AU3628195A

AU3628195A - Method for recovering metal and chemical values

Info

Publication number: AU3628195A
Application number: AU36281/95A
Authority: AU
Inventors: Charles A Burrows; Paul R Dibella; Allan S Myerson; Charles Sanzenbacher
Original assignee: Metals Recycling Technologies Corp
Current assignee: Metals Recycling Technologies Corp
Priority date: 1994-09-08
Filing date: 1995-09-08
Publication date: 1996-03-29
Anticipated expiration: 2015-09-08
Also published as: JPH10509212A; AU710302B2; CN1166862A; CN1054888C; ATE210739T1

Description

METHOD FOR RECOVERING METAL AND CHEMICAL VALUES

BACKGROUND OF THE INVENTION 1. Field of the Invention

The present invention relates generally to a process for the recovery of metal and chemical values from industrial waste streams comprising zinc compounds and iron compounds. The present invention relates more specifically to a process subjecting a waste materials stream comprising zinc compounds and iron compounds, such as electric arc furnace (EAF) dust, to a combination of leaching and reducing steps, which enable the separation and recovery from the waste materials stream of zinc oxide, zinc metal, iron and carbon compounds, lead, and cadmium.

A useful application of the present invention is a process in which additional waste material streams, such as iron-rich and iron-poor wastes, are combined with a waste materials stream typically comprising zinc compounds and iron compounds. The combined waste product is subjected to a combination of steps including leaching, resulting in a precipitate comprising iron oxides, which then is subjected to roasting, resulting in an enriched direct reduced iron compound which can be used as a feedstock for steel mills. During the recovery process, carbon compounds can be added to the waste stream, and a cake product produced from the undissolved iron and carbon compounds, which also can be used as a feedstock for steel mills. 2. Prior Art

The treatment of waste metal process dust in general is known in the art. Specifically, the recovery of zinc oxide and other zinc products is known. However, a complete continuous recycle treatment of waste metal process dust, which results in the recovery of chemical and metal values and the production of a feedstock for steel mills, is not known.

Zinc oxide, which has a variety of uses, is found in commercial by-products including waste material streams such as fly ash and flue dust. Known methods for recovering zinc oxides, including recovering zinc oxide from industrial waste materials, include leaching with mineral acid, caustic soda, ammonium hydroxide, and ammonium carbonate solutions. These methods have low yields of zinc oxide and typically do not recover pure zinc oxide, the recovered zinc oxide being contaminated with other metal salts. To obtain pure zinc oxide, subsequent roasting and evaporation processes were necessary.

U.S. Patent No. 3,849,121 to Burrows, now expired but which was assigned to a principal of the assignee of the present invention, discloses a batch method for the selective recovery of zinc oxide from industrial waste. The Burrows method comprises leaching a waste material with an ammonium chloride solution at elevated temperatures, separating iron from the solution, treating the solution with zinc metal and cooling the solution to precipitate zinc oxide. The material obtained in the last step is a mixture of a small amount of zinc oxide, hydrated zinc phases which can include hydrates of zinc oxide and zinc hydroxide, as well as other phases and a large amount of diamino zinc dichloride Zn(NH₃)₂Cl₂ or other similar compounds containing zinc and chlorine ions. Currently, the Burrows method is not economically viable because of environmental guidelines established subsequent to the issuance of the Burrows patent.

The first step in the Burrows patent is the treating of the EAF dust with an ammonium chloride solution. As twenty to fifty percent of the zinc present in the Burrows dust is a iron-zinc complex (known as a spinel) which cannot be leached by the ammonium chloride solution, the Burrows process therefore cannot leach and recover a significant portion of zinc present in the EAF dust. The second step in the Burrows process is cementation with zinc dust. Zinc dust causes an electrochemical reaction which causes the lead and cadmium to deposit on the zinc particles. Burrows does not teach the need to remove the lead and cadmium in this step efficiently without using a large amount of zinc. The third step in the Burrows patent cools the filtrate from the cementation process to obtain zinc oxide crystals. However, Burrows does not produce zinc oxide of any degree of purity; x-ray diffraction figures clearly show that upon crystallization there is a mixture of many phases. Burrows indicates no method of cooling or controlling either purity or size, and the particles produced do not meet commercial requirements. Further, a significant portion of the ammonium chloride is lost in the crystal washing step when the diamino zinc dichloride decomposes.

Waste metal process dust typically has varying amounts of lead, cadmium and other metals contained in the dust. For various reasons, it is desirable to remove such metals from the waste metal dust, for example to recycle the lead and cadmium and/or to prevent introduction of the lead and cadmium into the atmosphere. The Burrows patent includes a method for removing dissolved lead and cadmium from the ammonium chloride solutions which have been used to treat the waste metal dust by the addition of powdered zinc dust to the ammonium chloride solutions. The resulting electrochemical reaction forms elemental lead deposits on the surface of the powdered zinc dust. For this reaction to proceed, a large surface area of zinc initially must be present because as the lead covers the zinc dust particle, the particle becomes no longer available for the electrochemical reaction. For this reason, very fine powder is used which, unfortunately, immediately aggregates to form large clumps which sink to the bottom of the vessel. Rapid agitation does not prevent this from happening. Because of the aggregation of zinc, a large amount of zinc must be added to remove all of the lead, a poor practice for economic reasons. Further, if it is desired to separate the lead and some cadmium from the zinc so that all of these metals can be sold or reused, the higher the zinc concentration in the metals, the larger the mass to be processed per unit mass of zinc.

U.S. Patent No. 4,071,357 to Esters discloses a method for recovering metal values which includes a steam distillation step and a calcining step to precipitate zinc carbonate and to convert the zinc carbonate to zinc oxide, respectively. Eelers further discloses the use of a solution containing approximately equal amounts of ammonia and carbon to leach the flue dust at room temperature, resulting in the extraction of only about half of the zinc in the dust, almost 7% of the iron, less than 5% of the lead, and less than half of the cadmium. Steam distillation precipitates zinc carbonate, other carbonates and iron impurities, whereas temperature lowering advantageously precipitates a number of crystalline zinc compounds. Steam distillation also increases system temperature, driving off ammonia and carbon dioxide, resulting in the precipitation of iron impurities and then zinc carbonate and other dissolved metals.

The solubility of zinc and zinc oxide is relatively high in NH₄C1 solution, and the solubility of zinc and zinc oxide in the solution declines rapidly with temperature, which is the basis for the crystallization-based separation which is used later in the present process. The rate of the leaching is a function of the difference between the zinc concentration in solution and the saturation concentration; the higher the saturation concentration the more rapid the leaching. The present process leaches for only 1 hour, while the Peters process leaches for at least several hours. Lead and lead oxide, as well as cadmium and cadmium oxide, are soluble in the ammonium chloride solution while iron oxide is virtually insoluble. During the leaching process of the present invention, 95-100% of the zinc present as zinc oxide is extracted, compared to about 55% in Peters: 50-70% of the lead present is removed, compared to less than 5% in Peters: and 50-70% of the cadmium is removed, compared to less than half in Peters. Peters indicates that his residue, which is high in lead and is a hazardous waste, is discarded. By leaching out a significant portion of the lead and cadmium, the present process produces a material which can be used by the steel producer as they use scrap metal. Likewise, the present process enables separation and recovery of substantially pure lead and cadmium, thereby reducing the overall volume of waste and reclaiming materials having potential economic value.

Another process offered by Engitec Impianti SpA, of Milan, Italy proports to recover zinc metal and lead cement using an electrowinning technology to extract the metal from the soluble salt in an electrolytic cell. In the Engitec process, EAF flue dust is leached with a spent electrolyte, such as ammonium chloride, which dissolves the zinc, lead, copper and cadmium in the EAF dust into solution while leaving the iron in solid form. The solution containing the dissolved zinc is placed in an electrolytic cell which draws the zinc from the solution onto a cathode plate, while the other heavy metals are filtered out in solid form into cement cakes. Apparently, the electrolysis of the zinc amino occurs in a conventional open cell using a titanium permanent blank cathode and a proprietary graphite anode. In the electrolysis cell, the zinc plates on the titanium cathode. However, the deposition time for the zinc is 24 to 48 hours, depending on the current density. The electrolysis cell consumes ammonia and evolves nitrogen and to maintain the pH of the electrolyte in the desired range of 6 to 6.5, additional ammonium must be added, to the cell in the range of 180kg per tonne of product zinc. In effect, the Engitec process takes the product solution from the Burrows process and subjects it to electrowinning.

The use of an electrolysis cell adds costs to the process. The Engitec process also results in the formation of metallic zinc which has less value than zinc oxide. The residue removed from the Engitec process comprises zinc ferrite which is an additional impurity for any future process. It would be more advantageous to obtain a residue comprising primarily iron oxide with no zinc ferrite or other impurities, or only an insignificant amount of such other impurities.

U.S. Patent No. 4,292,147 to Fray discloses and claims a method for the electrodeposition of cadmium or zinc from chloride solutions derived from chlorine leaching of materials. An aqueous solution having 15 to 30% by weight of zinc or cadmium chloride is electrolyzed at a pH of 2 to 3.5 at a temperature of below 35°C with gas agitation at a current density above lOOA/m² to form coherent zinc or cadmium at the cathode. A typical zinc containing material such as flue dust is leached with a saturated chlorine solution, preferably in the presence of chlorine hydrate. The zinc chloride solution preferably contains 20 to 30% by weight zinc or cadmium chloride and up to 20% by weight alkaline metal or ammonium chloride. The electrolysis preferably is carried out at 0°C to 9°C and above 2500A m² with intermittent current reversal. Chlorine hydrate liberated at the anode may be recycled to affect leaching. BRIEF SUMMARY OF THE INVENTION The present invention is a method which recovers iron-containing compounds, zinc oxide, and other chemical and metal values from waste materials. Along with the zinc oxide, zinc metal can be recovered, along with values of other metallic elements contained in the waste material such as lead, silver, and cadmium. The solutions used in the process are recycled such that the process does not have any liquid wastes. The solids recovered from the process all can be used in other processes. Several such residues, including the iron oxide cake, lead metal residue, and cadmium are of such quality that they can be used directly as raw material for production of a variety of goods.

Briefly, the preferred waste material, typically a fly ash or flue dust such as EAF, is leached with an ammonium chloride solution resulting in a product solution comprising dissolved zinc and or zinc oxide and other metal oxides and undissolved materials comprising iron oxides. An ammonium salt in which the negative ion will form insoluble compound with calcium can be added to remove calcium compound impurities, which precipitate out from the product solution. The product solution and the undissolved materials are separated, with both the product solution and the undissolved materials being further treated to recover valuable components. Zinc metal is added to the product solution, preferably at 90°C or higher, to cement out any lead and cadmium contained in the product solution. A dispersant also can be added to prevent the zinc metal from flocculating. The remaining product solution is rich in zinc compounds.

The remaining product solution then can be treated in several manners. For example, the remaining product solution can be cooled to between about 20°C and 60°C thereby precipitating the zinc components from the product solution as a mixture of crystallized zinc compounds. These crystallized zinc compounds are separated from the product solution, washed with a wash water at between 25°C and 100°C and then dried at elevated temperatures above 100°C, resulting in a zinc oxide product of 99% or greater purity. In another example, the remaining product solution can be subjected to electrolysis in which zinc metal plates onto the cathode of the electrolysis cell. Any remaining product solution after crystallization or electrolysis is recycled back to treat incoming waste material.

The undissolved material separated from the product solution is rich in iron oxide, and typically has some impurities such as zinc ferrite. The undissolved materials can be used as a feedstock for steel mills so long as the quantity of impurities is not too great. It is preferable, however, to remove the impurities from the iron oxide prior to using the iron oxide as a feedstock. Even more preferably, reducing the iron oxide to direct-reduced iron (DRI) is desired as DRI can be used to replace part or all of the steel scrap charge.

Prior to be leached by the ammonium chloride solution, the waste material, typically including franklinite and magnetite, may be roasted at temperatures greater than 500°C for a predetermined period of time. The roasting process generally comprises the steps of adding heat to the waste material and/or passing heated reducing gases through the waste material and causes a decomposition of the franklinite zinc oxide-iron oxide complex into zinc oxide, iron oxide and other components. A rotary hearth furnace has been found to be a suitable vehicle for the roasting process. Although all reducing gases are suitable, hydrogen and carbon-containing gases such as carbon dioxide are preferred, as well as mixing carbon (activated) with the material and roasting in a gas containing oxygen.

In the cementation step, lead, cadmium and copper plate out on zinc particles introduced into the solution, thereby forming a cake of waste metals which is filtered and removed from the solution. This waste metals cake may be further processed to separate and purify component elements such as lead and copper, which may then be sold as products. The waste metal cake is washed with water and transferred to a vessel containing sulfuric acid. The sulfuric acid will dissolve zinc, cadmium and copper present in the waste metal cake. Lead metal, however, is not soluble in sulfuric acid and any lead oxide present in the cake will dissolve and reprecipitate as lead sulfate. The resulting solid is filtered, washed with water, and dried under nitrogen. This solid is mainly lead metal having trace impurities of lead oxide, lead sulfate, copper, zinc and cadmium. This lead metal may be resold, and is suitable for a variety of uses. The remaining sulfuric acid solution contains cadmium and zinc with small amounts of copper. The cadmium may be removed electrochemically by placing zinc metal sheets in the solution to produce a cadmium sponge, which is suitable for resale as a product. Alternatively, electrolysis can be used to recover the cadmium. The remaining solution is mainly zinc and sulfuric acid, which may be recycled into the primary leach solution to eventually recover the zinc as zinc oxide. The filtrate from the cementation step is hot (90-110°C) and contains a large amount of dissolved zinc with small amounts of trace impurities. Upon controlled cooling of the solution, crystals of zinc salts begin to appear. Control of the cooling rate and temperature versus time profile is important in controlling the size distribution of the crystals and in reducing or eliminating many of the impurities which might occur. This is especially true of the included solution; control of the crystallization can reduce this to virtually zero. In addition, since crystallization is based on differential solubility, and none of the impurities is present in a concentration which can crystallize, the zinc salts are virtually free of any metal impurities. Iron-poor and iron-rich waste materials may be added to the waste stream. The preferred iron-poor waste feed stream is taken from fumes emanating from industrial processes. For example, fumes from reduction furnaces and from the iron and steel making processes typically are filtered in baghouses. Other industrial processes also produce fumes which may be filtered in baghouses. The waste product removed from the fumes in the baghouses may be subjected to the present process for recovery of chemical values and production of an iron-rich product. Likewise, the fumes emanating from direct-reduced iron reduction furnaces may be filtered, with the filtrate recycled to the present process. Alternatively, the fumes may be cleaned using a recirculating water or ammonium chloride solution wet scrubber. The loaded recirculating water or ammonium chloride solution (the scrubbant) may be recycled to the ammonium chloride leach step of the present invention, as discussed below.

Iron-rich waste materials can be added to the combination waste stream to help dispose of such iron-rich waste materials and to produce an iron-based feedstock having an even higher percentage of iron. The use of mill scale as an iron-enhancer in the iron and steel making processes is contrary to common technology, as mill scale is considered a waste product or impurity. Likewise with used batteries. By adding the iron oxide rich material to the EAF dust, and treating the combined waste material, a resultant iron-rich feedstock is produced, suitable as a feedstock to the iron and steel making processes. The iron oxide in the undissolved materials can be reduced to DRI in several manners. First, the undissolved materials may be subjected to a high temperature roasting step, in the 980°C to 1315°C range, to reduce the iron oxide present in the undissolved materials to DRI. Roasting at this elevated temperature oxidizes and/or drives off the majority of the remaining impurities. To assist in the formation of a more usable DRI, the undissolved materials can be pelletized with carbon or sodium silicate, or another suitable material, at the end of or after the roasting step. Second, carbon, in the form of activated carbon, carbon dust, carbon pellets or the like, can be introduced to the ammonium chloride and waste material mixture during the leaching process. Third, carbon can be introduced to the dried undissolved material cake. When the iron oxide and carbon are heated under a reducing atmosphere, such as CO or CO₂ or other common reducing gases, the carbon will react with the iron oxide, assisting in reducing the iron oxide to DRI. Combining any of these methods can result in an even purer DRI product. The present invention also provides a method by which iron-rich by-products produced by the recovery process are reduced in a reduction furnace which reduces the iron oxide to DRI. Fumes exhausted by the reduction furnace are filtered through a baghouse or/and a wet scrubber. The materials captured by the baghouse or/and wet scrubber may then be recycled back into the leaching step of the recovery process of the present invention where they are used in the recovery process. The solid particles captured by the baghouse may be combined with the primary waste stream feed, such as EAF dust, or, alternatively, fed as a separate primary feed to the ammonium chloride leach. The loaded scrubbant liquid from the wet scrubber may be combined with the primary ammonium chloride leachant or, alternatively, if an ammonium chloride solution is used as the scrubbing liquid, used as the primary ammonium chloride leachant.

Fumes exhausted from the reduction furnace used to reduce the iron-rich materials into DRI are fed to a baghouse or/and a wet scrubber containing a heated ammonium chloride solution. The fumes, which typically are iron poor, consist primarily of zinc, lead, and cadmium. The materials captured through the baghouse or wet scrubber filtering process may then be recycled back into the leaching step of the recovery process of the present invention. If the fumes are filtered through a baghouse, the captured materials will be solids which are placed into the waste material stream whereby they are added to the ammonium chloride solution of the leaching step. If the fumes are filtered through a wet scrubber, the captured materials will be discharged from the wet scrubber in a liquid stream directly into the ammonium chloride solution of the leaching step. Alternatively, if ammonium chloride is used as the scrubbing liquid, the ammonium chloride scrubbant may be used as the leaching (digesting) solution.

Due to the continuous nature of the process, calcium impurities may build up, resulting in lower efficiency. The use of a secondary ammonium salt, different from ammonium chloride, helps alleviate this calcium impurity build up, maintaining efficiency. Calcium present in the fumes may be leached by the ammonium chloride solution. A build up of calcium in the ammonium chloride leach will reduce the ability of the ammonium chloride to leach zinc from the waste material. A secondary ammonium salt such as, preferably, ammonium sulfate or ammonium hydroxide, is added to the leach tank prior to charging with the waste material to precipitate out the calcium ions as calcium sulfate. The loaded recirculating water or ammonium chloride solution (the scrubbant) then may be recycled to the ammonium chloride leach step of the present invention, as discussed below, without creating a calcium build up in the scrubbant.

BRIEF DESCRIPTION OF THE DRAWING Fig. 1 is a schematic of a representative process of the present invention. DETAILED DESCRIPTION OF A PREFERRED EMBODIMENT The method for recovering chemical and metal values disclosed herein is carried out in its best mode in recovering these materials from the waste streams of industrial or other processes. A typical industrial waste stream used is a flue gas such as electric arc furnace (EAF) dust where the charge contains galvanized steel, having the following percent composition: TABLE I

Analysis of Flue Dust

Component Weight Percent zinc oxide 39.64 iron oxide 36.74 lead oxide 5.72 inert materials 9.10 calcium oxide 2.80 potassium oxide 2.41 manganese oxide 1.29 tin oxide 1.13 aluminum oxide 0.38 magnesium oxide 0.33 chromium oxide 0.16 copper oxide 0.06 silver 0.05

2 unidentified materials 0.22

TOTAL 100.00

General Process Description

Generally, the present process is a continuous method for the recovery of zinc oxide and iron-containing compounds from waste material streams which comprise zinc compounds, comprising the intitial steps of: a. roasting the waste material at an elevated temperature and in a reducing atmosphere and/or in the presence of carbon in part to reduce any iron oxides in the waste material to direct reduced iron (DRI) and to prepare the waste material for further chemical and metal values recovery;

siliceous material, such as slag, with carbon granules occluded. ' molybdinum, antimony, indium, cadmium, germanium, bismuth, titanium, nickel and boron. b. treating the waste material with an ammonium chloride solution at an elevated temperature to form a product solution which comprises dissolved zinc and dissolved zinc oxide whereby any iron oxide in the waste material will not go into solution; c. separating the product solution from any undissolved materials present in the product solution including any of the iron oxide; d. adding zinc metal and a dispersant to the product solution whereby any lead and cadmium ions contained within the product solution are displaced by the zinc metal and precipitate out of the product solution as lead and cadmium metals and the dispersant is selected from the group consisting of dispersants which will prevent the aggregation of said zinc metal; e. separating the product solution from the lead and cadmium metals which may be subjected to further processing, thus allowing their purification and recovery; f. further treating the product solution to recover zinc compounds and other chemical and metal values; and g. further treating the undissolved materials to recover an iron product suitable for use as the feedstock to a steel mill.

This portion of the present process also can comprise a two-stage leaching process for even greater yields of zinc oxide. The two-stage process comprises the steps of: a. treating the waste material a first time with an ammonium chloride solution at an elevated temperature to form a first product solution which comprises dissolved zinc constituents whereby any iron oxide in the waste material will not go into solution; b. separating the first product solution from the undissolved waste material compounds present in the first product solution including any of the iron oxide; c. roasting the undissolved waste material compounds at an elevated temperature and in a reducing atmosphere; d. treating the roasted undissolved waste material compounds a second time with the ammonium chloride solution at an elevated temperature to form a second product solution which comprises dissolved zinc constituents whereby any iron oxide remaining in the roasted undissolved waste material compounds will not go into solution; e. combining the first and second product solutions to form a combined product solution; and then f. carrying out steps d - g of the General Process disclosed above. An ammonium chloride solution in water is prepared in known quantities and concentrations. If the two-stage leaching process is used, the feed material which contains the zinc species, such as the waste material flue dust described in Table I or any other feed material source which contains zinc or zinc oxide mixed with other metals, is added to the ammonium chloride solution at a temperature of about 90°C or above. Otherwise, the feed material is roasted. The zinc and/or zinc oxide dissolves in the ammonium chloride solution along with other metal oxides, such as lead oxide and cadmium oxide. The iron oxide does not dissolve in the ammonium chloride solution. The solubility of zinc oxide in ammonium chloride solutions is shown in Table II.

TABLE II Solubility of ZnO in 23% NH₄C1 solution

Temperature °C g Dissolved/1 QO g

90 14.6

80 13.3 70 8.4

60 5.0

50 3.7

40 2.3 A 23% by weight ammonium chloride solution in water at a temperature of at least 90°C provides the best solubility of zinc oxide and has been chosen as the preferred ammonium chloride solution concentration. Concentrations of ammonium chloride below about 23% do not dissolve the maximum amount of zinc oxide from the flue dust, and concentrations of ammonium chloride above about 23% tend to precipitate out ammonium chloride along with the zinc oxide when the solution is cooled. Iron oxide and inert materials such as silicates will not dissolve in the preferred solution.

The zinc oxide, as well as smaller concentrations of lead or cadmium oxide, are removed from the initial dust by the dissolution in the ammonium chloride solution. The solid remaining after this leaching step contains zinc, iron, lead and cadmium, and possibly some other impurities. The remaining solid then is roasted in a reducing atmosphere, typically at a temperature greater than 420°C and often at 700°C to 900°C. The reducing atmosphere can be created by using hydrogen gas, simple carbon species gases such as carbon dioxide, or by heating the material in an oxygen containing gas in the presence of elemental carbon. The carbon preferably is in the form of dust or pellets. Typical roasting times are from 30 minutes to 4 hours. As discussed above, the waste dust first may be roasted and second may be leached, omitting the first leaching step.

After the dust has been roasted, it is leached in the 23% ammonium chloride solution at a temperature of at least 90°C. Any zinc or zinc oxide formed during the roasting step dissolves in the ammonium chloride solution. The zinc oxide containing ammonium chloride solution then is filtered to remove any undissolved material, including the iron oxide. While the filtered zinc oxide and ammonium chloride solution is still at a temperature of 90°C or above, finely powdered zinc metal is added to the solution. Through an electrochemical reaction, any lead metal and cadmium in solution plates out onto the surfaces of the zinc metal particles. The addition of sufficient powdered zinc metal results in the removal of virtually all of the lead of the solution. The solution then is filtered to remove the solid lead, zinc and cadmium.

To help keep the zinc powder suspended in the zinc oxide and ammonium chloride solution, water soluble polymers which act as antiflocculants or dispersants may be added. Surface-active materials also will act to keep the zinc powder suspended, as will many compounds used in scale control. These materials only need be present in concentrations of 10 - 1000 ppm. Various suitable materials include water soluble polymer dispersants, scale controllers, and surfactants, such as lignosulfonates, polyphosphates, polyacrylates, polymethacrylates, maleic anhydride copolymers, polymaleic anhydride, phosphate esters and phosponates. A discussion of these various materials can be found in the literature, such as Drew, Principles of Industrial Waste Treatment, pages 79-84, which is incorporated herein by reference. Flocon 100 and other members of the Flocon series of maleic-based acrylic oligomers of various molecular weights of water soluble polymers, produced by FMC Corporation, are effective. Adding the dispersants to a very high ionic strength solution containing a wide variety of ionic species is anathema to standard practice as dispersants often are not soluble in such high ionic strength solutions.

This cementation step preferably is carried out by adding approximately two times the stoichiometric amount of zinc and dispersant. After this initial striking step, the lead, cadmium and copper concentration remaining in the solution is monitored. A second polishing step may then be performed by adding a small amount of powdered zinc and dispersant as necessary.

At this stage there is a filtrate rich in zinc compounds and a precipitate of lead, cadmium and other products. To recover zinc oxide, the filtrate then is cooled to a temperature of between about 20°C and 60°C resulting in the crystallization of a mixture of zinc compounds. The mixture contains a significant amount of diamino zinc dichloride, or other complex compounds which involves zinc amino complexes, hydrated zinc oxides and hydroxide species. Crystallization helps to achieve a high purity zinc oxide of controlled particle size, typically through control of the temperature- time cooling profile. Reverse natural cooling, that is cooling the solution slower at the beginning of the cooling period and faster at the end of the cooling period, is preferred to control the nucleation to crystal growth ratio and, ultimately, the crystal size distribution. The precipitated crystallized solid is filtered from the solution and washed with water at a temperature of between about 25°C and 100°C. The filtered solution is recycled for further charging with feed material. The solubility of diamino zinc dichloride in water is shown in Table III.

TABLE III Solubility of Zn(NH₃)₂Cl₂ in water

Temperature °C g DlSSOlYtdflPQ g H^

90 32

80 24

40 21 25 12.8

Very little of the hydrated zinc oxide dissolves in the water. This solution is then filtered to remove the hydrated zinc oxide species, which are placed in a drying oven at a temperature of over 100°C. After a sufficient drying period, the resultant dry white powder is essentially pure zinc oxide. The filtrate from the solution is recycled for charging with additional zinc compound mixture.

The zinc oxide may be dried at approximately 100°C . To ensure that the material is free of chloride, however, it is preferable to heat the zinc oxide to a higher temperature. Diamino zinc dichloride decomposes at 271°C and ammonium chloride sublimes at 340°C. Therefore, heating the zinc oxide to a temperature between 271 °C and approximately 350°C to prevent the sublimation of significant amounts of ammonium chloride is preferred. Typically, the zinc oxide should be dried in this temperature range for approximately 2 to 60 minutes, and preferably from 5 to 20 minutes. A 10 minute drying time has been found to be a satisfactory average. As the zinc, lead and cadmium contained in the feed materials are amphoteric species, by using ammonium chloride solution these species will go into solution, while any iron oxide present in the feed material will not go into solution. Other solutions, such as strong basic solutions having a pH greater than about 10 or strong acidic solutions having a pH less than about 3, also can be used to dissolve the zinc, lead and cadmium species; however, if strong acidic solutions are used, iron oxide will dissolve into the solution, and if strong basic solutions are used, iron oxide will become gelatinous. The lead and cadmium can be removed from the ammonium chloride solution through an electrochemical reaction which results in the precipitation of lead and cadmium in elemental form. The difference in solubility between diamino zinc dichloride and zinc oxide in water and in ammonium chloride solutions allows the selective dissolution of the diamino zinc dichloride such that pure zinc oxide can be recovered. This also can be used in the crystallization step to improve the relative amounts of diamino zinc dichloride and zinc oxide species form. Significantly, all of the zinc can be recycled so that all of the zinc eventually will be converted into zinc oxide.

Recovering An Iron Feedstock By taking the undissolved precipitate, which is for the most part iron oxides, and roasting it at elevated temperatures under a reducing atmosphere, a product can be made which is equivalent to DRI. In general terms, heating the iron cake above 980°C up to about 1260°C, and typically no higher than 1315°C, a DRI product is formed. This DRI product then can be pelletized with carbon or with a sodium silicate, or other suitable compound, after it comes out of the furnace. The final product then can be used as a feedstock for steel mills without any additional treatment. Roasting the undissolved precipitate reduces the iron oxide and drives off any zinc, cadmium, and lead, and other impurities. The resulting iron product may have been reduced from several forms of the iron, such as FeO, Fe₂O₃, or Fe₃O₄, reduced to an iron extremely usable as the feedstock for steel mills.

Iron-rich materials, for example, mill scale or used batteries, also may be added to the waste material to be leached and further processed. During the roasting of the undissolved precipitate, the bond to the non-leachable zinc oxide-iron oxide complex, contained in the undissolved precipitate is broken, and the zinc oxide compounds are exhausted in the off gas and captured in a pollution control device, such as a baghouse, leaving the iron oxide cake as the residue. The iron oxide cake is roasted at an elevated temperature, causing the reduction of the iron oxide, leaving the iron metal values. The iron then can be mixed with a binder and formed into briquettes or cubes to be used as the feedstock. The exhausted impurities then can be recycled to recover, for example, zinc oxide, cadmium metal, and lead metal.

The present process is carried out in its best mode in recovering the waste material from the waste streams of industrial or other processes, and combining it with waste material recovered from furnace exhaust streams. Many processes produce an iron poor waste stream, such as reduction furnaces and iron and steel making processes.

Many other processes produce an iron oxide rich waste stream. Other processes remove iron oxide rich materials prior to processing. The iron poor materials are combined with a typical industrial waste stream which, after treatment, results in an iron-rich material suitable for use as a feedstock to a steel mill.

The basic iron feedstock production process is a continuous method comprising the steps of: a. combining a typical industrial process waste material stream, such as from a metal or metal product process, with an iron poor waste material, such as from a reduction furnace or the iron and steel making processes; b. treating the waste material combination with an ammonium chloride solution at an elevated temperature to form a product solution and an undissolved precipitate comprising iron oxide; c. separating the product solution from the undissolved precipitate comprising the iron oxide; and d. further treating the undissolved precipitate in a roasting process resulting in the recovery of a relatively pure iron product.

Any additional iron poor waste material, if in solid form such as from a baghouse, is added to Basic Process Step a. Alternatively, any additional iron poor waste material, if in solution form such as from a wet scrubber, is added to Basic Process Step b.

To the basic process steps, a number of additional steps may be added depending on the process conditions and iron properties desired. The additional steps include, either individually or in some combination: 1. preroasting the solid waste material at an elevated temperature and/or in a reducing atmosphere in part to produce DRI;

2. pretreating the solid waste material with an ammonium chloride solution at an elevated temperature to form a product solution and an undissolved precipitate comprising iron oxide, roasting the undissolved precipitate at an elevated temperature and optionally in a reducing atmosphere, and then treating the undissolved precipitate with an ammonium chloride solution at an elevated temperature to form a product solution and an undissolved precipitate comprising iron oxide;

3. preroasting the solid waste material at an elevated temperature and optionally in a reducing atmosphere, pretreating the waste material with an ammonium chloride solution at an elevated temperature to form a product solution and an undissolved precipitate comprising iron oxide, roasting the undissolved precipitate at an elevated temperature and optionally in a reducing atmosphere, and then treating the undissolved precipitate with an ammonium chloride solution at an elevated temperature to form a product solution and an undissolved precipitate comprising iron oxide; and/or

4. Taking the off-gases from the preroasting process, which typically comprise zinc, cadmium, lead and other metals and compounds, and subjecting them to the ammonium chloride leach process to recover the zinc, cadmium, lead and/or other metals and compounds as values. To the basic process steps, additional iron product purification steps may be added. For example:

1. Elemental carbon can be added during the leaching step or steps to initiate the reduction of the iron oxide into DRI during the leaching step or steps. The elemental carbon may be added in a number of forms including, but not limited to, dust, granules, and pellets. The elemental carbon does not go into solution and remains with the undissolved precipitate.

2. Elemental carbon can be added to the undissolved precipitate after it has been separated from the product solution. Combining elemental carbon and iron oxide in this manner at an elevated temperature and under a reducing atmosphere also will initiate the reduction of the iron oxide into DRI. The elemental carbon can be mixed into the undissolved precipitate in a number of manners including, but not limited to ribbon blenders and mixers.

Preroasting

The preroasting step can be carried out prior to the initial leaching step, or between a first and second leaching step, or both. The waste dust or the combination of waste dust and the iron oxide rich material, is heated to temperatures greater than 500°C.

This temperature causes a reaction which causes a decomposition of the stable franklinite phase into zinc oxide and other components, and yet does not allow for the complete reduction of zinc oxide to zinc metal. The resulting zinc oxide can be removed by sublimation or extraction with an ammonium chloride solution. The resulting material after extraction has less than 1% by weight zinc.

The solid waste material can be preroasted using many conventional roasting processes, such as, for example, rotary hearth furnaces, direct or indirect heating and the passing of hot gases through the dust. For example, non-explosive mixtures of reducing gases, such as hydrogen gas and nitrogen or carbon dioxide, can be passed through the powder containing franklinite and magnetite. Hydrogen gas is not the only species that may be used for reductive decomposition of franklinite. It is possible to use carbon or simple carbon containing species, including carbon-containing reducing gases and elemental carbon. Heterogeneous gas phase reductions are faster than solid state reductions at lower temperatures and therefore suggest the use of carbon monoxide. The carbon monoxide can be generated in situ by mixing the franklinite powder with carbon and heating in the presence of oxygen at elevated temperatures. The oxygen concentration is controlled to optimize CO production. The carbon monoxide may be introduced as a separate source to more clearly separate the rate of carbon monoxide preparation from the rate of Franklinite decomposition. The prepared zinc oxide then can be removed by either ammonium chloride extraction or sublimation.

Carbon Addition The present process also can be operated to produce a high-quality iron-carbon cake as a residual product. The iron oxide contained in the waste stream does not go into solution in the ammonium chloride solution, but is filtered from the product solution as undissolved material. This iron oxide cake can be used as is as the feedstock to a steel mill; however, as previously discussed, it becomes more valuable if reduced by reaction with elemental carbon to produce an iron-carbon or DRI product.

A mixture of iron oxide and carbon is used by the steel industry as a feedstock for electric arc furnaces. The iron oxide cake which is removed as undissolved material from the leaching step is primarily iron oxide, being a mixture of Fe₂O₃ and Fe₃O₄. The iron oxide cake can be treated in three manners. First, carbon can be added to the leaching step and the iron oxide cake will have carbon plus iron oxide. The iron oxide- carbon cake can go directly to the steel mill and, if it goes directly to the steel mill, then the reduction of the iron oxide would take place in the steel mill furnace. Second, the iron oxide-carbon cake can be pelletized and roasted in a reduction furnace to form DRI.

The iron oxide precipitate, which typically contains around 80% solids, is ground up with carbon and formed into pellets, briquettes or cubes and then heated. These pellets, briquettes or cubes then can be introduced to a steel making furnace. The difference in the material that would be introduced to the furnace from the first manner and the second manner is that in the second manner, DRI is introduced to the steel making fumace, while in the first manner, a combination of iron oxide and carbon is introduced to the steel making fumace. The iron oxide plus carbon can be supplied to the steel mill as is. When this carbon enriched iron oxide is melted, it forms a foamy slag, and a foamy slag is desirable in steel making. Third, the carbon can be added through a ribbon blender, and then the iron oxide-carbon cake can be introduced either directly into the furnace or, preferably roasted in a reduction fumace first to form DRI, which would be preferred for steel making.

Combining carbon and iron oxide in a reducing atmosphere and at an elevated temperature results in the reduction of the iron oxide, producing DRI. DRI can be used to replace part or all of the steel scrap charged to a steel mill. In some operations, DRI is preferred to scrap because it has a known uniform composition and generally contains no residual elements such as chromium, copper, nickel, and tin. When carbon-enriched iron oxide is melted, it forms a desired foamy slag because it contains both carbon and iron oxide. Because the price of steel scrap usually is lower than DRI, the use of DRI usually cannot be economically justified. DRI typically runs in the $120.00 and higher per ton range. However, since the iron oxide is a residual product of an economical recovery process, such as the recovery of zinc oxide from flue dust described generally below, with the main value of the process being from the zinc oxide product, the iron oxide or DRI can be produced more economically. Therefore, the iron oxide produced as a residual in this process has significant value.

Generally the iron oxide and carbon product is pressed into a cake for ease of handling and use. The cake typically contains approximately 82% solids, but may range from 78% to 86% solids and be easily handled and used. Although cakes of less than 78% solids can be formed, the other 22%+ of material would be product solution which, if the cake is used as a feedstock to a steel mill, would be reintroduced to the steel- making process, which is uneconomical. Likewise, drying the cake to have more than 86% solids can be uneconomical.

The roasting process produces vapors, from the zinc, lead, cadmium and other impurities, that have to be condensed into dust. These impurities can be sent to the baghouse at the end of the steel making process, mixed into the original waste dust, and then sent to the first leaching step, in a recycle fashion. Alternatively, the exhaust vapors and dust from the roasting step may be sent to a separate baghouse at a stand alone facility. In any manner, the fumes exhausting from the steel mill furnace and the reduction fumace typically are iron poor, but comprise other valuable components. The furnace exhaust fumes are an excellent source of iron poor waste materials useful for recovery in the present process. The exhaust fumes may be filtered in a baghouse, with the resulting filtrate being added to the waste stream feed of the present process, or with the resulting filtrate being the primary waste stream feed of the present process. The exhaust fumes also may be scrubbed in a wet scrubber, with the resulting loaded scrubbing solution being added to the ammonium chloride leachant of the present process. If an ammonium chloride scrubbing solution is used instead of water, the loaded ammonium chloride scrubbing solution may be used as the primary leachant of the present process. Enhanced Zinc Recovery

The zinc dust obtained from various sources have shown by chemical analysis to contain from 20% - 25% zinc by weight. Certain crystalline phases exist in this dust, specifically zinc oxide. The positive identification of the iron phase is complicated by the possible structural types (i.e. spinel type iron phases showing almost identical diffraction patterns). The zinc oxide (as well as smaller concentrations of lead or cadmium oxide) are removed from the initial dust by dissolution in a concentrated ammonium chloride solution (23% ammonium chloride).

Filtration and washing of the undissolved species leaves a residual powder. This powder shows a zinc concentration that is still elevated (i.e., 10 - 13% by weight), but that is not zinc oxide. All crystalline phases can be identified by spinel type phases. This powder is a combination of franklinite (Fe, Mn, Zn)(FeMn)₂O₄, and magnetite (iron oxide: Fe₃O₄). Both of these phases have very similar spinel type structures. The zinc within the franklinite cannot be removed by dissolution with ammonium chloride. In addition, no simple extraction process will remove zinc from this stable oxide phase. Although this compound is very stable to oxidation (all elements in the highest oxidation state), it is relatively easy to destroy this compound by reduction at elevated temperatures. The reduction of the franklinite in an atmosphere that cannot readily reduce zinc oxide or allow for the rapid oxidation of zinc to zinc oxide following reduction and subsequently recover the zinc oxide by ammonium chloride extraction or sublimation (the highly volatile zinc oxide will sublime from the mixture at relatively low temperatures and recondense at the cold locations of the roaster). The alternative will be complete reduction of the franklinite to zinc metal and removal by distillation or separation of the molten zinc by settling techniques. Crystallization

The purpose of the crystallization/washing step is to produce a high purity zinc oxide of controlled particle size. This is accomplished through control of the temperature-time profile during cooling in the crystallization. The crystallization step in the process takes the filtrate from the cementation step at 90-100°C. This filtrate contains the dissolved zinc with small amounts of trace impurities such as lead and cadmium. In order to prepare a pure zinc oxide it is necessary to prevent the formation of solvent inclusions inside the grown crystals. Solvent inclusions are pockets of liquid trapped as a second phase inside the crystals. Control of crystallization conditions can be employed to reduce these impurities. Recycle

One purpose of this process is to produce pure zinc oxide from waste dust containing zinc. To do so this efficiently and in a safe and cost effective way, the process recycles all zinc which is not removed from the leachate in the crystallization step. In addition, the diamino zinc dichloride which is redissolved in water in the washing step also is recycled. The recycle of zinc increases the overall zinc concentration in liquid solution in the process. This allows the crystallizer to operate at a higher temperature due to the rapid change in zinc oxide solubility with temperature in ammonium chloride solution.

Recovery Of Lead And Cadmium This process also can produce essentially pure lead and cadmium from the waste metals cake filtered out of the solution after the cementation step. Once recovered, these metals can be sold as products suitable for a variety of uses. A preferred method for recovery of these metal byproducts comprises: a. washing the waste metals cake filtered from the solution after the cementation step with water; b. treating the waste metals cake with sulfuric acid, which will dissolve zinc, cadmium and copper present in the waste metals cake; c. removing lead metal, which is insoluble in sulfuric acid, from the solution, dissolving and reprecipitating and lead oxide as lead sulfate; and d. electrochemically removing dissolved cadmium from the solution by placing zinc metal sheets into the solution onto which the cadmium plates to produce a cadmium sponge.

The lead solids may be filtered, washed with water, and dried under an inert gas such as nitrogen to produce a relatively pure lead metal. Some impurities are present in the form of lead oxide, lead sulfate, copper, zinc, and cadmium. Alternatively, electrolysis may be used to cause cadmium in the solution to plate out as a sponge on other cathodic materials. The solution remaining is mainly zinc in sulfuric acid, which can be recycled back to the leach solution for eventual recovery of the zinc as zinc oxide. A cake of waste metals is produced during the cementation step when zinc dust added to the ammomum chloride solution causes an electrochemical reaction in which lead, cadmium, and copper atoms plate out on the surface of the zinc dust. The resulting solids are filtered from the solution to produce a cake of waste metals. The waste metals cake is washed with water to remove any remaining solution. The wash water may be purified and recycled. The waste metals cake is then treated with sulfuric acid, which dissolves zinc, cadmium, and copper present in the waste metals cake, with zinc and cadmium dissolving at a more rapid rate than copper present in the cake. Lead metal is not soluble in sulfuric acid, thus lead present in the waste metals cake will remain in solid form. Preferably, the waste metals cake is leached by the addition of a dilute sulfuric acid solution which forms a slurry. The reaction of the zinc oxide in the dust and the sulfuric acid is exothermic. The reactions of cadmium oxide, copper oxide and lead chloride with the sulfuric acid are relatively slower, with the reaction of copper oxide being the slowest. Lead sulfate is formed which is insoluble and removed by filtration at this point. The cadmium solids obtained from the cementation steps can be dissolved by sulfuric acid resulting in soluble sulfates of zinc and cadmium being formed. The zinc sulfate is recycled to the acid leach. This treatment causes the following major reactions to occur:

(1) ZnO + H₂SO₄ -> Zn^ + SO₄ ^~ + H₂O (fast, exothermic) (2) CdO + H₂SO₄ --> Cd^"" + SO₄ ^" + H₂O

(3) CuO + H₂SO₄ -> Cu + SO₄ ^" + H₂O (slower)

(4) PbCl₂ + H₂SO₄ -> PbSO₄ (insoluble) + HC1

Metallic and sulfate ions are formed along with insoluble lead sulfate. Additional sulfuric acid may be added until the solution remains acid (ρH<2 and preferably pH~l). In this way, an economical minimum of acid is consumed. The rapid rate of reaction (1) allows this to be done with little delay. Reaction (1) releases a great deal of heat, and external heating of the solution may not be required. Reactions (2) and (3) take longer to go to completion during the leach stage and the levels of Cd and Cu in solution may be monitored. Leaching may continue until all of the extractable copper is dissolved. It is preferable that the leachable Cu and Cd be removed before proceeding. It is preferable also that a water rinse or second dilute leach take place in order to rinse the solids clean of any entrapped ions, and prevent contamination of the next leach steps.

Soluble lead oxide present in these dusts is converted to the highly insoluble lead sulfate. The abundance of sulfate ions present in solution greatly suppresses the solubility of lead ions. Due to reaction (4), the chloride ions are introduced into the leach liquor. Zinc sulfate targeted for the electro-chemical uses must be kept low in chloride, but even so, the high solubility of zinc chloride makes contamination unlikely, and easy to remove by recrystallization. The lead solids are filtered from the solution, washed with water, and dried under nitrogen. This solid is mainly lead metal with some impurities including lead oxide, lead sulfate, copper, zinc, and cadmium.

After filtering out the neutral precipitate, the neutral filtrate solution pH may be adjusted to become slightly acidic (pH 4-5) by the addition of an acid, preferably sulfuric acid. The remaining solution contains cadmium and zinc with small amounts of copper and possibly lead present. The pH of the solution can be adjusted to and maintained at the preferred pH of 4-5 by the addition of zinc oxide. Cadmium present in the solution may be removed electrochemically by placing a sheet of zinc metal into the solution to produce a cadmium sponge by the following reaction:

(5) Cd + Zn° — > Cd° metal (sponge) + Zn Alternatively, electrolysis may be used to recover cadmium present in the solution. This cadmium sponge may be separated from the zinc metal sheet, rinsed and redissolved in sulfuric acid to produce high purity cadmium sulfate by the following reaction:

(6) Cd° + H₂SO₄ — > CdSO₄ + H₂ (slow) Air oxidation of the cadmium will increase the rate of attack by sulfuric acid solutions, greatly increasing the rate of dissolution, and forming water as the reaction's only byproduct:

(7) CdO + H₂SO₄ —> CdSO₄ + H₂O (fast) The cadmium sponge product, likewise, may be removed from the zinc sheet and sold directly as cadmium metal.

After removal of the cadmium sponge and zinc sheet, the remaining solution is mainly zinc and sulfuric acid. This solution may be recycled by combining it with the primary leach solution, thus enabling eventual recovery of the zinc as zinc oxide. The sulfate will react with calcium present in the primary leach solution, and will precipitate as calcium sulfate.

Electrolysis This process can recover zinc metal by replacing the crystallization steps with an electrolysis step. The combined product solution from the leaching steps comprises zinc ions in solution as Zn²⁺. When the combined product solution is subjected to electrolysis in an electrolytic cell containing an anode and a cathode, the zinc metal is electrodeposited on the cathode. Although it is preferable to have the cathode made from zinc metal, cathodes of other material also will allow the electrodeposition of zinc metal from the combined product solution. Any of the electrolysis cells discussed in the literature are suitable, as long as such cells are configured for the electrolysis of zinc ion containing solutions. The two electrodes of the electrolysis cells are connected externally to a power supply capable of impressing a suitable voltage across the electrodes. The zinc ions, being positive in nature, migrate toward the negative electrode, or cathode, where they combine with electrons supplied by the external circuit to form neutral zinc metal atoms. When this happens, the zinc metal, in effect, electroplates onto the cathode. By using a zinc cathode, the entire cathode can be removed and used as necessary as a source of zinc. Alternatively, a cathode on which electroplated zinc metal can be easily removed can be used. Periodic Precipitation Of Other Solubles

The product solution also may contain sodium, potassium, magnesium, calcium, manganese, and other solubles in solution. These solubles can be recovered by introducing an electrolyte either in the leaching step or in the ammomum chloride storage tanks receiving the recycled product solution. As ammomum chloride is used as the leachant, ammomum salts in solution is the preferred electrolyte. For example, if some ammomum sulfate is added, one could precipitate out calcium sulfate. Ammomum sulfate is a preferred electrolyte to add because the process already uses ammomum in the form of ammonium chloride. The preferred electrolytes include ammonium sulfate, ammonium hydroxide, or ammonium carbonate to precipitate out various solubles. Manganese can be removed by the addition of an oxidizing agent such as potassium permanganate or hydrogen peroxide. This oxidation results in soluble Mn being oxidized to insoluble Mn ⁺ which will precipitate out as a manganese solid.

Removal of Calcium Compounds Due to the continuous nature of the process, calcium impurities may build up, resulting in lower efficiency. The use of a secondary ammonium salt, different from ammomum chloride, helps alleviate this calcium impurity build up. Calcium present in the fumes may be leached by the ammonium chloride solution. A build up of calcium in the ammonium chloride leach will reduce the ability of the ammonium chloride to leach zinc from the waste material. A secondary ammonium salt such as, preferably, ammomum sulfate or ammonium hydroxide, is added to the leach tank prior to charging with the waste material to precipitate out the calcium ions as calcium sulfate. The loaded recirculating water or ammonium chloride solution (the scrubbant) then may be recycled to the ammomum chloride leach step of the present invention, as discussed below, without creating a calcium build up in the scrubbant.

The addition of a soluble ammonium salt in which the negative ion will form an insoluble compound with calcium will remove calcium from the leach solution and at the same time balance the ammonium and chloride ions. Two such salts are ammonium hydroxide (NH OH) and ammonium sulfate ((NH₄)₂SO₄). The addition of ammonium hydroxide will result in the formation of calcium hydroxide which is insoluble. Ammonium hydroxide will increase the system pH thereby resulting in the loss of a substantial amount of ammonia due to shifting the ammonium/ammonia equilibrium as the pH becomes more basic. The addition of ammomum sulfate will result in the formation of calcium sulfate which also is insoluble. Ammomum sulfate will keep the pH close to neutral while precipitating calcium sulfate. The preferred ammonium salt is ammonium sulfate, although other ammonium salts are considered within the scope of this invention. Iron-rich materials also may be added to be leached and further processed.

The calcium in the waste material typically is in the form of lime (CaO) of which some also is leached by the ammonium chloride. In a fresh ammonium chloride solution, the solubility of calcium is relatively low (on the order of 2-3%). The addition of the calcium ion, along with the processing of the leaching solution at various stages in the process, results in the loss of ammonium ion which is converted into ammonia and lost through the ventilation and scrubber system. This loss of ammonium ion unbalances the equilibrium of ammonium and chloride ions and results in the formation of calcium chloride. As the solution is repeatedly recycled, the concentration of calcium (and hence, calcium chloride) rises.

The solubility of zinc (from zinc oxide) in a fresh ammonium chloride solution (20% at 96°C) is about 13%. As shown in Table IV, the increase in the calcium chloride concentration of the leaching solution reduces the solubility of zinc. This drop in zinc solubility makes each leaching successively less effective since a smaller amount of material can be leached through each cycle.

TABLE IV Soluhilitv of ZnO in aqueous solution at 96°C containing 20% NH4C1

40% NaCl 34% C1 1.6% MgCl₂ and different quantity of CaCl₂ CaCl₂ Concentration

5% 10% 15%

Saturated solution contains: Calcium 1.9% 3.7% 6.5% Magnesium 0.4% 0.4% 0.46% Sodium 1.2% 1.2% 1.4% Zinc 10.8% 8.4% 4.95%

As stated above, the addition of ammomum sulfate to the leaching solution is preferred. The ammonium sulfate can be added to the leach tank prior to charging with dust. The calcium sulfate which forms will be filtered out with the iron cake and returned to the steel making furnace. The calcium will calcine to calcium oxide when it is heated during the steel making process.

Recovery of Ammonium Chloride and Wash Water Purification

The wash water used to wash the zinc compounds precipitated from the product solution contains some ammonium chloride, as well as other compounds. Rather than dispose of this polluted wash water, it can be treated to produce pure water and a more concentrated solution containing ammonium chloride and other compounds. The pure water can be recycled to wash additional zinc compounds precipitated from the product solution, and the concentrated solution can be recycled back to the leaching step. The purification can be accomplished using evaporator condensers or reverse osmosis membrane technology.

From an economically competitive situation, the use of reverse osmosis membrane technology to filter the wash water containing ammonium chloride solution to obtain pure water on one side of the membrane and a concentrated ammonium chloride solution on the other side of the membrane, will save energy costs. Every so often it will be necessary to back flush the salts off of the membrane to recover them for makeup use in the future. In essence, reverse osmosis membrane technology is using a pump to pump the wash water through a membrane, which is significantly lower in cost than burning natural gas in an evaporator condenser to evaporate and recondense distilled water.

Iron By-Product Recycle Iron-rich by-products produced during the recovery process can be processed further to obtain an end product which can be recycled back into the leaching step of the recovery process of the present invention. The iron-rich by-products preferably are reduced to DRI in a reduction furnace. During the reduction process, exhausts fumes which consists primarily of zinc, lead and cadmium are produced in the reduction furnace.

In a first embodiment, the DRI is sent to a steel mill where it is used in the production of steel. The steel production process results in exhaust fumes which are processed through the baghouse or/and a wet scrubber, either or both of which can be located at the steel mill. Fumes processed through the baghouse are filtered, and the captured solid residuum, along with an added amount of EAF dust, is recycled back into the waste materials stream whereby it is returned to the leaching step of the recovery process. Fumes processed through the wet scrubber are scrubbed in a liquid stream and the residual impurities obtained from the scrubbing process are discharged from the wet scrubber directly into the ammonium chloride solution of the leaching step.

In a second embodiment, the fumes exhausted from the reduction furnace used to produce the DRI are processed through the baghouse or/and the wet scrubber. Fumes processed through the baghouse are filtered, and the captured solid residuum is recycled back into the waste material stream, whereby it is returned to the ammonium chloride solution of the leaching step. In this embodiment, no EAF dust need be added in with the solid residuum. Fumes processed through the wet scrubber are scrubbed in a liquid stream and the residual impurities obtained from the filtering process are discharged from the wet scrubber directly into the ammonium chloride solution of the leaching step. Iron-rich products which are produced during the recovery process of the present invention can be further processed to produce fumes consisting primarily of zinc, lead and cadmium which are captured in a baghouse or/and a wet scrubber and recycled back into the ammonium chloride solution of the leaching step to be used in the recovery process. The locations of the baghouse and wet scrubber are a matter of design choice, plant efficiency and convenience. For example, steel mills are equipped with baghouses and wet scrubbers which can be used in the recycling process of the present invention. Similarly, the locations of the baghouse or wet scrubber used to process fumes from the DRI reduction furnace are also a matter of design choice, plant efficiency and convenience.

Preferred Embodiment Referring to Fig. 1 , a preferred embodiment of the process is shown. Subprocess 500 comprises the feed process to the present invention. Feed streams such as iron poor waste fume streams from electric arc furnaces 12 and other furnaces such as reduction furnaces or smelters 14 are filtered in a baghouse 16. Other feed streams such as iron rich DRI and pig iron, as well as scrap iron and steel, are subjected to the iron or steel making process. Exhaust fumes from such processes, which typically include an electric arc furnace or other reduction furnace, also are filtered in a baghouse 16. The constituents filtered out in baghouse 16 comprise the waste stream feed to subprocess 100.

In subprocess 100, the waste stream feed is leached in digester 18 with ammonium chloride, preferably at approximately 90°C and approximately 23% by weight concentration. Constituents soluble in ammonium chloride go into solution, such as zinc oxides, while constituents insoluble in ammomum chloride, such as iron oxides, precipitate out. The precipitates are filtered from the solution in filter 20. The filtered solution is sent to cementer 22, and subjected to subprocess 200 to recover other chemical values. The precipitate, which is an iron cake (IC), is sent to subprocess 300.

Calcium present in the fumes may be leached by the ammonium chloride solution. Due to the continuous nature of the process, calcium impurities may build up, resulting in lower efficiency. A build up of calcium in the ammonium chloride leach will reduce the ability of the ammomum chloride to leach zinc from the waste material. A secondary ammomum salt such as, preferably, ammomum sulfate or ammonium hydroxide, is added to the digester 18 prior to charging with the waste material to precipitate out the calcium ions as calcium sulfate. The loaded recirculating water or ammonium chloride solution (the scrubbant) then may be recycled to the ammomum chloride leach step of the present invention, as discussed below, without creating a calcium build up in the scrubbant.

In subprocess 300, the precipitate is dried and crushed in dryer/crusher 24. Exhaust gases from dryer/crusher 24 may be sent to a baghouse such as baghouse 16, but more typically are sent to an air scrubber such as air scrubber 26 for cleaning, as the exhaust gases from dryer/crusher 24 typically do not have a significant quantity of recoverable constituents. The dried and rushed precipitates are compacted in compactor 28 and sent to a reduction fumace or smelter 14. In reduction furnace 14, the dried and crushed iron cake is roasted at between 980°C and 1315°C, producing an enriched iron cake (EIC) which can comprise DRI and pig iron, which can be in liquid form. The EIC can be compacted in a second compactor 30, and then cooled by cooling water in a cooling conveyor 32, to produce the DRI. The DRI then can be used as the feed to a steel mill EAF, and the process cycle starts over.

Exhaust fumes from the reduction furnace 14 are sent to scrubber 34, which preferably is a recirculating wet scrubber using water or an aqueous ammomum chloride solution. Exhaust fumes from EAF 12 also can be sent to scrubber 34. In scrubber 34, the exhaust fumes are scrubbed and the scrubbed oflf-gas released. The water or aqueous ammomum chloride solution containing the constituents scrubbed from the exhaust fumes is sent either to cementer 22 or digester 18, depending on purity; more pure solutions typically are sent to digester 18, while less pure solutions typically are sent to cementer 22.

In the preferred embodiment, the fumace 12, 14 off-gases comprise ZnO and other paniculate impurities. If the off-gases are scrubbed in scrubber 34, the water balance is maintained using a temperature control such as heat exchanger 36. Additionally, the concentration of ZnO and other solubles in the scrubbing liquid may be controlled by the addition of water W to the cementer 22, or ammonium chloride to the scrubber 34. As discussed above, if an ammomum chloride solution is used as the scrubbing liquid, it is preferred to maintain the solution at approximately 90°C and approximately 23% NT^Cl. Example 1

Prior Art A metal dust of composition listed in Table I of the Burrows patent is added to 23% by weight NH₄C1 solution (30g NH₄C1 per lOOg H₂O), as discussed in the Burrows patent, in the amount of 1 gram of dust per 10 grams of solution. The solution is heated to a temperature of 90°C and stirred for a period of 1 hour, during which the zinc oxide in the dust dissolves. The remaining solid, which has a composition of approximately 60% iron oxide, 5% calcium oxide, 5% manganese, 30% other materials, is filtered out of the solution. Powdered zinc then is added to the filtrate at 90°C, causing the precipitation of waste metals, the precipitate containing about 60% lead, 40% zinc, 2% cadmium and 8% other metals. The waste metals then are filtered out and the filtrate is cooled to room temperature (between about 18°C and 30°C) over a period of about two hours. The solution then contains a white precipitate which is not essentially pure zinc oxide but is a mixture of hydrated zinc phases and diamino zinc dichloride.

Example 2 A metal dust of composition listed in Table I is added to 23% weight NH₄C1 solution (30g NH C1 per lOOg H₂O). 1 gram of dust is used per 10 grams of solution. The solution is heated to a temperature of 90°C and stirred for a period of 1 hour. During this period the zinc oxide in the dust dissolves. The remaining solid, having a composition of approximately 60% iron oxide, 5% calcium oxide, 5% manganese, 30% other materials, is filtered out of the solution. Powdered zinc then is added to the filtrate at 90°C. This causes the precipitation of waste metals, the waste metal precipitate containing about 60% lead, 40% zinc, 2% cadmium and 8% other metals. The waste metals then are filtered out and the filtrate is cooled to room temperature (between about 18°C and 30°C) over a period of about two hours. The solution then contains a white precipitate. The precipitate is a mixture of hydrated zinc phases and diamino zinc dichloride.

The hydrated zinc phases are virtually insoluble in water; however, the measurements in Table III show that diamino zinc dichloride is quite soluble in water. A portion of the white precipitate was dried and zinc oxide and diamino zinc dichloride, as well as some other components, are present. The white precipitate then is filtered from the solution and resuspended in water at 90°C and stirred for a period of one hour. This suspension then is filtered and product dried in an oven at 140°C. The resulting white solid is 99%+ zinc oxide. The amount of zinc oxide obtained was 47.8% of the mass of the original precipitate. The ZnO recovered by this Example also had the following components: lead: 866 ppm

Potassium: 45 ppm calcium: < 25 ppm manganese: < 25 ppm chromium: < 25 ppm

Example 3 The procedure of Example 1 is followed until the step in which the zinc containing filtrate is cooled. Since the diamino zinc dichloride is more soluble then the majority of the other possible precipitates in the ammonium chloride solution (except for zinc chloride which is so soluble that it will not appear), the diamino zinc dichloride appears as a larger fraction of the solid as the temperature declines. The filtrate was divided into fractions and each fraction cooled to a different temperature. The resulting solids were than filtered, resuspended in water at 90°C for one hour, filtered and dried. The result was 99%+ zinc oxide in all cases; however, the yield changed with the temperature to which the fraction was cooled as follows: Crystallization Percent ZnO

Tem rø Obtained

75 65

70 60

60 60

50 50

Crystallization at temperatures from 60°C up improve the yield of ZnO.

Example 4 ZnO also can be recovered from the wash water used in the process. Fifty grams of dried zinc phase precipitate (the solid obtained after cooling to room temperature) obtained using the procedure of Example 1 is added to lOOg of H₂O at 90°C. The diamino zinc dichloride dissolves while only a small amount of the other zinc phases dissolve (due to the ammonium chloride which is part of the diamino zinc dichloride). The remaining solid is filtered out and is dried resulting in 99%+ zinc oxide. The filtrate is cooled to room temperature and the solid filtered out. The solid is again a mixture of hydrated zinc phases and Zn(NH₃)₂Cl₂. The solid is washed in 90°C water, filtered and dried resulting in 99% ZnO. The yield is 40% ZnO.

The yield also can be improved by crystallizing at higher temperatures. In addition, the same wash water can be used again instead of fresh water since this part of the process relies on the change in Zn(NH₃)₂ solubility with temperature.

Example 5 The source of the zinc does not have to be dust. If pure ZnO is added to a 23% NR,C1 solution, the result is the same. As an example, saturated solutions of ZnO in 23% ammonium chloride solutions were prepared at temperatures ranging from 40°C - 90°C, using the solubility data of Table II. These solutions were then cooled to room temperature over a period of 1 - 2 hours. The resulting solid was filtered, washed in 90°C water, and dried. As before, the original solid was a mixture of hydrated zinc phases and diamino zinc dichloride, the final product was 99% ZnO. The yields obtained as a fraction of the original solid precipitate are listed below: 96/08585 PCI7US95/11367

37

Temperature ZnO Added ZnO Obtained in Product

(°C\ < (% .

90 14.6 . 64

80 13.2 62

70 8.4 60

60 5.0 60

50 3.7 45

40 2.3 40 These results indicate that the yield of ZnO improves as the amount of dissolved ZnO increases (which also means higher temperatures).

Example 6 This example shows the present procedure run in a continuous crystallization process to increase the throughput and to maximize the zinc oxide yield. The procedure of Example 1 is followed until the step in which the waste metals are precipitated out of the zinc oxide containing solution. Fifty gallons of the solution are used as the feedstock for a continuous crystallization process. The solution, initially at about 90°C, is pumped into a 1 -gallon jacketed crystallizer equipped with baffles and a draft tube at a rate of 1 gallon per hour. The crystallizer jacket temperature is maintained at about 55°C by use of a constant temperature circulating bath. The solution and the product crystals are removed continuously so as to keep the volume of material present in the crystallizer constant. At steady state, the temperature in the crystallizer is maintained at about 60°C. The product solution flows through a filter which collects the solid. The solid product then undergoes the washing and drying steps as discussed in Example 2. The yield of zinc oxide from this continuous crystallization process is about 60% of the total mass of the solid crystallized.

The crystallizer can be operated at lower temperatures; however, lower temperatures decrease the final yield of zinc oxide obtained as shown in Example 3. The flow rate employed also can be altered along with the crystallizer jacket temperature to minimize crystallization on the crystallizer vessel walls. In addition, these variables, along with the crystallizer jacket temperature, can be used to alter the crystal size distribution.

Example 7 Metal dust of the composition shown in Table I is digested in 23% ammonium chloride solution at about 90°C. One gram of zinc metal dust is used per 10 grams of ammonium chloride solution. After one hour, the remaining solid is filtered out of the solution. 500 cc of the solution is put into each of two vessels with stirrers and the temperature of the solutions is maintained at 90°C. 500 ppm of Flocon 100 is added to one of the vessels, while nothing is added to the other vessel. Four-tenths of a gram (0.4g) of 200 mesh zinc dust then is added to each of the two solutions. In the solution containing the Flocon 100, the zinc dust remains suspended, while in the other solution containing no additive, the zinc dust clumps together (flocculates). After one hour at about 90°C, the solids are filtered out of each of the solutions, weighed and analyzed. The mass of solid from the solution which contained the dispersant was 1.9 grams and comprised approximately 21% zinc, 75% lead, 2% cadmium and the remaining amount other metals. The mass of solid obtained from the solution with no dispersant was 1.2 grams and comprised approximately 33% zinc, 63% lead, 2% cadmium and the remaining amount other metals. From this example, it can be seen that the additional step of adding a dispersant increases the amount of lead and other metals removed from the waste stream in solution.

Example 8 A dust containing 19.63% Zn, 27.75% Fe, 1.31% Pb, 9.99% Ca, and 0.024% Cd (analysis based on elements not oxides) was leached at 100°C in a 23% ammonium chloride solution. The solid remaining after the leaching process was dried and analyzed to contain 12.67% Zn, 4.6% Ca, 35.23% Fe, 0.7% Pb, and 0.01% Cd. This material was placed in a quartz boat in the presence of activated carbon and heated at 900°C for two hours in an atmosphere of 95% N₂ and 5% O₂. After two hours, the material was removed and added to a 23% ammonium chloride solution at 100°C. The material was filtered and dried at 140°C for one hour to determine its composition. Analysis of this remaining solid was 42.84% Fe, 0.28% Zn, < 0.1% Pb, and < 0.01% Cd. The leached-roasted-leached material then can be subjected to the remainder of the general process to recover zinc oxide.

Example 9 A dust with composition given μi Table I is leached in 23% ammonium chloride solution for 1 hour at 100°C. The solid remaining (which contained 14% Zn) was placed in a quartz boat and heated to 700°C in an atmosphere of 8% H₂ and 92% Ar. The material was cooled and reheated at 100°C in 23% ammonium chloride solution at 100°C. The solid was separated, dried and analyzed for zinc. The zinc was found to be less than 1%. The leached-roasted-leached material then can be subjected to the remainder of the general process to recover zinc oxide.

Example 10 A dust of the composition given in Table I is taken through the leaching and cementation steps. After cementation the filtrate is maintained at 100°C. 500 ml of this filtrate is placed in a jacketed stirred vessel with the jacket temperature at 100°C. The temperature is lowered in the crystallizer as follows:

Time (minutes) Temperature (°C)

0 100

60 90

120 75 180 55

210 25

The resulting solid was washed and dried employing the procedure described above. The resulting material was analyzed as follows:

ZnO 99 + % Lead < 50 ppm

Cd < 25 ppm

Fe < 25 ppm

The cooling profile in Example 10 is known as a reverse natural cooling profile. Such a profile is the opposite shape as that which is observed by natural cooling. In a reverse natural cooling profile, the cooling is slower at the beginning and faster at the end; in a natural cooling profile, the cooling is faster at the beginning and slower at the end. This type of cooling profile also is used to control the crystal size distribution (CSD) of the zinc oxide obtained. The cooling profile controls the ratio of nucleation (birth of a new crystal) to crystal growth (growth of existing crystals). The ratio of nucleation/growth determines the final CSD.

Example 11

A 23% ammonium chloride solution at 100°C containing 11% by weight dissolved ZnO is divided into 4 portions. Each portion is placed in a jacketed agitated vessel. The cooling profiles in each vessel are given below:

Vessel A Vessel B

Time (minutes) Temp. (°C) Time (minutes) Temp. (°C)

0 100 0 100

60 75 60 50

120 50 120 37.5

180 25 180 25

Vessel C Vessel D

Time (minutes) Temp. (°C) Time (minutes) Temp. (°C)

0 100 0 100

60 87.5 60 87.5

120 75 120 75

180 25 180 62.5 270 25

The solid is washed using the usual procedures described previously. The average size and size distribution of these materials were measured using a laser light scattering particle size analyzer. The results were as shown below: Vessel Mean Size

A 22

B 19

C 27

D 37 The results show that controlling the temperature with a reverse natural cooling curve results in a larger average size than by linear cooling (A) or natural cooling (B). This principle can be employed to design cooling profiles to produce zinc oxides of a desired average size and distribution. Example 12

By controlling the recycle, the steady state zinc concentration can be raised to 7g/100g of solution. If the outlet of the crystallizer is kept at 60°C, 3g/100g solution of solid will crystallize (the solid is a mixture of zinc oxide and diamino zinc dichloride). The system does not have to be cooled further since this is an efficient way to operate to conserve energy (one does not have to cool then reheat the solution). In addition, operating at the higher Zn concentration improves the ratio of ZnO/diamino zinc dichloride produced in the crystallizer.

The recycle has the advantage that the solution becomes saturated relative to certain materials present in the dust, such as CaO. When this occurs, CaO no longer is leached from the dust but remains with the iron in the iron cake. This increases the value of the cake since CaO is still present and will not have to be added when the iron cake is fed to a fumace in steel making. Another important advantage in that there is no liquid effluent in this process. The only products are solid (iron cake, zinc oxide, waste metals), which are then sold for use in various industrial processes. No waste is produced since all liquid is recycled.

Example 13 A sample of the mixed waste metals cake was taken fresh from the mixed metals press and placed into an air tight plastic bag. The cake was mixed within the bag and excess liquid was removed by allowing the bag to drain. Attempts were made to exclude air from the bag as well. The major elemental composition of this cake material tested to be: ElementWeight %

Cdl.5 Cul.O Pbl9.2

Zn2.1 Other materials present include water and ammonium chloride, as well as oxides of the mixed metals.

A sample of this mixed metals cake was taken from the bag, added to a beaker, and washed with an equal weight of warm water on a hot plate with mechanical stirring.

Some white precipitate, mainly zinc oxide, formed by the decomposition of the complex diamino-zinc salt. The washing step was carried out to remove ammonium chloride, and other soluble components, if present.

The wash water was decanted from the product. Fresh water was added, enough to cover the solids, to prevent any further air oxidation of the solids and a large excess of sulfuric acid added in stages over several days, during which time bubbling was noted. No heating was applied. Additional sulfuric acid was added when the pH of the mixture reached 5. The solution was mixed and then allowed to react, without further mixing. When analyzed the elemental composition was: Element Weight %

Cd0.19 Cu4.1 Pb43.2 Zn0.04 The solid was observed with crossed polars under a microscope, and a great deal of crystalline-"non-metallic" material was noted. A majority of this material likely is lead sulfate, formed by the reaction of the lead metal with the acid. Remainders are likely to be copper and lead metal. The solution produced in this process also was analyzed and found to contain zinc and cadmium in large amounts, while having very low concentrations of copper and lead. This solution can be further treated by cementation processes, if desired to produce high purity cadmium metal. Example 14

A second batch of washed mixed metals was taken from the waste metals cake described in Example 13 and treated hot with a limiting amount of sulfuric acid (lOg acid/1 OOg mixed metals). Reaction was allowed to continue for 4 hours. At the end of this time the pH increased to 6, meaning the acid had been completely reacted with the product.

A sample of the remaining solids was collected and allowed to air dry on a warm glass slide. It was analyzed to contain:

ElernentWeight % Cdl.9

Cu4.0

Pb78

Zn2.9

By microscopy, the product appeared to be much higher in metallic solids than the previous run. Some crystalline material similar to the previous material was noted, however.

The above description sets forth the best mode of the invention as known to the inventor at this time, and the above Examples are for illustrative purposes only, as it is obvious to one skilled in the art to make modifications to this process without departing from the spirit and scope of the invention and its equivalents as set forth in the appended claims.

Claims

What is claimed is:

1. A continuous method for the recovery of metal and chemical values from waste material streams which comprise iron compounds and zinc compounds, comprising the steps of: a. preroasting said waste material stream at an elevated temperature resulting in the reduction of at least a portion of the iron oxides into direct reduced iron and the production of exhaust vapors comprising zinc, lead, and cadmium compounds; b. treating said exhaust vapors with an ammomum chloride solution at an elevated temperature to form a product solution which comprises dissolved constituents and an undissolved precipitate, whereby any iron oxide in said waste material will be contained in said undissolved precipitate and will not go into solution; c. separating said product solution from said undissolved precipitate; and d. roasting said undissolved precipitate at an eleveted temperature resulting in the reduction of the iron oxide into direct reduced iron.

2. The method as claimed in Claim 1, further comprising the step of combining an iron oxide rich material with the waste material stream prior to preroasting said waste material stream.

3. The method as claimed in Claim 1, further comprising the step of combining an iron poor material with the waste material stream prior to preroasting said waste material stream.

4. The method as claimed in Claim 1 , further comprising the steps of: e. adding a zinc compound to said product solution whereby lead, copper and cadmium contained in said product solution are removed by precipitation with said zinc compound thereby producing a waste metals cake comprising lead and cadmium; f. treating the waste metals cake in a dissolving solution wherein zinc and cadmium are soluble and lead is insoluble; g. recovering the lead by separating the lead from said dissolving solution; and h. recovering the cadmium from said dissolving solution by electrochemical means.

5. The method as claimed in Claim 1 , further comprising the steps of: e. cooling said product solution in a controlled manner; and f. precipitating zinc oxide crystals out of said product solution in a controlled manner such that the zinc oxide crystals have predetermined purity and particle characteristics.

6. The method as claimed in Claim 1 , further comprising the steps of: e. adding zinc metal to said product solution whereby any zinc- displaceable metal ions contained within said product solution are displaced by said zinc metal and precipitate out of said product solution as metals; f. separating said metals from said product solution and lowering the temperature of said product solution thereby precipitating at least a portion of any zinc component of said product solution as a mixture of crystallized zinc compounds; g. separating said crystallized zinc compounds from said product solution and washing said crystallized zinc compounds with a wash water thereby solubilizing certain of said zinc compounds; and h. separating any remaining crystallized zinc compounds from said product solution and drying said remaining crystallized zinc compounds at a temperature of between about 100°C and 200°C resulting in the recovery of a zinc oxide product of 99% or greater purity.

7. The method as claimed in Claim 1, further comprising the steps of: a. initially combining an iron oxide rich material with said waste material stream to produce a waste material combination; b. pretreating said waste material combination a first time with a 23% by weight ammonium chloride solution at an elevated temperature to form a first product solution which comprises dissolved constituents and an undissolved precipitate, whereby any iron oxide in said waste material will be contained in said undissolved precipitate and will not go into solution; c. separating said first product solution from said undissolved precipitate; d. preroasting said undissolved precipitate at a temperature of at least 500°C in a reducing atmosphere resulting in the reduction of at least a portion of the iron oxides into direct reduced iron and the production of exhaust vapors; and e. carrying out steps b through d of Claim 1, wherein said roasting takes place at a temperature of between 980°C and 1315°C.

8. The method as claimed in Claim 7, further comprising the step of adding carbon to said exhaust vapors and ammonium chloride combination whereby said carbon will not go into solution.

9. The method as claimed in Claim 1 , further comprising the steps of: d. treating said product solution with a leachant solution comprising of sulfuric acid until at least a substantial portion of the zinc is dissolved and any lead in said product solution will not go into solution and separating said lead from said solution; e. adding a compound selected from the group consisting of zinc oxide and zinc hydroxide to said product solution to increase the pH of said product solution to a sufficient level to cause the formation of precipitates of sulfate salts and separating said salts from said product solution; f. adding a zinc metallic dust to said product solution to achieve a first cementation step causing the formation of copper solids and separating at least a portion of said copper solids from said product solution; and g. adding a zinc metallic article to said product solution in an electrolysis step causing the formation of a cadmium sponge on said zinc metallic article and separating at least a portion of said cadmium sponge from said product solution.

10. The method as claimed in Claim 1, further comprising the step of treating said product solution with a stoichiometrically suitable amount of a soluble ammonium salt in which the negative ion will form an insoluble compound with the calcium to form a product solution substantially free of calcium products and an undissolved calcium compound precipitate.

11. The method as claimed in Claim 10, further comprising the step of preroasting said waste material at an. elevated temperature of at least 500°C in a reducing atmosphere prior to treating said exhaust vapors with the ammomum chloride solution.

12. The method as claimed in Claim 11, wherein said undissolved precipitates are roasted at an elevated temperature to reduce any iron oxide in said undissolved precipitates into direct reduced iron.

13. The method as claimed in Claim 12, wherein said preroasting step takes place in a rotary hearth furnace.

14. The method as claimed in Claim 13, wherein said waste material stream is selected from the group consisting of waste streams from said roasting step, waste streams from ore smelting processes, waste streams from metals making processes, waste streams from metals products making processes, waste streams from iron-making processes, and waste streams from steel-making processes.

15. The method as claimed in Claim 14, wherein said undissolved precipitate is roasted at a temperature of between 980°C and 1315°C.

16. The method as claimed in Claim 1, further comprising the step of treating the exhaust vapors in the ammonium chloride solution with a soluble ammomum salt in which the negative ion will form an insoluble compound with the calcium constituent.

17. The method as claimed in Claim 16, wherein said undissolved precipitate is roasted at a temperature of between 980°C and 1315°C and the concentration of said ammomum chloride solution is approximately 23% by weight.

18. The method as claimed in Claims 1 through 6, wherein said undissolved precipitate is roasted at a temperature of between 980°C and 1315°C.

19. The method as claimed in Claim 18, wherein said ammonium chloride solution is 23% ammonium chloride by weight in an aqueous solution.

20. The method as claimed in Claim 1 through 19, further comprising the steps of: e. treating said preroasted waste material with an ammomum chloride solution at an elevated temperature to form a second product solution which comprises dissolved constituents and a second undissolved precipitate, whereby any iron oxide in said waste material will be contained in said second undissolved precipitate and will not go into solution; f. separating said second product solution from said second undissolved precipitate; and g. roasting said second undissolved precipitate at an eleveted temperature resulting in the reduction of the iron oxide into direct reduced iron.

21. The method as claimed in Claim 20, further comprising the step of precombining said waste material with carbon prior to preroasting said waste material.

22. The method as claimed in Claim 20 further comprising the steps of: h. adding zinc metal dust to said second product solution resulting in the cementation of said lead and said cadmium; and i. cooling said second product solution resulting in the crystallization of zinc compounds.

23. The method as claimed in Claim 22, wherein said undissolved precipitate is roasted at a temperature of between 980°C and 1315°C.

24. The method as claimed in Claim 21, wherein said preroasting of said waste material occurs at a temperature of at least 500°C and in a reducing atmosphere comprising carbon.

25. The method as claimed in Claim 24, further comprising the steps of: h. adding zinc metal to said second product solution whereby any zinc-displaceable metal ions contained within said second product solution are displaced by said zinc metal and precipitate out of said second product solution as metals; i. separating said metals from said second product solution and lowering the temperature of said second product solution thereby precipitating at least a portion of any zinc component of said second product solution as a mixture of crystallized zinc compounds; j. separating said crystallized zinc compounds from said second product solution and washing said crystallized zinc compounds with a wash water thereby solubilizing certain of said zinc compounds; and k. separating any remaining crystallized zinc compounds from said second product solution and drying said remaining crystallized zinc compounds at a temperature of between about 100°C and 200°C resulting in the recovery of a zinc oxide product of 99% or greater purity.

26. The method as claimed in Claims 5, 6, 22, or 25, further comprising the steps of washing and drying said zinc oxide crystals.

27. The method as claimed in Claim 26 wherein said zinc oxide crystals are precipitated by diluting said product solution at a predetermined rate by a factor ranging from 3 to 30 at a temperature ranging from 70°C to 100°C to precipitate said zinc oxide crystals.

28. The method as claimed in Claim 27 wherein said product solution is diluted by a factor of 3 - 5 at a temperature of approximately ranging from 90°C to 100°C.

29. The method as claimed in Claim 28 wherein said waste material stream is first treated with an intermediate selected from the group consisting of sodium hydroxide, ammonium sulfate, ammonium chloride liquor, ammonium phosphate, potassium hydroxide, ammonia/ammonium oxalate, and ammonia/ammonium carbonate solutions to produce said product solution.

30. The method as claimed in Claim 29 wherein said intermediate is a concentrated 50% - 70% sodium hydroxide solution.