Patent Application
20230137480
The present disclosure pertains to the technical field of steelmaking, specifically relating to a new hydrometallurgical method for recovering valuable metals from steelmaking waste, and it more specifically relates to a new hydrometallurgical method for extracting and recovering valuable metals from electric arc furnace dust produced by the steelmaking industry (steelworks) worldwide, such as zinc, lead, silver, iron and calcium, in the form of industrial products, from treating complex oxides.
The known electric arc furnaces used for producing steel are fed with industrial scrap, and this scrap is a complex consisting of metallic compounds from the chemical point of view, as it typically has as constituents Fe, Zn, Pb, Mg, Mn, Cl, Ca, percentagewise; Cr, Cd, Ag, P, Sn, in parts per million (ppm); and furthermore several chemical elements in parts per billion (ppb).
The average or standard chemical composition of electric arc dust is the following:
Electric arc furnace dust is generated inside the electric arc furnace at temperatures higher than 1,300° C.
Depending on the geographic location, electric arc furnace dust chemical composition percentage varies, because steels produced before being converted to scrap have had various uses and various corrosion protection systems (galvanising, paints, plastics) or a component of an alloy (chromium, nickel, etc.) which allow it to have special properties, suited to each specific local need local specific. The content of zinc, which is in the ranges of 12% to 35%, essentially varies.
The generation of electric arc furnace dust has a range which varies from 11 kg to 17 kg per metric ton of steel produced, which indicates that per million metric tons of steel produced by the electric arc furnaces, between 11,000 and 17,000 annual metric tons of electric arc furnace dust are generated. The lifetimes of steelworks are very long and, for that reason, over time, this waste becomes considerable in volume, but also risky because electric arc furnace dust is considered hazardous for the environment and for human and animal health due to the presence of some toxic elements such as lead, cadmium, arsenic, mercury among others.
Existing pyrometallurgical and hydrometallurgical methods for recovering or extracting metals such as zinc, lead, silver, iron and calcium of electric arc furnace dust cannot prevent the generation of solid waste with a hazardous content, so it is not possible, with the current state of the art, to recover the aforementioned metals without preventing industrial landfills and the constant risk of environmental pollution and health hazards.
Moreover, in the current state of the art there is no pyrometallurgical method, hydrometallurgical method, or a combination of both, which recovers simultaneously and in a single method all the valuable content of zinc, lead, silver, iron and calcium from electric arc furnace dust, moreover converting the non-metallic contents of electric arc furnace dust into commercial final products, without generating solid waste or liquid effluents.
With respect to pyrometallurgical methods, the Waelz kiln process, which is the most widely used process to recover zinc from electric arc furnace dust, takes zinc to the gas phase by using a high temperature (between 1,000° C. and 1,500° C.), surpassing the boiling point of zinc, using metallurgical coal (coke) as a reducer, producing zinc oxide (ZnO).
This process does not recover all the metals, such as the iron lost in the process slag (Waelz slag). Additionally, other metals such as calcium and aluminium are lost in this slag. This process obtains only the intermediate product zinc oxide (Waelz oxide) which still needs to go through a refinery to obtain final zinc.
The Waelz kiln process, in general, has the drawback of producing intermediate metallurgical products because the zinc oxide produced requires subsequent metallurgical treatment, does not recover iron, generates slag, and uses a great deal of energy in the process. Moreover, this method is not designed to be implemented in small steelmaking plants which generate less than 20,000 metric tons of electric arc furnace dust per year.
The Waelz kiln process needs an order of magnitude of 100,000 metric tons of electric arc furnace dust per year, a volume that far exceeds the annual generation of this waste in several steelworks located in different countries, which amounts to about 30,000 metric tons per year.
Other pyrometallurgical methods similar to the Waelz kiln process, such as, for example, Primus, PIZO, ESRF, Mitsumi, electrothermal furnace, flame reactor, daido furnace; produce, in general, the same product as the Waelz kiln process, in other words, crude zinc oxide (CZO), which requires subsequent treatments such as the IS (imperial smelting) process or conventional electrodeposition methods to obtain electrolytic zinc.
In general, existing pyrometallurgical methods in the state of the art are methods that produce intermediate metallurgical products that need subsequent metallurgical methods so as to be able to obtain and use on an industrial level the generated zinc. Moreover, they do not recover iron and generate solid waste, such as slag, containing most of the non-metallic components and several hazardous metals, in addition to liquid effluents which need to be processed in treatment plants.
With respect to existing hydrometallurgical methods in the state of the art, acid leaching or caustic leaching are known, which also produce zinc oxides (ZnO) as intermediate metallurgical products which subsequently need electrodeposition methods to obtain zinc. These methods do not recover iron and use chemical agents (acids and bases) for subsequent selective zinc leaching methods.
There are also the EZINEX, ZINCEX, and RECUPAC leaching methods, which use chemicals, based on acidic chlorine, sulphuric, ammonia-based or organic chemical solutions, which are a variation of those mentioned above. Said methods, as in the preceding methods, have the same limitations of producing intermediate metallurgical products and do not allow for the simultaneous recovery of all the heavy metals (Cd, As, Sb). Moreover, they produce solid waste and liquid effluents which need to be processed in treatment plants.
The hydrometallurgical methods mentioned in the above paragraph, with respect to leaching, show advantages and drawbacks with respect to acid or alkaline leaching. While high dissolution kinetics and reagent availability are desirable, it is necessary to also deal with low selectivity, which is of high importance in electric arc furnace dust due to the presence of other chemical elements.
Due essentially to the fact that both types of leaching cannot efficiently break up ferrites (Fe2O3.ZnO) with chemicals in solution, which inevitably produces zinc losses in the insoluble iron and the presence of iron in zinc solutions, and moreover compromises the quality of the solutions e insoluble elements and produces a great deal of complexity with the presence of other metals present (Cd, As, Sb).
Consequently, both types of leaching do not recover the iron, and its insoluble elements constitute industrial waste; and, moreover, they are not able to recover valuable elements simultaneously (Zn, Fe, Pb, Ag), and also lack the capability to completely remove hazardous constituents (As, Sb, Cd, Hg, Co, etc.).
It should be noted that hydrometallurgical methods using sulphuric acid, hydrochloric acid, nitric acid, ammonia, sodium hydroxide, ammonium chloride, calcium chloride, as a leachate, organic compounds as extractive media, high-pressure leaching generating method waste (insoluble elements or precipitates) or liquid effluents (wastewater), is unrelated to the new method developed.
The new hydrometallurgical method developed is capable of treating any type of electric arc dust and recovers, by simultaneously extracting zinc, lead, silver, iron and calcium, in the form of industrial products; zinc as zinc sulphate or zinc cathodes; lead and silver as a concentrate of lead and silver; iron as reduced elemental iron for return to the electric arc furnace; and, lastly, calcium as gypsum.
Moreover, no solid waste or liquid effluents are generated with the new method, which is an important advantage as electric arc furnace dust is considered a hazardous waste that increases each year. Industrial metals thereby return to the industry, and the need for continuous and growing landfills for waste is eliminated, mitigating the potential risk to the environment and human and animal health.
The synergy achieved with the invented method is due to the integration of its different steps, a diagram of which is detailed in
Unlike the pyrometallurgical and hydrometallurgical methods present in the state of the art and used for treating and recovering materials from the dust of a steelworks electric arc furnace, the invented method has been developed based on the consideration that electric arc furnace dust is a mixture of complex oxides and not solid solutions such as (M1/M2)xOy, but rather agglomerations such as M1O.M2xOy (ferrites), particle sizes in the range of 0.17 micra to 6.76 micra, are very fine dust, have a large surface area, are agglomerated naturally in a very easy manner. The alkali and alkaline elements are in balance with the halogen elements. An important additional aspect is that the average diameter D50 is 0.62 micra, which makes the powder very chemically reactive with high reaction kinetics under certain circumstances.
The dust is generated inside the electric arc furnace at temperatures higher than 1,300° C., and many of the metals present such as Zn, Pb, Cd, Co, etc., are in the gaseous state and are extracted by gas capture systems. In addition, the balance of the content of molten steel forms a liquid slag in the presence of Fe, Ca, Si, etc. During the blowing process inside the furnace, fine particles of slag and even steel (very fine droplets) are driven through the gas capture systems.
Inside the capture tubes and pipelines, the whole (gases and particles) is cooled on the way, due to the drop in temperature to about 60° C., and all the metallic gases pass to the solid state, the integrity of which forms what is referred to as electric arc furnace dust.
A fundamental aspect, due to the genesis of the formation thereof inside the electric arc furnace, which is of an oxidising condition due to the addition of gaseous oxygen to the furnace, is that this dust is made up of complex oxides of the forms MxOy/MO.MxOy, where M is the metal (Fe, Pb, Zn, etc.) and O is oxygen.
The alkalis, alkalines and halogens present in the scrap are added to this complex, and when they are cooled, they are present in their stable thermodynamic forms under normal conditions. In general, particles having a larger diameter contain more iron.
The new hydrometallurgical method developed for the treatment of electric arc furnace dust are shown schematically in
The purpose of this step is to homogenise and identify the chemical composition of electric arc furnace dust, in other words, the content of zinc, iron, Cl, Pb, Ca, Ag, Cd and Hg in order to know the valuable metals present, of the elements of risk for metallurgical control and balance in the method.
Insofar as electric arc furnace dust, in dry conditions, is very fine, it tends to form gray layers of different sizes, so it is necessary to homogenise them, this action being performed in an encapsulated mixture which produces the homogeneous mixture making up the homogeneous electric arc dust stock, which is stored in encapsulated hoppers preventing the leakage thereof.
The homogeneous electric arc dust stock will enter the method after the chemical analysis thereof has been performed.
The most important aspect is to determine the zinc (17.50% to 19.50%) and iron (17.26% to 28.26%) grade, in addition to knowing with certainty the content of Cl, Pb, Ca, Ag, Cd and Hg. Therefore, this provides knowledge with the highest possible level of certainty of the valuable metals and elements of risk for metallurgical control and balance in the method.
The electric arc dust (hereinafter, dust) contains halogens (CI) and, consequently, alkalis and alkalines, which elements must be removed from the oxide complex because they are detrimental to the following steps of the method.
For this purpose, the homogenised dust is transported from the encapsulated hoppers to the scrubbing tanks, which are encapsulated tanks so as to prevent the possibility of dust leaking and to send the water vapours to the evaporation and condensation systems, having with a suction system which allows operating at a negative a pressure, 0.97 atmospheres.
The water comes from the condensed water feed system, has an absence of dissolved gases and salts, enters at 80° C., with a mass ratio of 4 to 1. The absence of salts and gases dissolved in the water and the operating temperature confer to the water better properties for dissolving the complexes of Cl, Na, K, Mg, Ca, Ba present in the electric arc furnace dust.
The scrubbing tanks maintain a constant suspension by means of mechanical agitation for 15 minutes in the first part of the scrubbing, and the suspension seeks contact among all the dust particles and the hot condensed water. This phase produces a liquid loaded with the already mentioned soluble complexes, which is sent to a liquid purification unit (DETOX) of the method by means of the liquid/pulp decanting system. The pulp enters a second scrubbing time of 10 minutes, with water having the same characteristics of the method, and the objective is to force a second dissolution of halogens, alkalis, alkalines. Similarly, the decanting system sends the liquid to the liquid purification system, and the previously filtered solids pass to the following phase.
There is obtained a reduction of Cl of more than 95%, consequently obtaining very high reductions of Na, Mg, Ba. A reduction of 17% by weight of the initial content of dust is obtained in general.
Due to the corrosive nature of the liquids of this method, the agitation systems of the tanks and the line pipes have an anticorrosive coating. The liquid and pulp impulsion systems are carried out by means of peristaltic pumps.
Accordingly, the filtered solids have, on average, 10% humidity, are insoluble solids, and are almost entirely made up of complex metal oxides.
The solid from the scrubbing phase enters the extensive sulphation phase. This consists of changing the chemical nature of the oxides to that of simple and complex sulphates in total form. In other words, going from a complex insoluble oxide integrity to a sulphate integrity. This step does not exist in any method present in the state of the art used for recovering metals from electric arc furnace dust, it consists of adding sulphuric acid to the solids of the scrubbing phase for the purpose of changing the chemical nature of the electric arc furnace dust from complex oxide compounds to a group of simple and complex reaction sulphates.
To generate this reaction, the mixture, by weight, of one part dust to 0.87 parts pure acid is performed in a reactor specially designed for this phase. The reactor is a continuous mixing reactor and a paste is generated in same; the reaction is exothermic and carried out in a range of 120° C. to 150° C., to which there is added water at 80° C. from the condensed water generation system, only in order to replace the water losses due to evaporation in the reaction and maintain the plastic condition of the paste.
This phase lasts for 20 minutes, and the paste generated is very dark, homogeneous and hot; it is important that it is mixed vigorously and constantly, because the paste formed is very viscous, and the complete chemical sulphation reaction and depletion of sulphuric acid must be obtained. This is a very important aspect since the method consumes all the acid, generating no free acid solutions in the method.
This phase does not produce liquids in any form and produces water vapour in a very limited form and very little acid mist, where these vapours and gases go to SO3 recovery systems and re-enter the sulphuric acid stock system of the closed circuit method.
Essentially, in this step, the oxide molecules are broken down, replacing the oxygen in the molecules with the typical compound SO4, which is an important aspect of the method and radically different from all existing methods, because the treatment of complex oxides is inefficient in the leaching methods with chemical reagents.
In this step, the chemical nature of the electric arc furnace dust changes completely, going from a complex oxide compound to a group of sulphates from a simple and complete reaction as the method continues until the reaction ends (complete consumption of the reagent). This is a turning point in the state of the art, because hereinafter, the nature of the entire method is different from all that exists because the material in the method has another chemical nature, that is, it is a sulphated mixture of electric arc furnace dust.
The sulphated mixture of electric arc furnace dust is dried in the same sulphation reactor, which continues to operate under continuous mixing, with the temperature of the reactor increasing to 200° C., and the paste proceeds to dry, losing all the water by evaporation, forming dark grey agglomerated crystals.
This step lasts for about 10 minutes and has two important objectives: first, to remove water in order to prevent thermal shock in the next step, and second, to ensure the complete reaction of the new sulfide complex.
The reactor is still encapsulated. It is theoretically possible for a minimum amount of SO3 to be present, the reactor being in line with of SO3 capture and gas cleaning systems.
The purpose of this step is to keep a part of the complex soluble (essentially zinc as zinc sulphate), and one part is converted to an insoluble part (essentially iron as hematite).
After the drying phase, the temperature of the reactor is increased to a working of 680° C. to 720° C., depending on the concentration of Zn, Fe, Pb, in the paste. The mechanical mixing is kept constant such that the crystals formed in the drying phase can increase the temperature homogeneously. The reaction time is about 2 hours.
In this phase, the thermolysis reaction (thermal decomposition) of iron sulphate takes place as the main reaction, which produces the formation of hematite (Fe2O3), with the corresponding generation of SO2 and O2, according to the reaction:
4FeSO4=2Fe2O3+O2+4SO2.
The reaction is carried out at normal pressure. The generated gases are sent to the gas cleaning and SO2 capture system, which is added to the sulphuric acid stock of the method. In addition to the thermal decomposition reaction of the iron, where the oxides with lower formation energy in relation to iron are also decomposed, as in the case of Pb, Ag, Si, Mn, P, Sn, Cd, Ni, Bi, etc.
The group of compounds present in majority form that do not decompose are of a higher energy of hematite formation, such as Zn, Ca and other minority compounds that maintain their new sulphate nature.
What has been achieved at this stage is of major importance in the method, that is, the hematite formed and all the additional oxides formed are insoluble, while, in contrast, zinc in the form of sulphate has a high solubility, which is sent to an encapsulated hopper where it is cooled to 70° C.
The purpose of this step is to obtain two new complexes, one being liquid with a large amount of zinc and the other one being insoluble and essentially made up of hematite, gypsum and lead oxides plus other minor oxides.
The leaching time is about 1 hour to 1 hour and 30 minutes, is carried out in encapsulated tanks with an evaporation water vapour extraction system, and leaching is carried out at 260 RPM and 70° C. The tanks have an anticorrosive coating, and the solutions are moved with peristaltic pumps.
The solid/liquid volumetric ratio is 1 to 3.6, where the water comes from the condensed water system and is a countercurrent system, such that the solids are solubilised and progressively lose zinc, whereas the solution progressively increases in terms of the content of zinc and, to a lesser extent, in terms of the content of Mn and Ca.
The leachate is condensed water, without the addition of any type of reactive chemical, where the objective of this phase is not to leave soluble elements in the solid essentially made up of hematite, and for this reason leaching is performed with the addition of water in order to replace water losses due to evaporation.
The aqueous leaching phase is very efficient and produces the very efficient extraction of zinc, producing a solution which, on average, tests 56 g of Zn per litre, with a small amount of other components, where the solids are, for the most part, hematite and other metal oxides such as calcium and lead oxides.
The solids are very fine, and a high-pressure pump filtration system is necessary for an efficient separation of the leached solution.
At this point, there are two new complexes, one being liquid with a large amount of zinc and the other one essentially made up of hematite, gypsum and lead oxides plus other minor oxides.
The solids are sent to the flotation method, and the liquids are sent to the evaporation-crystallisation/electrodeposition system, where it is essential to keep the temperature of the liquid flow at 70° C., which is moved by peristaltic impulse.
The purpose of this step is to obtain zinc, in the desired form, as the final product, preferably as zinc sulphate or as zinc cathodes. If necessary, it is possible to purify the solution with the addition of zinc dust, and the obtained sludge is sent to the sludge system.
In a first desired form, shown in
The evaporation method prevents the metal and non-metal ions from leaving the solution, and the water vapours do not contain ions. As the volume of liquid water is reduced, the concentration of zinc increases.
For producing zinc sulphate, which gives the highest added value, an oversaturated solution of 1,800 g Zn/L is produced, which solution enters the crystallisation method in steps and in countercurrent in the conventional encapsulated reactor with a temperature delta of 40° C. Crystallisation in steps is one of the most efficient forms of purification available. The first crystals are very pure, and the last crystals that are formed are less pure. This finally produces the crystalliser in a mixture of all these crystals, yielding a typical composition shown in Table 4. Zinc sulphate is widely used in the mining industry as a flotation reagent for polymetallic ores.
In a second desired form, to obtain zinc cathodes shown in
This purpose of this method is to separate the hematite from lead oxides and various metal oxides present in a very small amount, for example, cadmium, nickel, arsenic.
The solids coming from the leaching phase are insoluble under normal conditions, with a majority composition of hematite and with the minority presence of lead oxides, calcium sulphate (gypsum) and an important presence of silver; By using the flotation properties of the lead and silver oxides in the presence of hematite (absence of sulfides), foam flotation operations produce excellent separation, producing an ore concentrate of commercial-quality lead-silver the typical composition of which is reported in Table 2. This oxide ore flotation method also concentrates many of the heavy metals. However, it additionally cleans the hematite of this content.
Due to the ultrafine nature of the particles of all the components, it is a virtually artisanal operation that takes about two hours, the time needed to favour the entrainment of lead oxides and heavy metal oxides. The flotation reagents used are those from the family of sodium sulfide (Na2S), in the presence of sodium carbonate and sodium silicate, with the use of xanthate and pine oil. Additionally, the hematite needs starch as a depressant. The composition of the typical concentrate obtained is shown in Table 2 below.
The purpose of this step is to separate gypsum from the hematite.
The hematite still contains gypsum (CaSO4.2H2O); due to the need to use reduced hematite (FeO) as electric arc furnace feed material, it is necessary to remove the gypsum, for which magnetic separation is used, taking advantage of the wide delta of magnetic susceptibility existing between hematite (35×103 SI) and gypsum (−0.11×103 SI).
However, magnetic separation is also a unit operation which requires a great deal of supervision so as to prevent the entrainment of gypsum fines in the hematite, and it is done at low speeds between 0.7 feet/min and 0.8 feet/min of the magnetic separator and at a magnetic flux density between 19,000 gauss and 21,000 gauss;
This operation uses magnetic separation steps from lower to higher flux density, obtaining pre-concentrates of hematite which are subsequently mixed in order to be sent to the hematite reduction method in their conventional form to produce reduced iron, which is agglomerated due to its fine nature to finally be returned to the electric arc furnace (EAF).
10. SO3/SO2 Recovery System:
The method has a conventional catalytic system for SO3/SO2 recovery, capturing gases in diluted solutions of H2SO4 (at 70%) in the presence of catalysts, the capture solution is added to the sulphuric acid stock of the method. The commercial system has forced air heat sinks and is encapsulated.
The gases of the system are essentially air, O2 and CO2; however, given the ultrafine nature of the dust, a small portion of said dust is entrained by the streams of said gases, which is why it is necessary to have a gas scrubbing system that retains the particles.
The environmental efficiency of the method with respect to the gaseous phase depends on the efficiency of this system, whereby it is a countercurrent cleaning system forcing the gas and particles to pass through water mist and sprays under countercurrent (1.2 m3 per m3 of gas), repeatedly, with several scrubbing columns and coils, The gas passes through ultrafine filters before leaving the method so as to ensure that there is no loss of solids.
The solids are captured as sludge which is, in essence, electric arc furnace dust or calcine from the thermolysis method; this sludge is sent to the sludge collection system, and the liquid from the gas scrubbing method is sent to the liquid purification unit by impulsion by peristaltic pumps.
This step prevents the loss of dust because of its ultrafine nature and consists of handling sludge formed by these particles. All the reactors and flow systems are encapsulated and capture fugitive particles which, because the various systems are in closed circuit, produce sludge. The latter is sent to this step of the method.
The water vapour also entrains a minimum portion of particles, which are captured in the vacuum evaporation system and sent to the sludge collector.
This sludge is filtered by two twin pumps, the first with a 5-micron membrane and the second with a 2.5-micron membrane; said membranes are made of phenolic resin. This operation is carried out at 3.5 bar of pressure.
The obtained solids are added to the concentrate of lead-silver, thereby preventing the significant generation of waste. This operation does not affect the quality of the concentrate.
The resulting liquid has an ionic content and is therefore sent to the liquid purification system.
This step consists of a unit which receives liquid flows containing anions, cations, suspension of ultrafine solid particles from the dust scrubbing method, gas scrubbing method, sludge collector and liquid flows of the flotation phase (concentrate and tailings) and eventually from the cleaning and maintenance method for any reactor.
It consists of the water decontamination method, and consists of a chemical ion separation system, high-pressure membrane filtration, vacuum evaporation, chemical precipitation, returning the clean water to the industrial condensed water method, crystallising the contaminants. It is equipped with technology available on the market.
The solids are integrated (precipitates, sludge and crystals), homogenised and added to the concentrate of lead-silver for the respective marketing thereof.
A particular feature of the present method is that it is designed for the steelmaking operator, as the new method can be installed in the same steelmaking plant, very close to the electric arc furnace, and can even share synergies with the steel plant as it is encapsulated and not susceptible to experiencing disruptions due to the atmosphere of the operations, and the operations of the method do not disrupt the operations of the steel plant.
Due to the way the chemical nature of the complex oxides (electric arc furnace dust) changes to a sulfide complex, the hazards associated with the generation of fugitive cadmium and hexavalent chromium salts are eliminated, and the hydrometallurgical problem of low zinc and iron recovery is solved. Consequently, hydrometallurgy is made easier and more environmentally friendly, as condensed water is used as a leachate, the condensed water being continuously regenerated by vacuum evaporation systems without generating effluents. The method consumes a minimum of water (only the zinc sulphate hydration water, the calcium sulphate hydration water, the humidity of the concentrate of lead-silver and evaporation are lost) which is added as a replacement.
No metals in the form of gas or molten solutions or elements are handled, and the method uses in its reactions solids, liquids and ions that are selectively separated. The method defines the manner of extracting hazardous metals (Pb, Cd, As, Co, etc.), and converting them to a final metallurgical product (concentrate of Pb—Ag), where this aspect is an important contribution as it sends heavy metals back to the lead treatment smelters, which are the most suitable circuits and methods for treating and recovering heavy or toxic metals.
The sludge generated in the various steps (gas cleaning, return water filtration sludge, air cleaning dust) are mixed with the concentrate of lead, adding them to this product. The method does not generate solid waste. Moreover, if necessary, this concentrate can be mixed with concentrates of higher grade lead in order to fulfil the commercial grades required by the industry.
The method emits only CO2, as a result of the need to produce heat for the thermolysis reactor, due to the use of NGV/LPG to heat the reactor; the combustion gases are also used for the purification systems and maintenance of the reaction temperatures of the various solutions of the method and the evaporation systems at temperatures above normal conditions and negative pressure. It should be mentioned that electric systems such as motors, valves, actuators, sensors, lighting and contingency systems operate based on electrical energy (440V, 60 Hz) supplied by the public system; it furthermore has a generator set which, in the case of contingency, provides energy for the emergency system (safe shutdown of operations) and lighting.
One aspect of special attention is that all reactors and solution delivery systems are coated with resin and polymer films with high corrosion resistance and working temperature ranges of 100° C. on average.
Gas delivery systems are developed with conventional systems for corrosive hot gas flows in the metallurgical industry (sulphide smelters and steelworks).
The method, on average, is as shown in Table 3, has the following mass behaviour with respect to the products which are obtained from 1 MT of electric arc furnace dust.
The positive weight differences are due to the addition of sulphur and the hydration water; 7H2O in the case of zinc sulphate and 2H2O in the case of calcium sulphate.
With respect to the metallurgical recoveries of the valuable elements of the method, which are essentially zinc, iron, lead/silver, these can be seen in Table 4.
The payable zinc content is, on average, 97%, being contained in zinc sulphate, as the content present in the concentrate of lead-silver and in gypsum are not payable.
The concentrate of lead and silver is, in general, a concentrate considered dirty or borderline, because it receives sludge from the various purification or cleaning methods. The payable section is 87% for lead and 66% for silver, with respect to the content at the head, analysed in Table 1 and the quality reported in Table 2.
With respect to the reduced iron as the final step of the reduction of high-purity hematite, the method recovers 93% of the total, and this product returns to the electric arc furnace. The difference of the iron is, firstly, in the gypsum due essentially to the fineness of the particles which have a strip entrainment effect, and, secondly, in the concentrate of lead-silver.
The gypsum formed in the method has good holding properties for the mining industry, which is the final destination of the product because it contains a portion of metals and the balance of silver.
Steelmaking companies using electric arc furnaces for producing steels generally have a production which is, on average, a million tons of steel (1,000,000 MT) per year.
As previously mentioned, per ton of steel produced, 11 kg to 17 kg of electric arc furnace dust are generated, with a content of zinc from 12% to 35%.
Hence, on average, per million MT of steel produced annually, about 12,000 annual tons of electric arc furnace dust are produced.
In view of the attached figures, and according to the numbering of the steps of the method used, two non-limiting exemplary embodiments of the present disclosure can be seen therein, with the understanding that the description must be considered as an example of the principles of the disclosure and does not intend to limit the broad scope of protection of the hydrometallurgical method for simultaneously extracting metals and gypsum from the dust of a steelworks electric arc furnace.
Next, a detail for a typical operation of 40 DMT of electric arc furnace dust based on the described methods and
In the exemplary embodiment, 200 m3/day of liquids are purified.
Table 5 shows the specification and balance of products of the method for a typical application of 40 TMD of electric arc dust.
| Number | Date | Country | Kind |
|---|---|---|---|
| 000302-2020/DIN | Mar 2020 | PE | national |
| Filing Document | Filing Date | Country | Kind |
|---|---|---|---|
| PCT/PE2021/000002 | 2/9/2021 | WO |
