THE PROCESSING OF ZINC BEARING MATERIALS IN A DC ARC FURNACE
BACKGROUND OF THE INVENTION
This invention relates generally to the reaction of zinc bearing materials with a reducing agent in a d.e. arc furnace in order to recover zinc via a vapour phase, and produce a disposable slag.
The invention may be applied to recover zinc from zinc bearing secondary materials, or for the treatment of zinc ores and/or primary oxidic zinc concentrates .
Secondary materials such as lead blast furnace slags from lead smelting, Imperial Smelting Furnace (ISF) slags from zinc/lead smelting, electric arc furnace (EAF) dusts produced during the production of carbon steel from scrap, electrolytic zinc-plant residues or leach-process residues, and drosses which contain zinc and lead, are processed primarily for environmental and recycling reasons. The invention may be used for the treatment of these materials.
Primary oxidic zinc concentrates and/or zinc ores which are high in silica and therefore also difficult to leach economically, are also amenable to treatment by the method of the invention.
Technology exists for treating most of these materials to produce saleable
products and environmentally acceptable final slags or residues (eg Waelz kiln,
Elkem and Tetronics processes). Some of the known processes have
experienced technical difficulties or are economically viable only at very large
throughputs (more than 50kt of zinc bearing material per annum). The latter
factor has ied to the establishment of centralised processing facilities controlled
by a few large companies and this may place the proαucers of the secondary
materials at a disadvantage.
Although environmental considerations are a primary motivating factor dictating
the processing of these zinc-bearing secondary materials, it should be borne in
mind they contain from 10% to 40% zinc oxide and are a potential resource for the
recycling and recovery of zinc.
The use of a three-phase a.c. slag-resistance furnace instead of a d.e. arc furnace
for the fuming of zinc and lead has a number of drawbacks. Accurate control of
the CO:CO2 ratio in the furnace gas and of additions of reductant to the reaction
zone are not easily achieved, while a power constraint is imposed by the
nrevaiiing electrical resistivity of the slag. Flux additions may be required to
achieve a suitable slag resistivity. Also the high power fluxes (MW/m2 molten
bath area) and zinc fuming rates (Zn vapour/h/m2) of a d.e. arc furnace cannot be
reached in an a.c. furnace. Careful control of the slag temperature must be
maintained in an a.c. furnace to avoid excessive side-wall refractory erosion as
a result of the proximity of the electrodes to the furnace lining.
Use has been made of a zinc-splash condenser to condense zinc vapour drawn
from a.c. and d.e. fumaces. This approach produces an off-grade zinc, saleable
only at a significant discount. Other processes which do not incorporate a
condensation stage yield a crude zinc oxide with even greater sale price
penalties.
SUMMARY OF THE INVENTION
The invention provides a method of extracting at least zinc from zinc-bearing
material wherein the zinc-bearing material, in a solid or liquid state, and a
reducing agent are fed at a controlled re:ε to a reaction zone in a d.e. arc furnace
including at least molten slag in which at least zinc is volatilized, the volatilized
zinc being collected as metallic zinc in a condenser or being burnt and recovered
as a crude zinc oxide. The zinc condenser is preferably a lead-splash condenser,
but can also be a lead-spray or a surface film-type condenser.
The invention may ce applied to zinc-bearing secondary materials, or to primary
oxidic zinc concentrates.
The zinc-bearing material may be raw but preferably is pretreated to the extent
that the zinc metal product meets Prime Westem grade specifications, or that the
crude zinc oxide product meets the criteria for further downstream processing
in a zinc recovery plant (eg zinc electrowinning plant or ISF).
Appropriate pretreatment depends on the type and chemical composition of the
zinc-bearing material and the required quality of the product, and may include
dehalogenation, drying, calcining, prereduction and premelting. Pretreatment
equipment may include a.c. or d.e. melting furnaces, fluid-bed reactors, rotary
kilns, and washing/filtration equipment for aqueous dehalogenation. Additions
may be required during the pretreatment step in order to promote the removal of
impurities such as S, CI, F, Na, K, Cd and Cu via an aqueous, a gas or a metal
phase. For example additions of sodium carbonate may be necessary for
efficient aqueous dehalogenation.
A pretreatment furnace (melting furnace) may be used, for example to hold liquid
slag from a lead blast-furnace. This lowers the energy requirement of the d.e. arc
furnace (smelting/zinc fuming furnace), and reduces the potential carry-over of
feed material to the lead-splash condenser. A pretreatment furnace may also be
used to melt and desulphurize zinc leach residues or to melt and dehalogenate
EAF dust. The dust may also be subjected to aqueous dehalogenation
whereafter the dust is dried at 500°C to 600°C and is then fed, preferably hot, to
the d.e. arc furnace. Thermal dehalogenation in a rotary kiln, above 700°C, can
also be effected followed by feeding the dust, preferably hot, to the d.e. arc
furnace. The molten zinc-bearing material may be transferred continuously, in
the liquid state, from the pretreatment furnace to the d.e. arc furnace, via a
launder and an underflow weir.
Preferably the feed materials comprise lead blast-furnace slag, ISF slag, zinc
oxide containing EAF dust, zinc leach residues from an electrolytic zinc plant,
primary oxidic zinc concentrates, or combinations of slags, dusts, residues and
concentrates.
Other elements that are present in the zinc-bearing materials such as iron, lead,
copper, silver, molybdenum, cobalt, germanium and gallium may be recovered
simultaneously with the zinc, via a metal, matte or speiss phase tapped from the
pretreatment furnace or from the d.e. arc furnace (zinc fuming furnace), or via a
vapour phase from the pretreatment furnace or from the d.e. arc furnace (zinc
fuming furnace).
The reducing agent may comprise a carbonaceous material such as metallurgical
coke, coal or anthracite, or a metallic reducing agent sucn as metallurgical grade
silicon or ferrosilicon, or combinations of carbonaceous and metallic reducing
agents. Low-grade silicon or ferrosilicon fines, often available from ferro-alloy
plants, could be used. Optiona' a slag fluxing agent such as lime, silica or
dolomite may be used.
The reductant in the d.e. arc furnace should be present in a quantity which is
sufficient to give at least 90% extraction of zinc without excessive reduction of
iron oxides to metallic iron, i.e. less than 100kg iron reduced per 1000kg zinc
bearing feed material and preferably less than 30kg iron per 1000kg zinc bearing
feed material.
The carbonaceous reducing agent must have low levels of moisture and volatiles,
preferably below 0,2% and 3,0% respectively, and the moisture content of the zinc
bearing feed is preferably below 0,1 %, for satisfactory zinc condensing
efficiencies of at least 70%. Preferably feed materials are supplied hot to the d.e.
arc furnace, i.e. at a temperature above 200°C.
The d.e. arc furnace (smelting/zinc fuming furnace) contains normally one but
could have more graphite electrodes mounted in a suitable geometrical
arrangement above the molten bath. Solid or hollow graphite electrodes may be
used. The furnace is interfaced, via a relatively short refractory-lined duct, with
a zinc recovery unit, preferably a lead-splash condenser or a lead-spray
condenser.
Solid zinc-bearing material, reducing agents or fluxes may be fed directly to the
d.e. arc furnace, via a hollow graphite electrode, or through one or more ports
located in a roof of the furnace. Gases such as nitrogen or argon may be
supplied to the fuming fumace via the hollow electrode or through the feed ports
in the roof.
In the case of lead blast-furnace and ISF slag, the molten feed may be transferred
from the pretreatment fumace to the d.e. arc fumace at about 1300°C. Spent slag
may be tapped continuously or in batches from the d.e. arc furnace. The d.e. arc
fumace may be operated so that its tapping temperature is between 1300°C and
1600°C, and preferably above 1400°C.
It has been established that the furnace should operate at a temperature in
excess of 1300°C for satisfactory zinc extraction. On the other hand, above
1500°C there is a diminishing return in terms of zinc extraction, a risk of
unacceptable refractory erosion and contamination of the zinc vapour with
undesirable species from side reactions, such as the generation of magnesium
and manganese vapour and silicon monoxide, at these high temperatures. A
consideration of these factors indicates that a desirable operating temperature
for the zinc fuming furnace is in the range of 1400°C to 1550°C.
The slag basicity ratio, i.e. the (CaO + MgO):SiO, mass ratio, in the fuming
furnace may be greater than 0,8 and is preferably more than 1, to achieve more
than 90% zinc extraction and to minimize the presence of magnetite, which
adversely affects the fumace operation (formation of solid magnetite banks) and
the zinc extraction.
Preferably the fuming furnace is operated at a power flux of at least 0,3 MW/m2
or altematively at a current flux of at least 2kA/m2 to achieve zinc fuming rates of
over 50kg Zn/h/rτr.
The furnace and the condenser should be air tight, and operated at slightly
positive pressure (10 to 50mm water gauge).
The CO:CO2 volume ratio in the fuming fumace should be above 2 and preferably
above 10, to prevent reoxidation of zinc vapour in the free board of the furnace,
in the duct between the furnace and the condenser, or in the condenser.
In the case of EAF dust, the lead, zinc, iron and other oxides in the feed must not
react substantially with CO in the free board of the furnace or above the main
reaction zone which is the surface interface of the molten slag and the reducing
agent. This causes the formation of metallic lead, zinc, iron, etc in the free board,
which is partially carried over into the condenser and can result in the production
of hard zinc (zinc containing more than 1 % iron) instead of Prime Western grade
zinc. Furthermore, the reaction of lead, zinc and iron oxides with CO generates
CO2, providing a low CO:CO2 ratio in the free board, causing the oxidation of zinc
vapour.
Hard zinc formation and zinc oxidation by C02 may to a large extent be prevented
by using an optimized addition of a suitably reactive carbonaceous reducing
agent which is sufficient to generate a gas above the reaction site with a CO:CO2
voiume ratio greater than 10, and in the case when liquid feed is introduced via
an underflow weir, the reaction of lead, zinc and iron oxides with CO in the free
board of the furnace is minimized or even eliminated.
For the treatment of EAF dust, feeding of dust pellets or similar agglomerates,
feeding through the hollow electrode or injection of feed into the molten slag (for
example via a submerged water-cooled lance, a graphite pipe, or a refractory
tuyere), or the use of ferrosilicon as reducing agent may further improve the
recovery of Prime Western grade zinc from the condenser.
BRIEF DESCRIPTION OF THE DRAWINGS
The invention is further described by way of examples with reference to the
accompanying drawings in which:
Figures 1 (a), 1 (b) and 1 (c) respectively illustrate flow sheets of processes
according to the invention for the treatment of lead blast-furnace slags, zinc
leach residues, and EAF dusts; and
Figure 2 is a schematic diagram of a plant for carrying out the method of the
invention for the treatment of lead blast-furnace slags.
DESCRIPTION OF PREFERRED EMBODIMENT
Figures 1(a),1(b) and 1 (c) are substantially self explanatory and are respectively
process flow sheets for the treatment of slags, resiαues, and dusts, according to
the method of the invention.
The process of Figure 1 (a) includes the feeding of lead blast-furnace slags 10,
preferably in liquid form, to a holding or premelting furnace 12. In this furnace
pretreatment takes place for example in order to desulphurize or to remove
copper and cadmium.
Continuous transfer, at about 1300°C, of the molten feed from the furnace 12 to
a d.e. arc fuming furnace 14 is effected via a launder and underflow weir.
A suitable carbonaceous reductant is fed to the smelting furnace and selective
high temperature carbothermic reduction of oxidic zinc is carried out in the
furnace.
The smelting furnace is batch tapped at regular intervals to remove slag, and a
limited quantity of metal, mostly iron, is also tapped intermittently from the
furnace. This alloy can contain valuable elements such as cobalt and could be
processed to recover these elements if economically attractive.
Zinc in the slag in the furnace 14 is volatilized and the zinc vapour is condensed
in a lead splash condenser 16. Following condensation of the zinc the off-gas is
combusted, cooled and passed to atmosphere via a bag-house.
In the process shown in Figure 1 (b) a substantially similar sequence of steps
takes place. This process is intended for the treatment of zinc calcine leach
residues, either from first neutral or final acid leach. The leach residues are
roasted to remove most of the sulphur and then premelted in a furnace 12 to
adjust the composition of the residue, prior to liquid transfer to a fuming furnace
14. Altematively both roasting and melting are done in the fumace 12. Collection
of silver in a bullion phase, from the furnaces 12 and 14, is effected and zinc
vapour is passed, as before, to a lead splash condenser 16.
The process shown in Figure 1(c) includes aqueous dehalogenation of EAF dust
17, drying of dust in a rotary kiln 19, zinc volatilization in a d.e. arc furnace 14,
and condensation of zinc in a lead-splash condenser 16. Altematively
dehalogeneration of pelletized dust may be carried out in a rotary kiln operated
at 750°C to 1000°C.
Figure 2 schematically illustrates a plant 20 according to the invention for the
treatment of lead blast-furnace slag.
The plant includes first and second d.e. arc furnaces 12 and 14 respectively and
a lead-splash condenser 16, numbered with the same reference numerals as the
numerals employed in Figure 1 to indicate like components.
The first furnace 12 is a d.e. arc fumace and a launder 22 extends from a tap hoie
24 on the furnace to an underflow weir 26 on the second d.e. arc furnace 14.
The fumace 12 has a central hollow graphite electrode 28 and a side port 30 for
the feeding of material.
The fumace 14 also has a central hollow graphite electrode 32 and a side port 34
for the feeding of material. Tap points 36 and 38 respectively are provided for the
tapping of slag and metal from the furnace.
Each furnace has a refractory-lined, spray-cooled cylindrical shell, and a water-
cooled roof in the shape of a truncated cone. The flat part of the roof contains
the feed port 30 or 34, and a central entry port for the graphite electrode 28 or 32.
An off -gas port 40 is located at the side of the conical roof of the furnace 12. This
extends to a bag-house.
In the case of the fumace 14 a gas port extends via a short refractory-lined elbow
42 to the lead-splash condenser 16.
The anode in each furnace consists of a number of steel pins vertically
positioned in the hearth refractory and attacheα at their lower ends to a circular
steel plate which, via radially extending arms, is linked to the furnace shell and
to the anode busbars.
The condenser 16 includes a condensing chamber with at least a single impeller
44, although at least up to eight similar impellers may be used, a lead circulation
pump or pumps, a cooling launder with two or more immersible banks of cooling
pins, a flux bath and a zinc separation bath. The construction of the condenser
is substantially conventional in accordance with Imperial Smelting Furnace
practise, and for this reason is not further described herein. A lead-spray
condenser or a surface film-type condenser may also be used.
A gas handling system 46 is provided to treat gas drawn from the condenser.
The system includes a refractory-lined combustion chamber 48, water-cooled
ducting 50, a radiant gas cooler 52 and a reverse-pulse bag filter 54 the outlet of
which is connected to a stack 56.
The process variables of major interest for the fuming furnace 14 are the
reductant addition and the operating temperature. Carbon additions are
calculated to give at least 90% extraction of zinc without excessive reduction of
iron. This facilitates the minimization of coke usage, energy consumption and
gas handling, since minimal volumes of CO are generated. Carbon levels must
however be sufficient to ensure a CO: CO2 ratio such that the zinc does not re-
oxidise before reaching the condenser. Theoretical considerations indicate that
about 30kg of coke are needed per 1000kg lead blast-furnace slag and a minimum
temperature of about 1350°C is required for 90% zinc extraction. Above 1500°C
there is a diminishing return in terms of zinc extraction, a risk of unacceptable
refractory erosion and contamination of the fume with undesirable species.
Further, the operating temperature must sustain a gas entry temperature to the
condenser of at least 1000°C to minimize back-reaction of zinc to zinc oxide. Any
iron that is produced is not carbon saturated and cannot be tapped at 1350°C.
A consideration of these factors indicates that a desirable operating temperature
is in the range of from 1400°C to 1550°C. An optimum region of operation of the
fuming fumace is obtained for coke additions between 2% and 5% by mass of the
lead blast-furnace slag.
In use of the plant 20 granular lead blast furnace slag is supplied from a feed
system 58 to the first d.e. arc furnace 12. Hot slag is fed continuously from the
premelter, via the transfer launder 22 and underflow weir 26 into the second d.e.
arc furnace 14. Metallurgical coke is fed to the fuming furnace 14 through the
feed port 34 or via the hollow electrode 32. According to the type of lead-blast
fumace slag, and in accordance with the considerations referred to hereinbefore,
coke is added at the rate of approximately 30 kg per 1000kg of lead blast-furnace
slag.
An altemative method of operation is to feed solid lead blast-furnace slag directly
to the fuming furnace through the hollow electrode 32 or via the port 34 located
in the roof. The premelter fumace is in that case switched off, and the underflow
weir is closed with refractories.
The zinc and lead oxides in the slag are reduced to their metals and volatilized
in the fuming furnace 14. Residual or spent slag is tapped from the fuming
furnace at regular intervals through the tap point 36. Metal, primarily iron, is
tapped from the furnace 14, as necessary, through the tap point 38.
The furnace 14 operates at near atmospheric pressure (less than 200mm water gauge and preferably less than 50mm water gauge but not less than 20mm) and delivers a gas to the elbow 42 and hence to the condenser 44 which consists mainly of zinc vapour, carbon monoxide, carbon dioxide and nitrogen. Zinc vapour is condensed in the condenser and molten zinc is tapped from the condenser, as required.
A cooling launder 60 underlies the condenser 44. Drosses are regularly removed from the cooling launder as they are generated. Gases and dust passing through the condenser are burnt in the combustion chamber 48 and are cleaned in the bag filter 54. Fumes are removed continuously from the bag filter. Gases emitted by the bag filter are monitored for solids content prior to discharge to atmosphere from the stack 56.
To control the smelting operation the theoretical energy requirements in kilowatt hours for each 1000kg of lead blast-furnace slag to be treated, are calculated for each furnace. Energy losses are measured using cooling flow rates and temperatures. The operating power levels of the furnaces are determined for selected feed rates. The main control parameters for running the furnaces are the tapping temperatures, which are measured with an optical pyrometer, and the content of zinc in the tapped slags . The designed tapping temperatures of the premelter and fuming furnaces are respectively in the region of 1300°C and 1450°C.
These temperatures are selected to minimize zinc losses in the premelter, to ensure sufficient fluidity, and to achieve a high degree of zinc extraction.
The general rule for the operation of the condenser and its cooling system is based on controlling temperature at 500°C ± 50°C. The lead pump speed is increased or decreased when the pump sump temperature is too high or low. If the return launder temperature is too high or low the cooling pins are immersed or withdrawn. Auxiliary fuel burners are used when the launder temperature still remains too low. The temperature of the gas entering the condenser is monitored. Control parameters other than temperature are pressure, rotor speed, and rotor immersion. The pressure in the condenser is kept slightly positive to avoid the ingress of air which could oxidise the zinc vapour and cause accretions .
It has been found that the plant 20 is capable of producing Prime Western grade zinc which is saleable at attractive commercial rates. The final slag from the furnace 14 consistently meets environmental leach criteria and discard slags are environmentally acceptable for disposal.
The process can be operated over a wide range of capacities to treat a broad spectrum of oxidic zinc containing materials.
The use of a d.e. arc furnace, when compared to a three- phase a.c. slag resistance furnace, offers reduced electrode consumption, symmetrical heat distribution and a high degree of operational control. Since the graphite electrode is not in contact with the molten charge accurate carbon additions can be made to the melt. The arc furnace generates most of its heat between the electrode tip and the bath and consequently the power input is not restricted by the electrical conductivity of the bath.
EXAMPLES OF THE INVENTION
EXAMPLE 1 - PROCESSING OF LEAD BLAST-FURNACE SLAG
Referring to Figure 1(a), the pilot-plant equipment consisted of two d.e. arc furnaces, a lead-splash condenser, a combustion chamber and a gas-cleaning system. Granular lead blast-furnace slag was premelted in the first d.e. arc furnace (premelter) and hot slag was fed continuously from the premelter, via a transfer launder and an underflow weir, into the second d.e. arc furnace (zinc fuming furnace) . The feed rate of lead blast-furnace slag was about 1500kg per hour. Metallurgical coke was also fed to the fuming furnace, at a rate of 30kg per 1000kg of lead blast-furnace slag, via a feed port located in the roof. The premelter was typically operated at 650kW (200 V, 3 , 2kA) , and the zinc fuming furnace was run at about 700kW (175 V, 4 kA) . Residual or spent slag was tapped from the furnace when about 2500kg of lead blast-furnace slag was fed to the premelter. During certain periods of the smelting campaign, the premelter was switched off, the underflow was closed with refractories, and granular lead blast-furnace slag was fed directly to the fuming furnace. In that case the fuming furnace was operated at power levels of about 1200kW. In total about 600 metric tons of lead blast-furnace slag was processed through the pilot- plant.
The lead blast-furnace slag contained 10,9% ZnO, 2,5 % PbO, 23,2% FeO, 26,8% Si02ι , 21,6% CaO, 4,8% MgO and 4,0% A1203.
The minor constituents of key interest with regard to the production of Prime Western grade zinc were copper at 0,4%, arsenic at 0,3%, and cadmium at 70ppm. The metallurgical coke contained 76,5% fixed carbon.
Typical analyses of products when hot slag transfer was employed are shown in Table 1.
Table 1 - Typical Analyses of Products
Non-Metallic Premelter Slag Fuming-furnace Products, mass% Slag
ZnO 10.3 1.8
PbO 1.6 0.1
FeO 23.3 21.0
SiO, 27.9 26.4
CaO 21.9 26.4
MgO 5.0 7.4
Al-A 4.2 5.1
CuO 0.3 0.1
Metallic Products, Premelter Fuming-furnace Zinc Metal mass% Metal Metal
Zn 0.3 0.1 98.4
Pb 9.5 0.6 1.3
Fe 16.4 87.1 0.03
Cu 42.1 4.5 0.18
As 29.2 4.6 0.06
Cd - - 0.02
When comparing the analyses of the premelter slag and the feed lead blast¬
furnace slag, it can be seen that a great part of the lead and copper were removed
from the lead blast-furnace slag during premelting. About 40% of the lead input
reported to the fume and metal of the premelter in a ratio of approximately 1 to
3. Also, about 40% of the copper was extracted in the premelter and mainly
passed into the premelter metal. Most of the cadmium reported to the fume, and
some arsenic was removed as a speiss phase in the premelter. More copper and
arsenic were removed via a metal/speiss phase of the fuming furnace.
The levels of ZnO and PbO in the slags tapped from the fuming furnace were
below 2% and 0,2% respectively when the fumace was operated such that tapping
temperatures of between 1400°C and 1500°C were achieved (temperatures of
slags flowing from the furnaces wert measured with an optical pyrometer.)
Samples of residual slags were submitted for toxicity leaching tests and were
found to conform to US EPA regulations for disposal. In most cases, the zinc
metal product met Prime Westem grade specifications. Sometimes the lead and
iron levels were somewhat above the specified maxima. This zinc could have
been liquidated to yield Prime Western grade zinc, which is the usual industrial
practice. Maximum levels of lead, copper, iron and cadmium in Prime Western
grade zinc are 1 ,4%, 0,20%, 0,05% and 0,20% respectively. Zinc extractions and
zinc condensing efficiencies were calculated as follows:
Zn in feed - Zn in slag % Zn extraction = x 100
Zn in feed
Zn in condensed metal
% Zn condensing efficiency = x 100
Zn in vapour
Zn in vapour being defined as: Zn in feed - Zn in slag
Zinc extractions and zinc condensing efficiencies were calculated this way for
selected periods of fairly consistent operation, during which about 120t of lead
blast-furnace slag was processed. The zinc extractions varied between 80% and
85%, while the condensing efficiencies were between 70% and 80%.
Zinc fuming rates were calculated for a period during which 60t of cold lead blast¬
furnace slag was fed at a relatively high feed rate of 2000kg per hour. The
amount of zinc fumed was defined as the zinc in the slag fed minus the zinc in the
residual slag. Zinc fuming rates of 120kg/h to 180kg/h were achieved, wnich
correspond with zinc volatilization fluxes of 40kg/h/m2 to 60 kg/h/m2 (based on a
molten bath area of 3m2).
EXAMPLE 2 - PROCESSING OF EAF DUST
Referring to Figure 1(c) about 25t of EAF dust were dehalogenated, dried and fed
to the d.e. arc fumace. During aqueous dehalogenation, the chlorine level in the
dust was reduced from about 2% to 0,2%. It is known that high levels of
halogens, especially chlorine, interfere with the proper operation of the
condenser, due to the formation of large quantities of dross. The dehalogenated
dust was dried in a rotary kiln at 500°C to 600°C to reduce its water content to
below 0,1%. Previous testwork with dehalogenated dust, containing about 0.5%
moisture, resulted in the formation of excessive amounts of "toothpaste-like"
dross, and consequently no metallic zinc was recovered from the condenser. The
dehalogenated and dried EAF dust was fed to the d.e. arc furnace together with
metallurgical coke, via the feed port located in the roof of the furnace. The coke
addition was 95kg per 1000kg of dust. The furnace was typically operated at
1270kW (200 V, 6,35KA). Dust was fed at a rate of about 1000kg/h and tapping of
spent slag was done intermittently, each time when about 3000kg dust was
supplied to the fumace. The average slag tapping temperature was 1465°C. The
dehalogenated and dried dust contained 24,6% ZnO, 2,3% PbO, 44,7% Fe2O3, 4,4%
SiO2, 7,7% CaO, 3,8% MgO, 1 ,0% AI2O3 and 3,3% MnO. The spent slag contained
on average 1,6% ZnO and the zinc extraction was about 96%. In total 4097kg zinc
was tapped from the condenser. The zinc condensing efficiency was about 80%.
Again the slags produced met US EPA regulations for disposal and, in most
cases, the zinc metal conformed with Prime Western grade specifications. Thp
average rate of zinc fuming per area of molten bath was 120kg Zn/h/m2.