HydrometTreatment en 4d7f53c6c9518

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    HYDROMETALLURGICAL TREATMENT OF COPPER WASTE PRODUCTS IN BULGARIA

    Valeri I.Tsekov, Georgi M. Savov, Valeri P. Kanev, Todor I.Garvanov, Todor T. Angelov

    IONTEH Ltd, 13 Prof.Tsv.Lazarov blv., 1574 Sofia, Bulgaria; e-mail: [email protected]

    Valeria K. Kovacheva-NinovaUniversity of Mining and Geology "St. Ivan Rilski", Department of Mineral Technology, Sofia, Bulgaria

    ABSTRACT:

    Waste materials from Pb-Zn plants contain significant amount of copper, zinc, lead and some nobles metals.

    The developed hydrometallurgical scheme include the following operation: 1)Oxidizing, desolving andpreparing of a pregnant solution; 2)Ion exchange separation and concentration of the valuables elements;

    3)Further chemical or electrochemical producing of final product - electrolytic metals and/or salts and oxides.

    The process feasibility was investigated in semi-industrial trials, carried out on a autoclave facility at Tzar

    Asen L-SX-EW plant. An economic analysis of the above options indicated the process profitability.

    This paper describes the results of the conducted trials and gives the most significant parameters of the process.

    Keywords: copper waste materials, extraction, sorption, autoclave

    1.INTRODUCTION

    Copper waste materials produced in

    conventional metallurgical plants in Bulgaria

    usually contained significant amounts of the

    valuable metals i.e. Cu, Zn, Pb and any precious

    metals. These waste materials are copper

    deposition from Pb/Zn plants and lead powders

    from the copper productions. In order to find a

    effective way to treatment a few

    hydrometallurgical techniques, which include

    dissolving, producing of barren solution, ion

    exchange separation and concentration and furtherchemical or electrochemical recovery of the

    valuable product was developed The net result of

    the use of this techniques is that valuable metals

    can be produced from sources that in the past

    would have gone untouched. Further, the process is

    capable of removing Cu, Zn, and Pb from waste

    materials where otherwise it would have been

    considered a contaminant to the environment.

    The developed techniques includes heat

    treatment and leaching of copper and zinc with

    acid solution. Further the pregnant liquor ispumped subsequently for sorption of zinc and

    solvent extraction of copper, and raffinate is

    returned to the dissolving stage. The organic

    phase, from extraction stage now loaded withcopper, discharges to the strip stage, where

    loaded organic is stripping with electrolyte,

    which has been returned from the EW tankhouse.

    The obtained in this stage strong electrolyte is

    then pumped to the EW tankhouse, where copper

    cathodes are produced.

    The other valuable product is crystalline zinc

    sulphate or solution of zinc sulphate, which are

    used in zinc electrolytic productions. Solid

    remnant contains lead and noble metals.

    The treatment of the lead powders includesleaching in sulphuric acid media with oxidizing

    agent nitric acid (HNO3). Leaching was

    performed in a stirred reaction vessel at low-

    temperature regime. Further, barren solution and

    solid residues are processing by the same

    technique like this used for the copper waste

    minerals.

    Examination of the results of earlier work

    dealing with processing of this type of materials

    and an analysis of all known hydrometallurgical

    techniques were shown that waste copperbearingmaterials are suitable for autoclaving treatment.

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    2.AUTOCLAVE PROCESSING OF LOW-

    GRADE COPPER RESOURCES

    A simplified flow chart of the process is given

    on Figure 1.

    Figure 1. Principle flowsheet

    Initial material for autoclaving was product

    from copper purification of zinc-bearing solutions

    in KCM, Plovdiv, Bulgaria. Table 1 represents

    the chemical composition of the copper-bearing

    materials.

    Table 1. Chemical composition

    Cu, % Zn, % Fe, % Pb, % Cd, %

    25.00 3.08 1.00 3.00 0.20

    Ag, g/t As, % Moisture % Density t/m3

    100 0.03 35 1.82

    The regime of autoclave processing wasinvestigated in leaching trials on a 3l autoclave at

    various parameters such a processing time,

    pressure oxidation, temperature and sulphuric

    acid concentrations. All trials were carry out at

    liquid/solid ratio =3/1. The optimal parameters of

    autoclave processing are:

    Processing time - 1.2-1.5 h

    Pressure - 0.25-0.35 MPa

    Liquid/solid ratio - 3/1

    H2SO4 concentration - 250-300 g/l

    Leaching of copper waste materials withH2SO4 in the autoclave resulted in 97.8% copper

    and 98.5% zinc and iron autoclave extraction.

    After leaching the solid residue is 32% from

    initial product and its contains about 300 g/t Pb

    and up to 9% sulphates. This solid product is

    called Pb-Ag unconventional concentrate.

    The autoclave facility working now at The

    Tzar Asen L-SX-EW plant (property of IONTEH

    Ltd.) is accounted for a total day output of

    approximately 12 t copper deposition (90 t/month

    Cu). The main process parameters of the

    autoclave facility are:

    Total operating volume 2 m3

    Stirring compressed air

    Operating temperature (max) 200oC

    Heating saturated steam

    Operating pressure (max) 2.2 MPa

    Output (on pulp) 0.5-1.5 m3/h

    Volume weight of pulp 1.2-1.5 t/m3

    The autoclave leaching was conducted

    according to the principal flowsheet shown inFigure 2.The liquid phase was water and

    sulphuric acid solution. A constant pH was

    maintained with regulating the feeding of H2SO4.

    For the preparing of the initial pulp reaction

    vessel (pos.1) was used. This pulp, by high

    pressure piston pump (pos.2) and through a

    buffer anti-pulsator (pos 3), goes to the first

    autoclave(pos 4/1) and step by step thru the rests.

    The outflow pulp from the last autoclave (pos

    4/4), entered to a separator and reducing the

    pressure goes to the reaction vessel (pos 6). Thenext step is the phase separation, which carried

    out with a filterpress . Then solution goes to

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    Figure 2. Flowsheet of machines and apparatus.

    purification and metals recovery. A continuous,

    with very high efficiency, regime was the

    autoclave facility working in.

    3.CONCLUSION

    The operating parameters of the autoclave

    facility and its coupling with SX/EW plants,

    sorption and concentrate processes gives an

    additional opportunity for hydrometallurgical

    treatment of wide range waste materials and

    unconventional resources.

    Now under development are techniques for

    dissolving of cementation copper concentrate,

    conventional copper sulphide concentrate and lead

    powders.

    4. REFERENCES

    Bartlett ,R ,1992-Leaching and Fluid Recoveryof Materials, Second edition

    Cooper W.C., Dreisinger D.B.,1995 -The

    principles and practice of leaching

    Dudas.L, Maass.H and Bhappu,R.,1974 Role of

    mineralogy and in situ leaching of copper

    ores,AIME

    Kosyakov.A,Hamalainen.P,1995 Autoclave

    processing of low grade copper-nickel

    concentrates

    Logsdail D.H., M.G. Slater, Solvent extraction in

    the process industries, Proceedings of ISEC

    93, Publihd for SCI by Elselvier Applied

    Sciece.

    Ritcey G.M., A. W. Ashbrook, Solvent extraction

    principles and applications to process

    metallurgy, Elselvier Scientific Publishing

    Company, Amsterdam-Oxford-New York,

    1979