3- 43.9% zinc, 0.09- 2.8% arsenic, and 1.15- 14.7% sulfur.
Flue dust samples 09TT03192 and 09TT03513 consist mainly of zinc oxide, zincite, other main compounds being zinc oxide chloride and dawsonite –type sodium carbonate in 09TT03192 and plattnerite and anglesite– type lead oxide and carbonate in 09TT03513. The sample 09TT03514 consist mainly galena, sphalerite, energite and organic carbon.
The chemical analysis of studied sampled are given in Table 8 and Table 9 and their mineralogical composition in Table 10 with distribution of copper. The microscope images, XRD and TG/DSC –graphs and results of water solubility tests are given for samples 09TT03192 in Appendix A, 09TT03513 in Appendix B and 09TT03514 in Appendix C
Table8: Chemical composition of studied sample, part 1
Lab code |
|
|
09TT03192 |
09TT03513 |
09TT03514 |
Sample |
|
|
Flue dust |
Flue dust |
Flue dust |
Sample code |
|
|
B11 |
B11 |
B11 |
|
|
|
|
|
|
Cu |
P1 |
% |
0.15 |
<0.003 |
0.01 |
|
P2 |
% |
7.00 |
1.69 |
0.43 |
|
P3 |
% |
2.25 |
0.06 |
0.01 |
|
P4 |
% |
0.17 |
0.09 |
0.05 |
|
Sum |
|
9.57 |
1.84 |
0.50 |
|
TOT |
% |
9.58 |
1.80 |
0.52 |
|
|
|
|
|
|
As |
P1 |
% |
< 0.004 |
<0.003 |
<0.002 |
|
P2 |
% |
0.08 |
0.40 |
2.51 |
|
P3 |
% |
< 0.005 |
<0.003 |
<0.003 |
|
P4 |
% |
< 0.002 |
0.04 |
0.13 |
|
Sum |
|
0.08 |
0.44 |
2.64 |
|
TOT |
% |
0.09 |
0.45 |
2.80 |
|
|
|
|
|
|
Fe |
P1 |
% |
< 0.004 |
<0.003 |
<0.002 |
|
P2 |
% |
0.58 |
0.20 |
0.03 |
|
P3 |
% |
0.02 |
<0.003 |
<0.003 |
|
P4 |
% |
0.12 |
0.05 |
0.12 |
|
Sum |
|
0.72 |
0.25 |
0.15 |
|
TOT |
% |
0.78 |
0.29 |
0.17 |
|
|
|
|
|
|
Ni |
P1 |
% |
0.01 |
<0.003 |
<0.002 |
|
P2 |
% |
0.05 |
<0.007 |
<0.006 |
|
P3 |
% |
0.03 |
<0.003 |
<0.003 |
|
P4 |
% |
0.14 |
<0.001 |
0.00 |
|
Sum |
|
0.22 |
0.00 |
0.00 |
|
TOT |
% |
0.23 |
0.00 |
0.00 |
|
|
|
|
|
|
Pb |
P1 |
% |
0.87 |
0.22 |
0.19 |
|
P2 |
% |
0.12 |
0.10 |
0.13 |
|
P3 |
% |
0.73 |
3.76 |
6.74 |
|
P4 |
% |
7.67 |
33.50 |
40.90 |
|
Sum |
|
9.39 |
37.58 |
47.96 |
|
TOT |
% |
9.18 |
39.60 |
51.00 |
P1= H2O, P2= H2SO4, P3= KCN+Br-MeOH, P4= HNO3–soluble, TOT= total -, BM= bromine-methanol dissolutions, KEM= ion exchange chromatography, LECO = S/C analyzer, satmagan = Fe3O4analyzer
Table 9: Chemical composition of studied sample, part 2
Lab code |
|
|
09TT03192 |
09TT03513 |
09TT03514 |
Sample |
|
|
Flue dust |
Flue dust |
Flue dust |
Sample code |
|
|
B11 |
B11 |
B11 |
|
|
|
|
|
|
Co |
TOT |
% |
0.01 |
0.00 |
0.00 |
Sb |
TOT |
% |
0.08 |
<0.01 |
0.10 |
Sn |
TOT |
% |
1.38 |
<0.01 |
0.28 |
Zn |
TOT |
% |
43.90 |
25.60 |
6.30 |
Mo |
TOT |
% |
0.01 |
n.a. |
0.07 |
Ag |
TOT |
% |
0.01 |
0.01 |
0.01 |
|
|
|
|
|
|
Se |
TOT |
% |
0.01 |
n.a. |
0.02 |
Sr |
TOT |
% |
< 0.002 |
n.a. |
n.a. |
Te |
TOT |
% |
< 0.002 |
n.a. |
n.a. |
Bi |
TOT |
% |
n.a. |
n.a. |
0.02 |
Cd |
TOT |
% |
n.a. |
n.a. |
0.08 |
|
|
|
|
|
|
SiO2 |
KEM |
% |
1.13 |
3.4 |
1.40 |
Al2O3 |
TOT |
% |
0.70 |
0.72 |
0.14 |
Cr2O3 |
TOT |
% |
0.04 |
0.01 |
<0.003 |
K2O |
TOT |
% |
0.53 |
6.00 |
1.11 |
MgO |
TOT |
% |
0.10 |
1.90 |
0.05 |
MnO |
TOT |
% |
0.03 |
0.07 |
0.00 |
Na2O |
TOT |
% |
7.66 |
1.30 |
0.41 |
CaO |
TOT |
% |
0.40 |
1.40 |
0.10 |
TiO2 |
TOT |
% |
0.02 |
n.a. |
0.01 |
Zr |
TOT |
% |
|
|
|
Ba |
TOT |
% |
< 0.01 |
n.a. |
n.a. |
P |
TOT |
% |
n.a. |
n.a. |
0.01 |
|
|
|
|
|
|
Cl- |
KEM |
% |
8.50 |
n.a. |
n.a. |
B |
TOT |
% |
0.01 |
n.a. |
n.a. |
S |
Leco |
% |
1.15 |
1.35 |
14.70 |
SO42- |
KEM |
% |
n.a. |
4.30 |
0.50 |
C |
Leco |
% |
0.79 |
0.60 |
15.20 |
Satmagan |
|
% |
0.00 |
n.a. |
n.a. |
surface area |
|
m2/g |
3.01 |
3.34 |
- |
density |
|
g/cm3 |
4.74 |
5.33 |
3.22 |
ash content |
|
% |
n.a. |
n.a. |
91.20 |
P1= H2O , P2= H2SO4, P3= KCN+Br-MeOH, P4= HNO3–soluble, TOT= total -, BM= bromine-methanol dissolutions, KEM= ion exchange chromatography, LECO = S/C analyzer, satmagan = Fe3O4analyzer
Table 10: Mineral composition and distribution of copper
09TT03192 |
|
|
|
09TT03513 |
|
|
|
09TT03514 |
|
|
B11 |
|
|
|
B11 |
|
|
|
B11 |
|
|
Mineral composition, -% |
|
|
|
|
|
|
|
|
|
|
Cu |
Copper |
2.63 |
|
Cu |
Copper |
0.07 |
|
Cu5FeS4 |
Bornite |
0.02 |
CuO |
Tenorite |
6.27 |
|
Cu2O |
Cuprite |
1.98 |
|
Cu3AsS4 |
Enargite |
13.23 |
CuSnO |
CuSn -oxide |
8.38 |
|
FeNiO2 |
Trevorite |
0.02 |
|
PbS |
Galena |
61.87 |
NiO |
Bunsenite |
0.06 |
|
K2O |
K -oxide |
6.00 |
|
ZnS |
Sphalerite |
10.51 |
PbCO3 |
Cerussite |
8.15 |
|
PbO |
Massicot |
0.11 |
|
CaSO4 |
Gypsum |
0.29 |
PbO |
Litharge |
0.23 |
|
ZnO |
Zincite |
34.09 |
|
C |
Carbon |
15.20 |
SiO2 |
Cristobalite |
1.51 |
|
PbO2 |
Plattnerite |
29.55 |
|
|
|
|
Zn2OCl2*2H2O |
Zinc oxide chloride |
19.54 |
|
PbSi(Fe,Al,Ca)O2-3 |
Pb- glass |
11.59 |
|
|
|
|
ZnO |
Zincite |
33.95 |
|
PbCaAsx |
Pb- glass |
1.91 |
|
|
|
|
NaAl(CO3)(OH)2 |
Dawsonite |
19.27 |
|
PbSO3 |
Anglesite |
13.57 |
|
|
|
|
|
|
|
|
NaCaSiOx |
NaCa -silicate |
1.10 |
|
|
|
|
Total |
|
100.00 |
|
Total |
|
100.00 |
|
Total |
|
101.13 |
|
|
|
|
|
|
|
|
|
|
|
Distribution of copper |
|
|
|
|
|
|
|
|
|
|
Cu |
|
27.01 |
|
Cu |
|
3.59 |
|
Cu5FeS4 |
|
0.20 |
CuO |
|
51.10 |
|
Cu2O |
|
83.42 |
|
Cu3AsS4 |
|
99.80 |
CuSnO |
|
21.89 |
|
PbSi(Fe,Al,Ca)O2-3 |
|
11.15 |
|
|
|
|
|
|
|
|
PbCaAsx |
|
1.84 |
|
|
|
|
Applicant's summary and conclusion
- Conclusions:
- Good quality study that assessed full chemistry and mineralogy of flue dust samples. Proposed RWC mineralogy (distribution pattern for each key element, i.e. % from Total into the various mineralogical forms/species present into the UVCB) can be used for classification of the UVCB substance (mixture toxicity rules)
- Executive summary:
The studied flue dust samples are fine- grained, the D50value is for all samples below 20µm. They contain 9.18- 51.0% lead, 0.52- 9.58% copper, 6.3- 43.9% zinc, 0.09- 2.8% arsenic, and 1.15- 14.7% sulfur.
Flue dust samples 09TT03192 and 09TT03513 consist mainly of zinc oxide, zincite, other main compounds being zinc oxide chloride and dawsonite –type sodium carbonate in 09TT03192 and plattnerite and anglesite– type lead oxide and carbonate in 09TT03513. The sample 09TT03514 consist mainly galena, sphalerite, energite and organic carbon.
.Based on these results, the following RWC Distribution pattern is derived (relevant for classification):
Copper in the metal Cu form (WC powder, 16.58% from total Cu) + in Cu(I) oxide forms (83.42% from total Cu)
Lead in the compound forms (100% from total Pb)
Zinc in the oxide form (100% from total Zn)
Arsenic in the form of Arsenic compounds (100% from total As)
Nickel in the form of oxide (WC NiO, 100% from total Ni)
Cadmium, tin, and other metals: oxide forms (each, 100% from total element)
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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