WO2003076070A1 - Regeneration, pretreatment and precipitation of oxides of manganese - Google Patents

Regeneration, pretreatment and precipitation of oxides of manganese Download PDF

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Publication number
WO2003076070A1
WO2003076070A1 PCT/US2003/007098 US0307098W WO03076070A1 WO 2003076070 A1 WO2003076070 A1 WO 2003076070A1 US 0307098 W US0307098 W US 0307098W WO 03076070 A1 WO03076070 A1 WO 03076070A1
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WIPO (PCT)
Prior art keywords
manganese
oxides
solution
temperature
stability area
Prior art date
Application number
PCT/US2003/007098
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English (en)
French (fr)
Inventor
Charles F. Hammel
Richard M. Boren
Patrick A. Tuzinski
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Enviroscrub Technologies Corporation
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Filing date
Publication date
Priority claimed from US10/328,490 external-priority patent/US7041270B2/en
Application filed by Enviroscrub Technologies Corporation filed Critical Enviroscrub Technologies Corporation
Priority to AU2003218018A priority Critical patent/AU2003218018A1/en
Priority to JP2003574330A priority patent/JP2005518938A/ja
Priority to PCT/US2003/018419 priority patent/WO2004009232A1/en
Priority to AU2003239975A priority patent/AU2003239975A1/en
Priority to US10/461,888 priority patent/US20040101457A1/en
Publication of WO2003076070A1 publication Critical patent/WO2003076070A1/en

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    • C22B47/0018—Treating ocean floor nodules
    • C22B47/009—Treating ocean floor nodules refining, e.g. separation of metals obtained by the above methods
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    • B01J23/32—Manganese, technetium or rhenium
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    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
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Definitions

  • the invention relates to systems and processes for pretreatment, regeneration and formation of oxides of manganese that have high oxidation states and/or high pollutant loading capacities which are suitable, amongst other uses, as a sorbent for capture and removal of target pollutants from industrial and other gas streams. Further, the invention relates to oxides of manganese so treated, regenerated or formed.
  • Oxides of manganese are utilized for a number of industrial applications, such as pollution control systems, steel manufacture, batteries and catalytic converters, to name a few.
  • interest to Applicants is the use of oxides of manganese in pollution control systems.
  • Applicants are co-inventors of the subject matter of co-pending U.S. patent applications numbers 09/919,600, 09/951,697, 10/044,089 and 10/025,270, the disclosures of which are incorporated herein by reference. These applications disclose pollutant removal systems and processes, known as PahlmanTM systems and processes, which utilize dry and wet removal techniques and combinations thereof, incorporating the use of oxides of manganese as a sorbent for capture and removal of target pollutants from gas streams.
  • PahlmanTM systems and processes which utilize dry and wet removal techniques and combinations thereof, incorporating the use of oxides of manganese as a sorbent for capture and removal of target pollutants from gas streams.
  • target pollutant refers to the pollutant or pollutants that are to be captured and removed from a gas stream.
  • target pollutants that may be removed with an oxide of manganese sorbent include, but are not limited to, NOX, SOX, mercury (Hg) and mercury compounds, H2S and other totally reduced sulfides (TRS), chlorides, such as hydrochloric acid (HC1), and oxides of carbon (CO and CO2).
  • oxides of manganese and/or "sorbent” to oxides of manganese or sorbent that has interacted with one or more target pollutants in a gas whether by chemical reaction, adsorption or absorption.
  • the term does not mean that all reactive or active sites of the sorbent have been utilized as all such sites may not actually be utilized.
  • oxides of manganese and/or "sorbent” to oxides of manganese or sorbent that has not interacted with target pollutants in a gas or gas stream.
  • Nirates of manganese refers to and includes the various forms of manganese nitrate, regardless of chemical formula, that may be formed through the chemical reaction between NOX and the sorbent and includes hydrated forms as well.
  • Sulfates of manganese refers to and includes the various forms of manganese sulfate, regardless of chemical formula that may be formed through the chemical reaction between SOX and the sorbent and includes hydrated forms as well. Oxides of manganese in various forms, utilized as sorbents, are introduced into the
  • PahlmanTM systems and other pollution removal systems
  • the target pollutants in gas streams routed through the systems as a catalyst, a' reactant, an absorbent or an adsorbent.
  • the oxidation (or valence) state of the oxides of manganese sorbent is reduced from its original state during reaction with the target pollutants.
  • pollutant removal occurs possibly through overall reactions such as the following:
  • manganese (Mn) is reduced from the +4 valence state to +2 valence state during formation of the reaction products shown. It should be noted that the actual reactions may include other steps not shown, and that indicating Reactions 1 and 2 is solely for illustrative purposes.
  • the element manganese (Mn), and therefore oxides of manganese may exist in six different valence (oxidation) states. Of particular interest and usefulness for gaseous pollutant removal are those oxides of manganese having valence states of +2, +3, and +4, which correspond to the oxides MnO, Mn2O3, MnO2 and Mn3O4.
  • the oxide Mn3O4 is believed to be a solid-solution of both the +2 and +3 states.
  • a characteristic of most oxides of manganese species is non-stoichiometry.
  • most MnO2 species typically contain on average less than the theoretical number of 2 oxygen atoms, with numbers more typically ranging from 1.5 to 2.0.
  • the non- stoichiometry characteristic of oxides of manganese is thought to result from solid-solution mixtures of two or more oxide species (such as may occur in the oxide Mn3O4), or distortions of molecular structure and exists in all but the beta ( ⁇ ), or pyrolusite, form of manganese dioxide.
  • Oxides of manganese having the formula MnOX where X is about 1.5 to about 2.0 are particularly suitable for use as sorbent for dry removal of target pollutants from gas streams and may be also be utilized in wet removal.
  • oxides of manganese for use as a sorbent for target pollutant removal usually have the formula MnO1.7 to 1.95, which translates into average manganese valence states of +3.4 to +3.9, as opposed to the theoretical +4.0 state. It is unusual for average valence states above about 3.9 to exist in most forms of oxides of manganese.
  • Oxides of manganese are known to exhibit several identifiable crystal structures, which result from different assembly combinations of their basic molecular structural units.
  • These basic structural "building block” units are MnO6 octahedra, which consist of one manganese atom at the geometric center, and one oxygen atom at each of the six apex positions of an octahedral geometrical shape.
  • the octahedra may be joined together along their edges and/or corners, to form “chain” patterns, with void spaces ("tunnels").
  • Regular (and sometimes irregular) three-dimensional patterns consist of layers of such "chains" and "tunnels" of joined octahedra.
  • crystalline geometries are identified by characteristic x- ray diffraction (XRD) patterns.
  • XRD characteristic x- ray diffraction
  • Most oxides of manganese are classifiable into one or more of the six fundamental crystal structures, which are called alpha ( ), beta ( ⁇ ), gamma ( ⁇ ), delta ( ⁇ ), epsilon ( ⁇ ), and ramsdellite.
  • Certain older literature also included rho (p) and lambda ( ⁇ ) structures, which are now thought obsolete, due partly to improvements in XRD technique.
  • Some (amorphous) forms of MnO2 exhibit no crystalline structure.
  • oxides of manganese probably arise from the size and shape of voids within these crystalline patterns and from certain elements, and compounds, which may occupy the voids and appear to help prevent collapse of certain structures. Applicants believe that these characteristics in addition to the oxidation state may have an affect upon the loading capacity of oxides of manganese sorbent. Further, many oxides of manganese, including those that are the subject of the present, come in hydrated or hydrous forms, having water chemically bound or combined to or within their crystalline structures, containing one or more molecules of water; this is sometimes referred to as bound water, structural water, water of crystallization or water of hydration. In these forms, the water is combined is such a way that it may be removed with sufficient heat without substantially changing the chemical structure of the oxides of manganese. Such oxides of manganese are also useful as a sorbent.
  • This bound water may also contribute to the chemical reactivity and possibly catalytic
  • MnO Manganous oxide
  • Mn(OH)2 will oxidize to MnO2 in the presence of air, for example.
  • the dioxides of manganese are themselves oxidizers. They readily exchange oxygen in chemical reactions and are known to have catalytic properties. This oxygen exchange ability may be related to proton mobility and lattice defects common within most MnO2 crystal structures.
  • the oxidizing potential of MnO2 is advantageously utilized in target pollutant removal in the PahlmanTM and other pollutant removals systems and processes.
  • Target pollutants such as NOX, SO2, CO, and CO2 gases, mercury (Hg) and other pollutants
  • MnO2 sorbent require oxidation of the species prior to reaction with MnO2 sorbent to form reaction products, such as manganese sulfates, nitrates, and carbonates, mercury compounds, and other corresponding reaction products, in order for them to be captured and removed from gas streams.
  • Manganese compounds or salts are soluble in water in the +2 valence state, but not in the +4 state.
  • Manganese compounds having an average valence state approaching +2 are soluble in water, while those with average valence states approaching +4 are not. Therefore Mn+2 compounds, including MnO are readily soluble in aqueous solutions, as opposed to MnO2.
  • reaction products such as manganese nitrates and sulfates, the manganese is reduced from about the +4 state to the +2 state.
  • reaction products formed on the surface of oxides of manganese sorbent particles to be readily dissolved and removed from the sorbent particles in aqueous solutions by disassociation into reaction product anions, such as sulfate or, nitrate, and manganese cations such as Mn+2 cations.
  • Manganese dioxides are divided into three origin-based categories, which are: 1) natural (mineral) manganese dioxide (NMD), 2) chemical manganese dioxide (CMD), and 3) electrolytic manganese dioxide (EMD).
  • NMD natural (mineral) manganese dioxide
  • CMD chemical manganese dioxide
  • EMD electrolytic manganese dioxide
  • NMD occurs naturally as various minerals, which may be purified by mechanical or chemical means.
  • the most common form of NMD is pyrolusite ( ⁇ -MnO2), which is inexpensive, but has rather low chemical activity and therefore low pollutant loading capacity.
  • CMD and EMD varieties are synthetic oxides of manganese. EMD is produced primarily for the battery industry, which requires relatively high bulk density (which often results from relatively large, compact particles), relatively high purity, and good electrochemical activity.
  • Oxides of manganese have the ability to capture target pollutants from gas streams, however, the low pollutant loading rates achieved with various prior art oxides of manganese have made some industrial applications of this ability uneconomical.
  • the low target pollutant loading rates of various prior art oxides of manganese sorbents would require voluminous amounts to effectively capture large quantities of target pollutants that exist at many industrial sites, e.g., NOx and/or SO2.
  • the large quantity of sorbent that would be required to capture NOx and/or SO2 could result in an overly costly pollutant removal system and sorbent regeneration system. It would therefore be desirable to enhance the loading capacities of the oxides of manganese sorbent in order to economically implement a pollution removal system utilizing oxides of manganese.
  • reaction products such as the manganese salts of Reaction (1) and Reaction (2) above, form on the surfaces of the sorbent particles of oxides of manganese. These reactions may extend to some depth inside the sorbent particles and into the pores and micro fissures. Applicants believe that formation of such reactions products occurs primarily on the surfaces of the oxides of manganese particles, resulting in a layer or coating, which effectively isolates the covered portion of the particle surface and thereby prevents continued rapid reaction with additional target pollutants. Further, the oxidation state and thus the loading capacity of the oxides of manganese below the surface of the reaction product coating may be reduced during the pollutant removal, thus diminishing the loading capacity of sorbent even after the reaction product have been removed or disassociated into an aqueous solution.
  • Applicants have developed methods of producing newly precipitated oxides of manganese, of treating commercially available virgin oxides of manganese, and of regenerating loaded oxides of manganese that results in the production of oxides of manganese useful, amongst other applications as sorbent for pollutant removal.
  • Oxides of manganese so produced may exhibit high or increased loading capacity and/or valence states as compared to reacted and virgin oxides of manganese of various forms, including a variety of commercially available oxides of manganese.
  • Applicants have additionally developed a system and process for cyclically loading, with target pollutants, and regenerating oxides of manganese sorbent that results in the production of useful byproducts.
  • Figure 1 is a Pourbaix diagram for an aqueous solution of 1 mole/liter manganese ion concentration.
  • Figure 2 is a Pourbaix diagram for an aqueous solution of 10-6 mole/liter manganese ion concentration.
  • Figure 3 is a block flow diagram of a system and process according to the invention.
  • Figure 2 is a block flow diagram of a system and process according to the invention.
  • Figure 3 is a block flow diagram of a system and process according to the invention.
  • Figure 4 is a block flow diagram of a system and process according to the invention.
  • Figure 5 is a block flow diagram of a system and process according to the invention.
  • Figure 6 is a block flow diagram of a system and process according to the invention.
  • Figure 7 is a block flow diagram of a system and process according to the invention.
  • Figure 8 is a block flow diagram of system and process according to the invention with electronic controls.
  • Figure 9 is a block flow diagram of system and process according to the invention with electronic controls.
  • Figure 10 is a block flow diagram of system and process according to the invention with electronic controls.
  • Figure 11 is a block flow diagram of an electrolytic cell by-products production system and process according to the invention.
  • Figure 12 is a graph plotting SOX loading capacities of oxides of manganese.
  • Figure 13 is a graph plotting NOX loading capacities of oxides of manganese.
  • Figure 14 is a graph plotting pH and Eh values relative to processing times.
  • Figure 15 is a graph plotting pH and Eh values relative to processing times with and without pH control.
  • the invention relates to methods and systems and processes for regeneration, precipitation and pretreatment of oxides of manganese that, amongst other uses, are utilized as a sorbent for removal of target pollutants from a gas stream.
  • the oxides of manganese processed in the methods and systems of the invention exhibit high pollutant loading capacities and/or oxidation states as appropriately compared to virgin oxides of manganese.
  • the invention loaded oxides of manganese particles bearing manganese salt reaction products on the surface of the particles, the reaction products being formed by reaction between target pollutants and virgin oxides of manganese, the loaded oxides of manganese are for rapid and adaptive regenerated.
  • the method of this embodiment comprises the steps of: rinsing the loaded oxides of manganese in a pre- oxidation aqueous rinse solution to the dissolve reaction products into solution, thereby removing reaction products from the surface of the oxides of manganese; separating or filtering the rinsed oxides of manganese from the solution, the solution being directed as a pre-oxidation filtrate for further processing or handling; feeding the rinsed oxides of manganese into regeneration vessel containing a heated aqueous oxidizing solution under agitation and mixing the solution to form a slurry, the solution being prepared so as to have Eh and pH values within the MnO2 stability area for an aqueous solution heated to a temperature at or near boiling temperature at atmospheric pressure; monitoring and adjusting solution temperature, Eh value and pH value so as to rapidly move solution conditions into and to maintain them within the MnO2 stability area; and maintaining the solution conditions within the MnO2 stability area until the oxides of manganese are regenerated so as to have pollutant loading capacity and/
  • loaded oxides of manganese particles bearing manganese salt reaction products on the surface of the particles are for rapid and adaptive regenerated.
  • the method of this embodiment comprise the steps of: feeding the loaded oxides of manganese into a regeneration vessel containing a heated aqueous oxidizing solution under agitation and mixing the solution to form a slurry containing manganese cations and anions of manganese salt which have been dissolved and disassociated into the solution, the solution being prepared so as to have Eh and pH values within the MnO2 stability area of an aqueous solution heated to a temperature at or near boiling temperature at atmospheric pressure and being heated to a temperature at or near the boiling temperature; monitoring and adjusting solution temperature, Eh value and pH value so as to rapidly move solution conditions into and to maintain them within the MnO2 stability area; and maintaining the solution conditions within the MnO2 stability area so as to precipitate the manganese cations out of solution as precipitated oxides of manganese and so as to regenerate the oxide of manganese particles; the precipitated and regenerated oxides of manganese having loading capacities and/or average oxidation states at least equal to that of the virgin oxides
  • virgin of virgin oxides of manganese are rapidly and adaptively preheated to increase their loading capacity and/or their average oxidation state.
  • the method of this embodiment of the invention comprises the steps of: optionally rinsing the virgin oxides of manganese in an aqueous rinse solution to remove impurities; feeding the virgin oxides of manganese into a regeneration vessel containing a heated aqueous oxidizing solution under agitation and mixing the solution to form a slurry, the solution being prepared so as to have Eh and pH values within the MnO2 stability area for an aqueous solution heated to a temperature at or near boiling temperature at atmospheric pressure; monitoring and adjusting solution temperature, Eh value and pH value so as to rapidly move solution conditions into and to maintain them within the MnO2 stability area; and maintaining the solution conditions within the MnO2 stability area until preheated oxides of manganese obtain pollutant loading capacities and/or average oxidation states greater that of the virgin oxides of manganese originally fed into
  • oxides of manganese are rapidly and adaptively precipitated.
  • This embodiment of a method according to the invention comprises the steps of: mixing a heated solution containing cations and anions of disassociated manganese salts and a heated aqueous oxidizing solution in a precipitation vessel to form a solution mixture, the heated aqueous oxidizing solution being prepared so as to have Eh and pH values within the MnO2 stability area of an aqueous solution heated to a temperature at or near boiling temperature at atmospheric pressure and being heated to a temperature at or near the boiling temperature; monitoring and adjusting the temperature, Eh value and pH value of the solution mixture so as to rapidly move mixture conditions into and to maintain them within the MnO2 stability area; and maintaining the solution conditions within the MnO2 stability area so as to precipitate the manganese cations out of solution as precipitated oxides of manganese having high loading capacities and/or high average oxidation states.
  • loaded oxides of manganese are rapidly and adaptively regenerated and oxides of manganese are rapidly and adaptively precipitate from a solution containing dissolved or disassociated manganese salt reaction products borne on the surface of the loaded oxides of manganese.
  • These reaction products form by reaction between target pollutants and virgin oxides of manganese.
  • This embodiment of a method of the invention comprises the steps of: rinsing the loaded oxides of manganese in a pre-oxidation aqueous rinse solution to the dissolve reaction products into solution, thereby removing reaction products from the surface of the oxides of manganese; separating or filtering the rinsed oxides of manganese from the solution to form a pre- oxidation filtrate; feeding the rinsed oxides of manganese into regeneration vessel containing a heated aqueous oxidizing solution under agitation and mixing the solution to form a slurry, the solution being prepared so as to have Eh and pH values within the MnO2 stability area for an aqueous solution heated to a temperature at or near boiling temperature at atmospheric pressure; monitoring and adjusting solution temperature, Eh value and pH value in the regeneration vessel so as to rapidly move solution conditions into and to maintain them within the MnO2 stability area; maintaining the solution conditions within the MnO2 stability area until the oxides of manganese are regenerated so as to have pollutant loading capacity and/or average
  • inventions include the oxides of manganese produced by a above methods.
  • the above methods may further comprise the step of maintaining solution or solution mixture pH constant throughout the processing cycle. They may also further comprise the steps of : separating the oxides of manganese from the aqueous oxidizing solution to provide separated oxides of manganese and a oxidation filtrate, the oxidation filtrate being routed for further processing and handling; rinsing and filtering the separated oxides of manganese to provide rinsed oxides of manganese and a rinse filtrate, the rinse filtrate directed further handling and processing; and optionally, drying and/or comminuting the rinsed oxides of manganese.
  • the aqueous oxidizing solution may contain an oxidant or oxidizer selected from the group consisting of persulfates, chlorates, perchlorates, permanganates, peroxides, hypochlorites, oxygen, air, and ozone (O3).
  • an oxidant or oxidizer selected from the group consisting of persulfates, chlorates, perchlorates, permanganates, peroxides, hypochlorites, oxygen, air, and ozone (O3).
  • the system of this embodiment of the invention comprises: an oxidation vessel equipped with probes for measuring temperature, Eh and pH values of aqueous solutions within the oxidation vessel, the oxidation vessel being configured for introduction of a solutions containing manganese salt ions, oxides of manganese in particle form, or a slurry containing oxides of manganese; a oxidant feeder containing a supply of aqueous oxidizing solution, the aqueous oxidizing solution being prepared so as to have Eh and pH values within the MnO2 stability area for an aqueous solution heated to a temperature at or near boiling temperature at atmospheric pressure; a heater for providing heat to the oxidation vessel; a base and/or acid feeder for feeding 'base or acid to the oxidation vessel; a least one filtration and/or rinse unit, which optionally may be incorporated into and a part of the oxidation vessel; and a controller for simultaneously monitoring and adjusting system operational parameters and regulating system components, the controller being in electronic communication with the probes of
  • the system of this embodiment may further comprise an electrolytic cell for production of oxidant and other useful by-products, the electrolytic cell being configured to receive and process filtrate and rinse solutions from the oxidation vessel and/or at least one filtration/rinse unit, the solutions being generated during processing with in the system, wherein the controller is in electronic communication with and regulates and controls operation of the electrolytic cell.
  • MnO2 stability area refers to the region of thermodynamic stability for manganese dioxide delineated by Eh and pH values for aqueous solutions or, phrased alternatively, the domain of MnO2 stability for an aqueous solution. More specifically, it refers to the region or domain delineated by Eh and pH values for aqueous solutions in an electrochemical stability diagram, such as presented by Pourbaix diagrams and their equivalents, such as the Latimer Diagram or the Frost Diagram.
  • Regenerated oxides of manganese refers to loaded or reacted oxides of manganese that have been processed according to the methods of the invention in which a heated aqueous oxidizing solution is mixed with a heated slurry of loaded oxides of manganese to form a mixture or a heated aqueous oxidizing solution to which loaded oxides of manganese are added to from a slurry mixture, the mixtures being adjusted and maintained so as to be within the MnO2 stability area.
  • Preheated oxides of manganese refers to virgin or unreacted oxides of manganese that have been processed according to the methods of the invention in which a heated aqueous oxidizing solution is mixed with a heated a slurry of virgin oxides of manganese to form a mixture or a heated aqueous oxidizing solution to which virgin oxides of manganese are added to from a slurry mixture, the mixtures being adjusted and maintained so as to be within the MnO2 stability area.
  • Precipitated oxides of manganese refers to oxides of manganese formed or newly formed by precipitation from a mixture of a heated manganese salt solution and a heated aqueous oxidizing solution or a mixture formed by addition of manganese salts to a heated aqueous oxidizing solution, the mixtures being adjusted and maintained so as to be within the MnO2 stability area.
  • the methods and systems of the invention each involve and employ Applicants' recognition that oxides of manganese processed in aqueous systems in which conditions and parameters are adjusted and maintained within the MnO2 stability area will yield oxides of manganese having high pollutant loading capacities and/or high oxidation states, hi its various embodiments, the invention and the methods and systems thereof provide for rapid, adaptive and stable processing of oxides of manganese as compared to the methods and systems currently know in the art. Oxides of manganese thus processed are suitable for use as a sorbent in dry and wet gaseous pollutant removal systems and are particularly suitable for use in dry pollutant removal systems.
  • MnO2 stability area for an aqueous system varies based upon the conditions of the system and may shift or drift as reactions in the aqueous system proceed. For example, changes in dissolved manganese ion concentration, oxidizer concentration, pH, Eh, solution temperature, and competing dissolved ions may affect the boundaries of the domain or region of stability for MnO2.
  • the aqueous oxidizing solution systems of the invention are typically at temperatures at or near the boiling temperature of aqueous solutions at given atmospheric pressures.
  • the boiling point of aqueous solutions will vary depending upon elevation and will be diffent at sea level than at other elevations.
  • the effects of such changes or different atmospheric conditions upon the boundaries of the MnO2 stability area on a Pourbaix Eh-pH diagram can be determined either by empirical data derived from experimentation or with computer software programs known to those skilled in the art, such as HSC Chemistry distributed by Outokumpu Oy of Finland. Software may also be written to determine the MnO2 stability area as defined by other diagrams, such as the Latimer Diagram or the Frost Diagram.
  • the MnO2 stability area is defined by the thermodynamically stable ranges or boundaries of pH-Eh combinations that promote the existence and formation of MnO2 (Mn having average valence state close to +4) as the most thermodynamically stable fo ⁇ n of manganese in an aqueous solution system.
  • the constituents of the aqueous solution systems are the loaded or virgin oxides of manganese or the disassociated manganese salts along with the oxidizer or oxidizers in the aqueous oxidizing solution and the base or acids that may be added thereto.
  • aqueous solution system conditions must be moved to and maintained at or within the boundary area delineated by the combination of Eh and pH ranges. In order to accomplish this, Eh and/or pH adjustments must be made through the addition of oxidizer, base or acid.
  • Applicants utilize a heated aqueous oxidizing solution to provide the oxidizer.
  • the oxidizer must be able to provide the required electrochemical (oxidizing) potential (Eh) at the specified temperature and within the specified ph ranges to provide an Eh-pH combination to achieve stable aqueous solution system equilibrium within the MnO2 stability area.
  • Eh electrochemical (oxidizing) potential
  • Suitable oxidizers to name a few include, but are not limited to, persulfates, such as potassium peroxidisulfate (K2S2O8), sodium peroxidisulfate (Na2S2O8), and ammonia peroxidisulfate ((NH4)2S2O8), chlorates, such as sodium chlorate (NaClO3), perchlorates such as sodium perchlorate (NaClO4), permanganates, such as potassium permanganate (KMnO4), oxygen (O2) or air, ozone (O3), peroxides, such as H2O2, and hypochlorites, such as sodium hypochlorite (NaOCl).
  • persulfates such as potassium peroxidisulfate (K2S2O8), sodium peroxidisulfate (Na2S2O8), and ammonia peroxidisulfate ((NH4)2S2O8)
  • chlorates such as sodium chlorate (NaClO3)
  • oxidizers suitable for use in the methods of the invention will be apparent to those skilled in the art; it being understood that the electrochemical potential (Eh) of the heated aqueous oxidizing solution, and therefore the effectiveness of the methods of the invention, depends, in part, upon the strength of the oxidizer and/or the concentration of the oxidizer in the solution.
  • the pH range of the boundary may be acidic, near neutral, or basic.
  • processing may be carried out over the full pH spectrum.
  • the oxidizer strength or concentrations required at the extremes of the pH spectrum may make such processing uneconomic though nonetheless achievable.
  • the system may tend to shift away from the desired pH range, in which case the addition of a suitable base or acid will help accomplish the necessary adjustment to maintain the system within the appropriate Eh-pH range of the MnO2 stability area.
  • the introduction of additional oxidizer to bring the system within the appropriate Eh range as pH drifts or shifts in the aqueous system may also beneficially accomplish the necessary adjustment.
  • the aqueous solution system is, and therefore the methods and systems of the invention are, dynamic and adaptive with necessary adjustments being made not only by introduction of acid or base but with introduction of oxidizer as well.
  • useful bases include but are not limited to alkali or ammonium hydroxides, potassium hydroxides, and sodium hydroxides.
  • useful bases include but are not limited to sulfuric, nitric, hydrochloric and perchloric acid to name a few. Applicants have found it useful to match the cations of the oxidant and base. For example, where the oxidant is a persulfate, such as potassium peroxodisulfate (K2S2O8), the pH could be adjusted with a compatible or suitable base, such as potassium hydroxide (KOH).
  • KOH potassium hydroxide
  • Na2S2O8 sodium peroxodisulfate
  • a compatible base would be sodium hydroxide (NaOH); and with ammonium peroxodisulfate ((NH4)2S2O8), ammonium hydroxide ((NH4OH) would be a compatible base.
  • the acids or bases and other process additives are generally commercially available and those skilled in the art would be able to readily identify compatible process additives useful within the scope of the invention.
  • heated oxidizing solutions having the desired pH-Eh- temperature combination can be prepared and maintained or adjusted by increasing or decreasing oxidizer, acid or base concentrations and/or temperature adjustment, as appropriate, so that the conditions are adjusted to remain within the MnO2 stability area.
  • an operator can make necessary adjustments in order to maintain or return the oxidizing solution to conditions within the MnO2 stability area.
  • Such monitoring and adjusting can also be automated utilizing electronic probes or sensors and controllers as discussed later herein below.
  • the systems in which the methods of the invention are carried out all have common or corresponding components that are substantially the same. Though referred to, in appropriate instances by slightly different terms (for purposes of clarity) and being identified with corresponding but different reference numbers in the figures and the disclosure herein below, their operation and function will also be understood to be substantially the same and equivalent. To the extent that there are operational or functional differences, they are identified and discussed as appropriate.
  • the common system components include oxidation vessels in which regeneration, pretreatment and precipitation are carried out; agitation devices and probes for temperature, Eh and ph measurement with which the oxidation vessels are equipped, filtration units, and rinses.
  • the oxidation vessels are also equipped with a heater (not shown in the figure hereof) for adding heat to and maintaining the temperature of the solutions in the vessels.
  • a heater for adding heat to and maintaining the temperature of the solutions in the vessels.
  • a dryer would be another common component.
  • a comminuting device would be another common component.
  • reaction products such as manganese salts
  • Such reaction products include for example, manganese salts such as MnSO4, Mn(NO3)2, MnC12 and other manganese salts and the like. It is further believed that formation of such salts or other reaction products occurs primarily, but not exclusively, on the surfaces of the oxides of manganese sorbent particles. These salts or reaction products form a layer or coating, which effectively isolates the unreacted sorbent under a coating of reaction products, thereby preventing continued rapid reaction with additional target pollutant gas molecules at such sites.
  • reaction products on the sorbent particle surfaces results in a loaded or partially loaded condition which over the course of target pollutant removal processing eventually diminishes the ability of the oxides of manganese to capture additional target pollutant gas molecules or to capture target pollutants at a desired level of removal efficiency.
  • the reacted or loaded oxides of manganese sorbent can be regenerated and made available for subsequent pollutant removal cycles or for use in other industrial or commercial applications. Additionally, as discussed later herein below, valuable byproducts may also be recovered from process stream of the invention.
  • reacted sorbent is processed in a heated oxidizing aqueous solution under controlled conditions, specifically within the MnO2 stability area, to produce regenerated oxides of manganese.
  • the regeneration methods of the invention can be understood with reference to Figures 3-5 which depicts different possible embodiments of a regeneration system of the invention in block flow.
  • loaded oxides of manganese or loaded sorbent is rinsed or washed with an aqueous solution in the pre-oxidation sorbent rinse 12 of regeneration system 10 (without the precipitation subsystem shown in Figure 5).
  • the rinse step serves to wash away reaction products from the surface of reacted oxides of manganese sorbent particles along with impurities and very fine particulate matter. Regeneration, however, may be conducted without the rinse step as discussed with reference to Figure 4 herein below.
  • the rinsed sorbent is separated from the rinse solution to provide rinsed sorbent or rinsed regenerated oxides of manganese and a pre-oxidation filtrate.
  • This filtration may be carried out using any of a variety of suitable filtration techniques and devices known _ .
  • a separate filtration device may be used following pre-oxidation rinse 12 or the filtration device may be incorporated in and part of pre-oxidation rinse 12.
  • the filtrate will contain recoverable values, such as cations and anions from disassociated reaction products.
  • the reaction products are manganese salts, such as manganese sulfate (MnSO4) and manganese nitrate (Mn(NO3)2), : Mn+2, SO4-2, NO3-1, spectator ions, suspended solids or other particulates.
  • these values can be recovered from the pre-oxidation filtrate through oxidation and precipitation of the Mn+2 ion as a solid precipitated oxides of manganese; and with further processing the sulfate or nitrate anions can be recovered and formed into useful and marketable by-products, e.g., fertilizers, chemicals or explosive products or routed for disposal as required.
  • useful and marketable by-products e.g., fertilizers, chemicals or explosive products or routed for disposal as required.
  • the rinsed sorbent is introduced or conveyed to regeneration vessel 14 which is equipped with an agitator 15, also referred to herein as an agitation means 15.
  • an agitator 15 also referred to herein as an agitation means 15.
  • Any of various agitation devices known to those skilled in the art to be suitable for agitating, mixing and stirring the solid-liquid slurries so as to keep the solid oxides of manganese particles generally suspended in the solution can be utilized.
  • vessel 14 is optionally equipped with temperature, probe 13 A, pH probe 13B and Eh probe 13C. These probes are utilized to measure their respective parameters in the heated aqueous oxidizing solution and may be in electronic communication with a controller as later discussed herein with reference to Figure 8.
  • the rinsed sorbent is mixed with a heated oxidizing aqueous solution therein to form a slurry.
  • the heated aqueous oxidizing solution is preferably preheated to temperatures at or near the boiling point of aqueous solutions at atmospheric pressure. For example, at sea level, this would be about 100 °C.
  • Regeneration may be carried out at temperatures ranging from about 90 °C to about 110 °C, with temperatures between 95 °C to about 108°C being preferred, and temperatures between about 100°C to about 105°C being more preferred at sea level atmospheric pressures.
  • the solution temperature should be maintained unless a temperature adjustment away for near boiling is required in order to maintain the aqueous solution system with the MnO2 stability area as other system parameters shift during processing.
  • the heated aqueous oxidizing solution provides the required electrochemical (oxidizing) potential (Eh), within the specified temperature and pH range to yield regenerated oxides of manganese having high loading capacities and/or high oxidations states.
  • Eh electrochemical (oxidizing) potential
  • the slurry in the regeneration vessel 14 is continuously mixed and the pH of the slurry is adjusted by appropriate means, e.g., addition of acid or base.
  • the rinsed oxides of manganese are allowed to remain within the slurry for a time sufficient to achieve an increased oxidation state and/or a target pollution loading capacity equal or greater than that of virgin oxides of manganese sorbent originally utilized to capture target pollutants.
  • a sufficient time may be between about 20 minutes to about 70 minutes, preferably between about 35 minutes to about 55 minutes, and more preferably between about 40 minutes to about 50 minutes. Such processing times are rapid compared to the hours and tens of hours of sometimes staged processing of prior art methods.
  • an optimal time for the solid rinsed oxides of manganese to remain in the regeneration vessel (14) is approximately 45 minutes, during which time the portions of the solid rinsed oxides of manganese particles that have had their reactivity or target pollutant loading capacity reduced, through lowering of valance state, are oxidized up to valance states close to +4.
  • a deviation of two to three minutes above or below 45 minutes is near enough to optimal to provide regenerated oxides of manganese having oxidation states and/or loading capacities particularly suitable for use as a sorbent for target pollutant removal. It being understood that with greater deviations from the optimal time but yet within the above stated time ranges oxides of manganese suitable pollutant removal (particularly when high loading capacity is not required) and for other uses may nonetheless be produced with the invention
  • Separation of the regenerated oxides of manganese and the oxidation filtrate is best preformed at close to operating temperature in regeneration vessel 14, or close to about 100 °C. Allowing the solution containing regenerated oxides of manganese and the aqueous oxidizing solution to cool to temperatures below the solubility temperatures for residual ions in solution, for example, but not limited to K+l and SO4-2 can result in the precipitation of solid salts such as K2SO4. Through experimentation, it has been recorded that allowing salts to precipitate with the regenerated oxides of manganese sorbent lowers the target removal efficiency and loading rates and should therefore be avoided.
  • the regenerated sorbent or regenerated oxides of manganese are then further rinsed with water to wash away any remaining spectator ions, hi Figure 3 this is illustrated as two separate steps: 1) filtering and separating the regenerated oxides of manganese from the aqueous oxidizing solution to provide an oxidation filtrate in filtration unit 16; and 2) rinsing the sorbent with water to wash away remaining spectator ions in the regenerated sorbent rinse 17.
  • Any of a variety of suitable filtration techniques and devices known to those skilled in the art may be utilized for this purpose. It should be noted that the filtration and rinsing step could be combined using filtration and rinsing equipment known to those skilled in the art.
  • the filtration unit 16 may alternatively be inco ⁇ orated into and as part of the regeneration vessel 14. Further still, the rinse, separation, regeneration and subsequent rinse and separation steps may all be carried out in an appropriately configured and equipped single vessel in which the sorbent is first rinsed and filtered, heated aqueous oxidizing solution is subsequently introduced and adjusted as necessary, followed by another rinse and filtration cycle.
  • the rinsing of the regenerated oxides of manganese should be of sufficient duration and with sufficient volume of water as to remove dissolved ions associated with the oxidizer, base, and acid in the aqueous oxidizing solution to a suitable level.
  • the presence of these ions in the regenerated sorbent in sufficient amounts may negatively impact the loading capacity or removal efficiency of the regenerated oxides of manganese. This is not to say that regenerated oxides of manganese that are not so rinsed will be ineffective for removal of target pollutants because in fact they may be so utilized without the rinse and good removal rates can be achieved.
  • the regenerated oxides of manganese may be more efficiently utilized following rinsing. This is equally applicable to oxides of manganese preheated or precipitated according to the methods of the invention.
  • TDS measurements of the oxidation filtrate taken by Applicants have been in the range of 80,000-200,000, representing the disassociated ions from the oxidant, base or acid and other possible dissolved solids or fine particulates associated with the regeneration.
  • the rinse step should generally being designed to remove such ions, solids and particulates from the regenerated oxides of manganese to an acceptable level or tolerance. Where precision is required the vessel or apparatus in which the rinse is carried out should be equipped with an appropriate measurement device for conductivity, resistivity, TDS level or other indicator.
  • the rinse step can be carried out until the oxidation filtrate reaches the desired level based upon the measurement technique employed.
  • the acceptable level or tolerance for the given use to which the regenerated oxide will be put can be determined, as well as the volume, flow rate and duration of the rinse in order to establish or standardize operating procedures.
  • lowering the TDS of the filtrate generally favorably impacts target pollutant removal efficiency and loading rates, Applicants have found that oxides of manganese prepared according to the methods of the invention may be utilized for target pollutant removal with or without the rinsing step.
  • the wet regenerated oxides of manganese if being utilized in a dry target pollutant removal system such as the PahlmanTM system, i2 first routed for drying to a dryer 18, referred to as sorbent dryer 18 in the figure.
  • Oxides of manganese may be introduced into pollution removal systems as a dry power, a wet filter cake, or a slurry by a slurry or spray feeder.
  • the wet filter cake and sprayed slurry may be "flash dried" upon contact with industrial gas streams which may be introduced at elevated temperatures into the pollutant removal systems.
  • the drying step may not be necessary and the wet or moist filter cake may be conveyed to a filter cake feeder.
  • the regenerated oxides of manganese need not be filtered or separated. Rather, they can be conveyed as a slurry to the feeder.
  • both drying and comminuting to size the oxides of manganese particles is typically performed.
  • the dryer 18 may be a kiln or other suitable dryer used for such pu ⁇ oses and known to those skilled in the art.
  • the dryer 18 may utilize waste heat generated by combustion which is transferred or exchanged from combustion or process gases at an industrial or utility plant.
  • the temperature should be below the thermal decomposition temperature of oxides of manganese but sufficiently high so as to drive off surface water or moisture without removing any waters of hydration or water of crystallization. Temperatures around 100 °C to 160 °C have been found to be adequate for this pu ⁇ ose.
  • Drying can be conducted at lower temperatures but drying time may be uneconomically extended; and at higher temperatures, which can be utilized in Applicants' invention, short drying time will have to be closely observed so as to avoid thermal decomposition of the oxides of manganese, driving off structural water, or undesired damage > to the crystalline structure of the oxides of manganese.
  • loaded sorbent is processed without a pre-oxidation rinse.
  • This is illustrated in Figure 4, where the loaded sorbent is introduced directly into vessel 24, also referred to as regeneration/precipitation vessel 24, of regeneration system 20 without a pre-oxidation rinse.
  • the system 20, as depicted includes an agitator 25, probes 23A-23C, filtration unit 26, rinse 27, dryer 28, and comminuting device 29.
  • the components of system 20, absent the pre-oxidation rinse 12 are essentially the same components as that of system 10 and that the function and operation of the corresponding system components will be the same in both embodiments of the systems and of the methods of the invention as depicted in Figures 3 and 4.
  • the statements made above regarding the corresponding counte ⁇ art components and process steps in regeneration system 10 of Figure 3 and operating conditions and parameters (temperature, Eh, and pH) are equally applicable to the components of system 20 of Figure 4 and therefore they are not repeated here.
  • the method proceeds in substantially the same manner as described above with reference to Figure 3 following the pre-oxidation rinse 12 where rinsed loaded oxides of manganese are introduced into the regeneration vessel 14.
  • the dissociated ions of the reaction products are retained and processed in the same oxidation vessel, vessel 24, as the solid oxides of manganese particles upon which the reaction products formed.
  • the slurry in vessel 24 will also contain disassociated reaction product ions in the heated aqueous oxidizing solution.
  • reaction products are manganese salts, e.g., manganese sulfate (MnSO4) and manganese nitrate (Mn(NO3)2), : Mn+2, SO4-2, NO3-1, spectator ions, suspended solids or other particulates will be in the slurry solution. While the solid oxides of manganese are being regenerated, the Mn+2 ions are at the same time being precipitated out of solution as newly formed oxides of manganese.
  • MnSO4 manganese sulfate
  • Mn(NO3)2 manganese nitrate
  • spectator ions suspended solids or other particulates
  • the solution temperature is at or near boiling at atmospheric pressure at a given elevation.
  • adjustment of heated aqueous oxidizing solution parameter, temperature, Eh and pH would also made as necessary to move solution conditions into and maintain those conditions within the MnO2 stability area after loaded oxides of manganese are introduced into vessel 24 without a pre-oxidation rinse.
  • the end product is a combination of regenerated and precipitated oxides of manganese having high oxidation states and/or high ⁇ or increased pollutant loading capacities.
  • the pre-oxidation filtrate contains the disassociated reaction products, including Mn+2 ions which can be precipitated out of solution as oxides of manganese without solid oxides of manganese particles being present in the solution.
  • the precipitation subsystem 30, as depicted includes, the precipitation vessel 34 equipped with agitator 35, and probes 33A-33C; filtration unit 36; rinse 37; dryer 38 and comminuting device 39.
  • the components of the precipitation subsystem 30 and steps of the method of the invention carried out therein are substantially the same though numbered differently and in a some instances termed differently. Nonetheless, the corresponding system components of the earlier discussed embodiments of the systems 10 and 20 of the invention and the steps of the methods as described herein above are substantially the same.
  • the statements made above regarding the corresponding counte ⁇ art components of regeneration systems 10 and 20 and operating conditions and parameters (temperature, Eh, and pH) are equally applicable to the components of the precipitation subsystem 30 of Figure 5 and the steps carried out therein. Therefore, they are not repeated here in order to avoid undue repetition.
  • the method proceeds in a similar manner as described above with reference to Figures 3 following the pre-oxidation rinse 12 or with reference to Figure 4. The obvious difference being that no solid oxides of manganese are initially present in solution in precipitation vessel 34.
  • the pre-oxidation filtrate is heated to or maintained at the operational temperatures, near boiling, prior to introduction into precipitation vessel 34 and is mixed into a heated aqueous oxidizing solution in the vessel 34.
  • the pre-oxidation filtrate may be introduced into the vessel 34 and heated followed by introduction of suitable oxidizers and bases or acids to move the conditions of the resulting solution into and to maintain them within the MnO2 stability area.
  • the heating of the two constituent solutions prior to mixture serves to avoid or minimize the precipitation of lower oxides of manganese and also serves to provide for the fairly rapid processing times previously mentioned above. Utilizing the probes 33A-33C, solution temperature, pH and Eh are respectively monitored.
  • Another embodiment of the invention relates to the pretreatment of virgin oxides of manganese, whether of the NMD, EMD or CMD type, to increase their loading capacity and/or their valence state.
  • oxides of manganese that otherwise might not be economical for use as a sorbent in, for example, a PahlmanTM or other pollutant removal system or for other commercial applications due to poor loading capacity or low valence states may be made viable for such uses.
  • pretreatment system 40 includes preheatment vessel 44, equipped with an agitator 45, probes 43 A-43C, filtration unit 46, rinse 47, dryer 48, and comminuting device 49.
  • FIG. 7 depicts a precipitation system according to the invention.
  • the operation of this system is substantially the same as the precipitation subsystem 30 depicted in Figure 5
  • the precipitation system 50 includes pretreatment vessel 54, equipped with an agitator 55, probes 53A-53C, filtration unit 56, rinse 57, dryer 58, and comminuting device 59.
  • pretreatment vessel 54 equipped with an agitator 55, probes 53A-53C, filtration unit 56, rinse 57, dryer 58, and comminuting device 59.
  • the components of the precipitation system 50 and steps of the method of the invention carried out therein are substantially the same though numbered differently and in some instances termed differently.
  • heated aqueous oxidizing solution, acid or base solution, and heated manganese salt solution are introduced into precipitation vessel 54.
  • the heated oxidizing solution is so prepared as to have conditions that move the mixture between it, the acid or base solution, and the manganese salt solution toward the MnO2 stability area.
  • the heating of the constituent solutions prior to mixture serves to avoid or minimize the precipitation of lower oxides of manganese and also serves to provide for the fairly rapid processing times previously mentioned above.
  • temperature, pH and Eh are respectively monitored and thereafter adjusted and maintained within the MnO2 stability area by introduction of additional oxidizing solution and base or acid and with temperature adjustment, all as necessary.
  • the resultant precipitated oxides of manganese whether dried and comminuted or utilized as a filter cake or slurry will have high or increased loading capacities and/or valence state that are equal to or greater than that of commercially available
  • NMD NMD
  • EMD EMD
  • CMD CMD
  • Precipitated oxides of manganese may be filtered, decanted or otherwise collected and dried. If further oxidation of the precipitated oxides of manganese is required, the drying step may be carried out in an oxidizing atmosphere.
  • an oxidizer as previously described may be introduced into vessel 30 or 50 while the oxides of manganese are being formed and precipitated. For example air or oxygen can be bubbled through or a persulfate or other suitable oxidizer may be used.
  • oxides of manganese particles can be sized for industrial and chemical application uses and particularly a particle size ranging from 0.5 to about 500 microns and be sent to the sorbent feeder for reuse in removal of target pollutants.
  • the oxidation filtrates from filtration devices 36 and 56 and the rinse filtrates from the rinses 37 and 57 will contain disassociated cations and anions such as potassium, sodium, or ammonium sulfates and/or nitrates which can be made into fertilizer products or other products such as fertilizers, explosives or marketed as is.
  • Use of acoustic energy during processing particularly during precipitation may favorably affect the performance of the oxides of manganese produced in the various embodiment of the invention.
  • Acoustic energy as applied industrially, includes the range from ultrasonic, which is short-wave, high-frequency (greater than 20,000 Hz.) energy, to infrasonic, which is long-wave, low-frequency (less than 20 Hz.) energy. All forms of acoustic energy are transmitted as pressure waves, and are usually generated by specialized devices or transducers which convert electricity or pressurized air into acoustic energy within the desired frequency range.
  • Ultrasonic acoustic energy include agitation of liquid solutions for applications such as solvent parts cleaning for example.
  • Infrasonic acoustic energy for example, is used to loosen material in dry powder transport systems, to promote smooth flow and prevent stoppage of the material, or to remove filter cake from bag-type filters; it is not typically used in liquid applications.
  • These and other applications of such technology may also be methods of transferring energy to a solution, gas, or solid material, without raising its temperature.
  • ultrasonic equipment such as small or laboratory scale ultrasonic equipment like those available from the Cole-Parmer Instrument Company and large scale equipment, such as high pressure and /or high temperature device available from Misonix.
  • acoustic energy in the form of ultrasonic or infrasonic waves has improvements in sorbent activity or loading capacity can be achieved.
  • the application of acoustic energy during processing of oxides of manganese may be doing all or some of the following actions: (1) enhancing agitation during sorbent processing to improve reaction rates and enhance mixing; (2) promoting rapid dissolution of reaction products from loaded sorbent surfaces during regeneration; (3) increasing dissolution rates of chemicals used in the processing of oxides of manganese; (4) altering structural development of crystal structure during and following precipitation from solution; and (5) breaking up large oxides of manganese crystal formations, h the methods and systems of the invention, acoustic energy would be generated by specialized devices or transducers and directed which may optionally be inco ⁇ orated into the oxidation vessels 14, 24, 34, 44 and 55. Such sonication devices may be used and inco ⁇ orated into other system components, such as oxidant, acid or base vessels or vessel in which manganese salts are mixed with water prior to
  • FIGS 8-10 illustrate embodiments of the invention inco ⁇ orating an electronic controller 67 to provide adaptive integrated simultaneous monitoring and adjustment of operational parameters, e.g., temperature, Eh, and pH, within the oxidations vessels with an optional feed back loop for checking the loading capacity of the oxides of manganese produced according the methods of the invention
  • operational parameters e.g., temperature, Eh, and pH
  • embodiments of the regeneration and/or precipitation systems are depicted as being integrated with a pollutant removal system 60 that utilizes oxides of manganese as a sorbent for target pollutant removal.
  • the system 60 is presented a representation of pollutant removal systems in general and it should be understood that the system 60 could be a wet scrubbing removal system, a dry removal system or a combination thereof.
  • System 60 as represented includes a reaction chamber 62 and a sorbent feeder 64 which contains and/or is configured to feed oxides of manganese to the reaction chamber 62.
  • oxides of manganese may be fed as a dry powder or dry particles, as a slurry, or as a wet filter cake.
  • a stream of untreated gas containing target pollutants is shown entering into the reaction chamber 62.
  • gas and sorbent oxides of manganese are introduced into the reaction chamber 62 and contacted under conditions and for a time sufficient to effect removal of the target pollutant(s) at a targeted removal efficiency rate for the target pollutant(s).
  • the gas and the oxides of manganese may be introduced together or separately into reaction chamber 62, depending upon the type pollutant removal system and type of reaction chamber employed. Clean gas, gas from which a target pollutant has been removed, is shown to be vented from the reaction chamber 62.
  • the PahlmanTM system may be viewed as being comprised of a feeder containing a supply of sorbent or oxides of manganese, at least one bag house configured to receive sorbent and a gas containing target pollutants, such as those identified herein above. Gas is introduced at temperatures ranging from ambient temperature to below the thermal decomposition or liquification temperature of manganese salt reaction products formed between the oxides of manganese and the target pollutant.
  • Gases are introduced into the bag house and contacted with the sorbent for a time sufficient to effect capture of the target pollutant at a targeted pollutant capture rate.
  • the target pollutant or pollutants are captured through formation of the reaction product between the target pollutant and the sorbent.
  • the system will also include a controller for simultaneously monitoring and adjusting system operational parameters.
  • the controller provides integrated control of system differential pressure and other operational parameters selected from the including, but not limited to, target pollutant capture rates, gas inlet temperatures, sorbent feeder rates and any combinations thereof. Differential pressure within the system is regulated by the controller so that any differential pressure across the system is no greater than a predetermined level and the target pollutant is removed at the targeted pollutant capture rate set point.
  • the system may inco ⁇ orate more than one reaction zone, both of which may be bag houses.
  • the system may optionally inco ⁇ orate a reaction zone upstream of a bag house into which gas and sorbent are introduced and subsequently directed to the bag house.
  • Such optional reaction zones may be selected from the group of reaction zones that includes a fluidized bed, a pseudo-fluidized bed, a reaction column, a fixed bed, a moving bed, a se ⁇ entine reactor, a section of pipe or duct and a cyclone or multi-clone.
  • the first target pollutant may be captured or removed in the first reaction zone or substantially removed in the first reaction zone and the second target pollutant will be removed in the second reaction zone.
  • This can be advantageously utilized particularly where the two reaction zones are bag houses to capture a first target pollutant such as SO ⁇ in the first reaction zone and a second target pollutant such as NO x in the second reaction zone. This would allow for separate regeneration of loaded sorbent having reaction products thereon from reaction between oxides of manganese and a single target pollutant or at least different target pollutants that are captured in the second bag house.
  • a regeneration system 10 and precipitation system 30 substantially as depicted in Figure 5 is illustrated in block flow and is connected to removal system 60.
  • Precipitation vessel 30 is equipped with temperature probe 33A, pH probe 33B, and Eh probe 33C; regeneration vessel 14 is equipped with temperature probe 13A, pH probe 13B, and Eh probe 13C all of which are in electronic communication with a controller 67.
  • An acid and/or base vessel (not shown) is configured to feed acid and or base to precipitation vessel 30 and regeneration vessel 14.
  • An oxidant vessel containing oxidizing solution (not shown) is configured to feed oxidizing solution to precipitation vessel 30 and regeneration vessel 14.
  • oxidizing solution may be routed directly from an electrolytic cell or the output of the electrolytic cell may be routed to the oxidant vessel.
  • Loaded sorbent may conveyed directly from reaction chamber 62 to regeneration pre-oxidation rinse 12 or it may be directed to a loaded sorbent vessel (not shown) for holding and subsequently conveyed to rinse device 12.
  • the pre-oxidation filtrate from rinse 12 is routed to precipitation vessel 30.
  • the rinsed sorbent from pre-oxidation rinse, device 12 is routed to the regeneration vessel 14.
  • controller 67 (not shown) are in electronic communication with the controller 67.
  • the controller 67 is also in electronic communication with the Eh probe 33C, pH probe 33B, and temperature probe
  • sorbent from the precipitation vessel 30 and the sorbent from regeneration vessel 14 may each have its own filtration device and processed sorbent rinse device.
  • Sorbent is then routed to the sorbent dryer 18 As illustrated, sorbent from sorbent dryer 18 is routed to comminuting device 19 and then to sorbent feeder 64 which in turn feeds the sorbent to reaction chamber 62. Alternatively, sorbent from dryer 18 may be routed directly to reaction chamber 62 or to a sorbent storage vessel prior to being directed to the feeder 64.
  • Reaction chamber 62 is equipped with optional target pollutant concentration readers or continuous emission monitors (CEMS) for NOX and SO2, readers 68 A and 68B, which are in electronic communication with controller 67. It should be understood the reaction chamber 62 may be equipped with other equivalent readers where different target pollutants are being captured.
  • CEMS target pollutant concentration readers or continuous emission monitors
  • the controller 67 interfaces with precipitation vessel 30 probes 33A, 33B, and 33C; NOx and SO2 readers 68A and 68B and oxidant, base and or acid feeders and vessels (not shown) for measurement and adjustment of operational parameters with in the vessels 14 and 34.
  • the controller 67 signals the addition of oxidant, acid, and or base to precipitation vessel 30 based upon the inputs received from the probes until the desired Eh/pH reading is obtained prior to addition of the pre-oxidation filtrate into the precipitation vessel 30.
  • Agitator 35 continuously agitates the solution.
  • the temperature, pH, and Eh of the precipitation vessel 30 are monitored and adjusted continuously so as to maintain conditions within the MnO2 stability area.
  • the controller 67 similarly interfaces with regeneration vessel 14 probes 13A, 13B, and 173; NOX and SO2 readers 68 A and 68B and oxidant, base and or acid feeders and vessels (not shown) for measurement and adjustment of operational parameters within the vessel 14.
  • NOX and SO2 readers 68 A and 68B and oxidant, base and or acid feeders and vessels (not shown) for measurement and adjustment of operational parameters within the vessel 14.
  • temperature, pH, and Eh of the aqueous oxidizing solution in regeneration vessel 14 are monitored and adjusted continuously so as to maintain conditions within the
  • Precipitation vessel 30 and regeneration vessel 14 may be run in parallel operation or alternating operation so as to be able to verify sorbent loading capability using the optional feedback loop of the conhoUer 67and probes 68A and 68B.
  • the conhoUer 67 contains a programmable logic controller (PLC) and other hardware components necessary for the operation of the conhoUer such as a power supply, input and output modules that would communicate with the probes 33A, 33B, and 33C; probe
  • the controller 67 receives inputs from the various probes and readers and converts them into ladder logic language that would be used by an internal proportional integral derivative (PID) loop to individually and simultaneously monitor system operational parameters and to reconcile the inputs with predetermined or computer generated calculated set points for the operational parameters, such as temperature, and Eh and pH levels.
  • PID proportional integral derivative
  • the conhoUer 67 will send an output as necessary to any of the feeders of oxidant and base and/or acid vessels (not shown) signaling a feeder to cycle on or to change feeder rate so as to maintain or adjust system operational parameters to within the MnO2 stability area for either precipitation vessel 30 or regeneration vessel 14.
  • the controller 67 may also contain an Ethernet card or other component that allows onsite or offsite remote display and operator interface and control as needed.
  • the conhoUer 67 would be given a start command and direct the loaded sorbent feeder (not shown) to inject predetermined amounts of loaded sorbent into the pre-oxidation rinse device 12.
  • the controller 67 signal injection of a predetermined amount of oxidizing solution, acid and/or base into the precipitation vessel 30 and regeneration vessel 14 checking and or adjusting the Eh and/or pH of the solution prior to feeding in the predetermined amount of pre-oxidation filtrate from the pre-oxidation rinse device 12 into the precipitation vessel 30 and a predetermined amount of rinsed sorbent from the pre-oxidation rinse device 12 into the regeneration vessel 14.
  • the Eh of the oxidizing solution in precipitation vessel 30 and regeneration vessel 14 may be adjusted by addition of an oxidizer in sufficient quantity as to raise the Eh to the desired level from an oxidizer vessel (not shown), containing a supply of oxidizer or aqueous oxidizing solution.
  • the controller 67 would also check, based on inputs received from the precipitation vessel 30 probes 33A, 33B, and 33C; and regeneration vessel 14 probes 13A,13B, and 13C and/or adjust the conditions of the precipitation vessel 30 and regeneration vessel 14 by adjusting the temperature utilizing a heater or heat exchanger (not shown) to increase or decrease solution temperature; the pH, if needed, by increasing or decreasing the rate of base or acid feed; and the Eh, if needed, by increasing or decreasing the oxidizer concentration of the aqueous oxidizing solution.
  • An optional, final quality control loop is provided utilizing the readers 68 A and 68B checking the loading performance of the processed oxides of manganese sorbent by sending, for example, SOx and NOx readings back to the controller
  • the conhoUer 67 would then adjust the precipitation vessel 30 and regeneration vessel 14 parameters, if needed, to provide precipitated oxides of manganese and regenerated oxides of manganese, respectively, capable of removing target pollutants at the targeted removal rates.
  • the same controller may also be used to control the entire operation of the removal system 60, the regeneration system 10 and the precipitation system 30 and their components as discussed above including, pre-oxidation rinse 12, filtration unit 16, rinse device 17, dryer 18, comminuting device 19, sorbent feeder device 64 and the by-products processing vessel 66, and electrolytic cell device (not shown but depicted in Figure 11) or separate controllers may be provided.
  • the regeneration and precipitation system 20 is depicted as integrated with removal system 60.
  • the operation and control of the integrated systems 20 and 60 with conhoUer 67 can be understood as being substantially the same with respect to corresponding components, shown and not shown, as described immediately above with respect to the integrated systems 10, 30 and 60.
  • the conhoUer 67 will be in electronic communication with the probes of a single oxidation vessel, vessel 24; otherwise, the operation and function of the electronic control and communication is substantially the same as described. With reference to Figure 10, this is equally applicable to the integration of systems 30 and 60 to the electronic communication and control of the corresponding system components. Note that a variation of regeneration and precipitation method is illustrated.
  • reacted sorbent is rinsed and filtered and routed to dryer 17. It is not direct to a regeneration vessel but the pre- oxidation filtrate is routed to precipitation vessel 34 where precipitation is carried out as previously described.
  • This variation of the method of the invention can be used where the loading capacity oxides of manganese below the reaction product surface coating on the sorbent particles has not been significantly diminished during pollutant removal as to required chemical regeneration. In such cases, it is sufficient to wash away the reaction products, dissolving and disassociating them into the rinse solution or pre-oxidation filtrate and the rinse oxides of manganese can then be dried and comminuted if necessary prior to be reused to capture target pollutants.
  • SOX is one such target pollutant; and that where the gas stream contains primarily concentrations of this pollutant a rinsing is all that is required prior to reuse of the rinsed sorbent, with recover of reaction product ions through precipitation and other processing.
  • filtrates for example in the pre-oxidation, oxidation filtrate and regeneration filtrate as shown in Figure 3, the oxidation and regeneration filtrates shown in Figure 4, the oxidation and precipitation filtrates shown in Figure 5, and the oxidation and preheatment filtrates shown in Figure 6.
  • the filtrates from the water used in the rinses may be utilized for a number of cycles before the spectator ion concentrations reach levels meriting there recovery.
  • oxides of manganese to capture SOX and/or NOX, sulfate, and nitrate, reaction products and their corresponding anions will be present in filtrates.
  • Ion exchange can be utilized as a mechanism for the separation and recovery of useful sulfate and nitrates.
  • the dissolved sulfates and nitrates of manganese in the pre-oxidation filtrate can be processed in anion exchangers, permitting the recovery manganese cations and separation of the sulfate and nitrate anions.
  • the pre-oxidation filtrate containing dissolved sulfates and nitrates, is passed across or through a bed or column of an anion exchange resin that has an affinity for at least one of the two anions to remove those anions.
  • the resin will absorb the anion, for instance the sulfate, while permitting the nitrate to pass through the bed or column.
  • the solution stripped of sulfate can then be passed across or through a second bed or column of yet a second anion exchange resin having an affinity for the nitrate thereby capturing the nitrate.
  • the vessel or vessels containing the resin can be taken off-line and the resin therein stripped of the captured anion and recovered for reuse.
  • Suitable anion exchange resins and vessels are known to and readily identified by those skilled in the art.
  • the anion exchange resin may have a halogen, for example a chloride, in the exchange position on the resin.
  • a halogen for example a chloride
  • the solution after passing through the anion exchanger or exchangers in series, will contain manganese chloride from which manganese carbonate or manganese hydroxide is precipitated with the addition of a soluble carbonate or hydroxide compound; and oxides of manganese as previously described in the discussion of the production of oxides of manganese from the pre-oxidation filtrate.
  • the sulfates and/or nitrates loaded on the resin can in turn be eluted with a solution containing chlorides of potassium, sodium or ammonium in order to generate useful sulfates and nitrate by-products for marketing or further processing.
  • the filtrates and rinse solutions left over after precipitate formation can be utilized for this pu ⁇ ose.
  • the solubility of manganese nitrate is greater than 1.5 times the solubility of manganese sulfate. Solubility of the nitrate is 61.7 mass percent of solute at 250 C, whereas the solubility of sulfate is 38.9 mass percent of solute at 250 C. (Handbook of Chemistry and Physics.)
  • Fractional crystallization a separation technique known to those skilled in the art, can take advantage of the solubility difference to isolate nitrates of manganese and sulfates of manganese from the pre-oxidation filtrate. The filtrate may be cooled and/or evaporated to cause the crystallization of the lesser soluble manganese sulfate which can then be harvested as solid crystals.
  • the solution remaining can be recycled to pre-oxidation rinse 12 for reuse.
  • concentration of manganese nitrate is sufficiently high, the solution after crystallization of sulfates is further cooled and/or evaporated to crystallize the nitrates which can then be harvested as solid crystals.
  • the solution high can be processed with hydroxides or carbonates, as previously described herein above, to generate oxides of manganese and marketable nitrate by-products.
  • Another variation upon the methods of the invention would utilize the difference in thermal decomposition temperatures of nitrates and sulfates of manganese. Nitrates of manganese are reported to decompose at temperatures between 140° C to 450° C to form NO and oxides of manganese.
  • sulfates of manganese are understood to liquefy at elevated temperatures but in the presence of trace amounts of a reducing agent, e.g., carbon monoxide or hydrogen, they decompose to SO2 and MnO which when further heated in an oxidizing atmosphere form oxides of manganese.
  • Reacted sorbent loaded with both nitrates and sulfates of manganese may be heated, prior to introduction into either oxidation vessel 14 or pre-oxidation rinse 12, in an oxidizing atmosphere whereupon manganese oxide is formed and nitrogen dioxide and/or sulfur dioxide are desorbed and captured. If both reaction products are to be thermally desorbed, the reacted sorbent would be heated to and maintained at a first temperature at which nitrates of manganese, primarily, if not exclusively, desorb.
  • the temperature could then be elevated to desorb the sulfates of manganese loaded on the sorbent.
  • the oxides of manganese may then be processed in oxidation vessel 14 as described herein above and the desorbed gas or gases captured and further processed. If the nitrates are first thermally desorbed, the sorbent may be routed either through a pre-oxidation rinse or routed directly to an oxidation vessel
  • FIG. 11 depicts an electrolytic cell 72 used for oxidant production and by-product production along with other beneficial integrated functions that may be used in a Pahlman TM or other pollutant removal system.
  • the oxidant production system 70 includes an electrolytic cell 72.
  • the electrolytic cell 72 has an anolyte compartment 74 with a vent, a positively charged anode 75, a catholyte compartment 76 with a vent, a negatively charged cathode 77, a diaphragm (not shown) dividing the anolyte compartment 74 and the catholyte compartment 76.
  • the oxidant production system 70 further includes a mixing tank 78, a cooler (not shown), a filter/dryer unit 79, an evaporator 80, an anolyte holding tank 82 and oxidant dissolving tank 84.
  • Filtrates solutions containing useful values may contain ions from reaction products, such as sulfates, nitrates, and chlorides, from oxidants, bases and acids, and other constituents such as heavy metals.
  • the filtrate solution, containing sulfate anions for example, is routed to the catholyte compartment 76 where it comes in contact with the cathode 77 that is negatively charged with a direct current (DC) voltage.
  • DC direct current
  • a solution of ammonium sulfate contained within the anolyte holding tank 82 is routed to the anolyte compartment 74 where it comes in contact with the anode 75 that is positively charged with a direct current (DC) voltage.
  • DC direct current
  • ammonium sulfate is purchased and brought into charge the anolyte compartment and is a closed loop that will from time to time need makeup.
  • the sulfate (SO4-2) anion component of the ammonium sulfate (NH4)2SO4 within the anolyte compartment 74 is converted to an ammonium persulfate (NH4)2 S2O8.
  • Some of the now free ammonium ions migrate across the diaphragm to the catholyte compartment 76. There will be migration or leakage of cations and anions across the diaphragm that is between the positively charged anolyte compartment 74 and the negatively charged catholyte compartment 76.
  • K2SO4 potassium sulfate
  • KOH potassium hydroxide
  • MnSO4 stripped sulfate anion from the manganese sulfate
  • An acid and or base may be introduced to the catholyte compartment 76 to adjust pH and is also used to adjust mass balances of cations and anions.
  • Heavy metals such as mercury and arsenic as an example, amongst many other kinds of metals, present in the filtrate will be plated out on the cathode or, depending upon the pH of the solution, could precipitate out as an oxide.
  • Both the anolyte compartment 74 and the catholyte compartment 76 are continually being filled and continually drained.
  • the anolyte compartment 74 drains into the mixing tank 78 and the catholyte compartment 76 drains into the mixing tank 78.
  • Ammonium persulfate ((NH4)2 S2O8) from the anolyte compartment 74 mixes with potassium sulfate (K2SO4) from the catholyte compartment 76 within the mixing tank 78.
  • the electrolytic cell 72 and the mixing tank 78 are cooled with a cooler (not shown) to around 15°C. Solutions entering and exiting the electrolytic cell 72 will be within a few degrees of 15°C. One may choose to run the electrolytic cell 72 at higher temperatures but there is reduced efficiency. Due to the solubility differences of ammonium persulfate and potassium persulfate it is possible to precipitate out the potassium persulfate as it has a much lower solubility than ammonium persulfate.
  • the liquor containing crystals of potassium persulfate and ammonium sulfate in solution is routed to the filter/dryer 79 and the potassium persulfate crystals are separated from the liquor.
  • the potassium persulfate crystals may then be dried for sale and a portion of the potassium persulfate crystals may be routed to the oxidant dissolving tank 84.
  • Distillate from the evaporator 80 is routed to the oxidant dissolving tank 84 to dissolve the potassium persulfate crystals and make a solution that may then be routed for use in sorbent regeneration, pre-treatment, and or precipitation according to the invention.
  • the solution of ammonium sulfate that has been separated from the potassium persulfate in the filter/dryer 79 is routed to the evaporator 80.
  • the concentration of the ammonium sulfate is increased to an acceptable point that provides for a high degree of conversion efficiency into an ammonium persulfate in the anolyte compartment 74.
  • the high concentration of ammonium sulfate solution in the evaporator 80 is routed to the anolyte holding tank 82 to be further routed to the anolyte compartment 74 of the electrolytic cell 72 in a continuing cycle.
  • a polarizer may be used in the anolyte compartment 74 to increase anode efficiency such as but not limited to NH4SCN.
  • Applicants use sulfate containing filtrate solution and ammonium sulfates for pu ⁇ oses of illustrative explanation of the operation and method of production in an electrolytic cell.
  • the filtrate may contain different ion constituents from which different oxidants, such those earlier identified herein, may be made. Again, attention to compatibility may ease processing when certain products are to be formed.
  • the above-described oxidant production methods may be combined with other processing steps to produce useful and marketable by-products from the values in the filtrates and rinse solutions routed to by-products vessel 66. For example, manganese oxides or useful salts may be produced.
  • the ability to produce oxidants from the process streams may eliminate or reduce cost of purchasing commercially available oxidants for use in the methods of the invention.
  • Example 1 outlines procedures to produce lab quantities (100 grams) of virgin oxides of manganese sorbent with Example 2 outlining large industrial quantities (50 pounds) of virgin oxides of manganese sorbent.
  • Figure 7 can be referenced in both examples 1 and 2.
  • precipitation example 1 in the precipitation vessel, 169 grams (1 mole) of MnSO4*H2O and 750 milliliters of water were mixed and heated to lOOoC. In the oxidant vessel, 376 grams (1.4 moles) of K2S2O8 and 1000 milliliters of water were mixed and heated to 80oC. The oxidizing solution was rapidly added to the manganese salt solution in the precipitation vessel and vigorously stirred while the solution was quickly heated to boil and maintained at not less than lOOoC.
  • Oxides of manganese having the formula MnOX where X is about 1.5 to about 2.0 are particularly suitable for dry removal of target pollutants from gas streams.
  • the most active types of oxides of manganese for use as a sorbent for target pollutant removal usually have the formula MnO1.7 to 1.95, which translates into manganese valence states of +3.4 to +3.9, as opposed to the theoretical +4.0 state.
  • MnO1.7 to 1.95 which translates into manganese valence states of +3.4 to +3.9, as opposed to the theoretical +4.0 state.
  • the newly precipitated oxides of manganese sorbent created in example 1 exhibits a valance state of 3.52, which translates into: MnO1.76.
  • a 50 pound quantity of newly precipitated oxides of manganese sorbent was prepared. Precipitation of the 50 pound batch was conducted following the same techniques and procedures as the 100 gram precipitation outlined in example 1 and the pH and Eh values during the precipitation are illustrated in figure 14, with the exception being the target pH level set point and the strength of the KOH solution.
  • the precipitation vessel 84.5 lbs of MnSO4*H2O and 45 gallons of water were mixed and heated to lOOoC.
  • the oxidant vessel 188 lbs of K2S2O8 and 60 gallons of water were mixed and heated to 80oC.
  • Average pore volume was measured to be 0.640cm2/gram and the average pore diameter was found to be 0.0082 microns.
  • Chemical composition analysis was also conducted and the % by weight constituents were measured as follows: 48.9 % manganese (Mn), 6.81 % potassium (K), 18.0 % structural water (H2O), 1.0 % adsorbed water (H2O), and the balance, determined by difference, to be 25.29 % oxygen (O). Additionally, upon analysis, it was found that the newly precipitated oxides of manganese sorbent created in example 2 exhibited a valance state of 3.54, which translates into: MnO1.77.
  • the oxides of manganese compound formed may be a mixture of cryptomelane (KMnO8O16), potassic manganese dioxide monohydrate (K)MnO2*H2O, and/or potassic vernadite ((K)MnO2*yH20). Regardless of the actual chemical designation, applicants have found the resulting oxides of manganese species to be useful to exhibit high loading capacities for target pollutant capture or removal.
  • a glass reactor designed to mimic the gas-solid interactions known to be present in the reaction zones of a PahlmanTM dry target pollutant removal system was utilized for the tests.
  • the glass reactor was a vertically positioned PyrexTM glass cylinder having an internal diameter of 2 inches and a length of approximately 18 inches.
  • test reactor For each test run, 25.0 grams of oxides of manganese were suspended in the reactor using a permeable fritted glass filter positioned approximately 4 inches from the bottom of the reactor, allowing for flow of the gas stream through the reactor while keeping the oxides of manganese suspended.
  • the test reactor was insulated and configured with thermocouples for temperature readings and heating elements for temperature control to maintain a temperature set point, which in the pu ⁇ oses of the conducted testes was 280°F.
  • a NOx and SO2 laden gas stream was pumped into the bottom of the test reactor at a flow rate which provided adequate fluidization of the bed of sorbent to promote optimal gas/solids contact.
  • the reactor was heated during the testing to 280°F and the gas flow rate was metered at a constant 6.5 liters per minute (1pm).
  • the slipstream of actual exhaust gas was from a 570 MW tangentially-fired coal-burning boiler operating on Powder River Basin (PRB) western coal.
  • PRB Powder River Basin
  • the composition of the exhaust gas was measured both on the inlet and outlet of the test reactor with appropriate gas analyzers, as one skilled in the art would employ and for the test run examples presented found to be within the following ranges: Oxygen (O2) 5.8-6.5%), carbon dioxide (CO2) 10-12%, oxides of nitrogen (NOx) 237-300ppm, sulfur dioxide (SO2) 207-455ppm.
  • O2 oxygen
  • CO2 carbon dioxide
  • NOx oxides of nitrogen
  • SO2 sulfur dioxide
  • the slipstream of the NOx and SO2 laden gas stream was passed through the fluidized bed of oxides of manganese, where the flow carried a portion of the sorbent up onto a sintered metal filter, thus creating a filter cake, which mimics a bag house reaction chamber of a PahlmanTM dry target pollutant removal system.
  • SO2 and NOX concentrations were measured continuously alternating from the reactor inlet and outlet utilizing a continuous emissions monitoring system (CEMS).
  • SO2 concentrations were measured utilizing a Bovar Western Research model 921NMP spectrophotometric instrument and NOX concentrations were measured utilizing a Thermo Electron model 42H chemiluminescent instrument, h order to obtain accurate and reliable emission concentrations, sampling and reporting was conducted in accordance with US EPA P T/US03/07098
  • Figure 13 shows the NOx loading curves.
  • EMD type oxides of manganese was at least achieving 90% NOx removal on a ppm basis for 12 minutes, during which time an accumulative total of 0.0451 grams of NOx entered into the laboratory test reactor with only 0.0029 grams of NOx exiting the reactor, for a total of 0.0422 grams of NOx being captured by the virgin EMD type oxides of manganese sorbent.
  • CMD type oxides of manganese was at least achieving 90% NOx removal on a ppm basis for 27 minutes, during which time an accumulative total of 0.1157 grams of NOx entered into the laboratory test reactor with only 0.0034 grams of NOx exiting the reactor, for a total of 0.1123 grams of NOx being captured by the virgin CMD type oxides of manganese sorbent.
  • Precipitated sorbent example 1 which was previously described in this application, achieved 90% NOx removal on a ppm basis for 102 minutes, with an accumulative total of 0.4372 grams of NOx entering the laboratory test reactor with only 0.0067 grams exiting, for a total of 0.4305 grams of NOx being captured by the oxides of manganese sorbent precipitated according to methods of the applicants invention.
  • the second example provided achieved 90% NOx removal on a ppm basis for 181 minutes, with an accumulative total of 0.6801 grams of NOx entering the laboratory test reactor with only 0.0125 grams exiting, for a total of 0.6676 grams of NOx being captured by the oxides of manganese precipitated in example 2, detailed previously in this application. From the provided graph in figure 13 and the NOx loading rates provided, applicants have illustrated the ability of the oxides of manganese precipitated according to this invention to exhibit substantially improved NOx loading rates, as compared to commercially available oxides of manganese
  • FIG. 12 shows the SO2 loading curves.
  • EMD type oxides of manganese was at least achieving 99% SO2 removal on a ppm basis for 18 minutes, during which time an accumulative total of 0.0999 grams of SO2 entered into the laboratory test reactor with only 0.0009 grams of SO2 exiting the reactor, for a total of 0.0990 grams of SO2 being captured by the virgin EMD type oxides of manganese sorbent.
  • CMD type oxides of manganese was at least achieving 99% SO2 removal on a ppm basis for 36 minutes, during which time an accumulative total of 0.2022 grams of SO2 entered into the laboratory test P T/US03/07098
  • Precipitated sorbent example 1 which was previously described in this application, achieved 99% SO2 removal on a ppm basis for 120 minutes, with an accumulative total of 0.5082 grams of SO2 entering the laboratory test reactor with only 0.0016 grams exiting, for a total of 0.5066 grams of SO2 being captured by the oxides of manganese sorbent precipitated according to methods of the applicants invention.
  • the second example provided achieved 99% SO2 removal on a ppm basis for 214 minutes, with an accumulative total of 1.6984 grams of SO2 entering the laboratory test reactor with only 0.0096 grams exiting, for a total of 1.688 grams of SO2 being captured by the oxides of manganese precipitated in example 2, detailed previously in this application.
  • applicants have illustrated the ability of the oxides of manganese precipitated according to this invention to exhibit substantially improved loading rates for SO2, as compared to commercially available oxides of manganese
  • the data from the lab-scale tests presented in Figure 13 and 12 illustrate the increased loading capacity for target pollutants NOx and SO2 that is achievable with the methods of the applicants' invention.
  • Figures 13 and 12 serve to illustrate the differential loading rates of target pollutants, specifically NOx and SO2.
  • the loading rate for SO2 is approximately 2.5 times the loading rate of NOx by weight; with SO2 in example 1 precipitated sorbent capturing 1.688 grams of SO2 at a 99% removal rate and 0.6676 grams of NOx at a 90% removal rate.
  • the differential loading rates for NOx and SO2 are believed to be indicative of the reaction kinetics of the removal process.
  • Figurel4 contains the ph and Eh values through time for precipitation of oxides of manganese reactions, as outlined above in examples 1 and 2.
  • the pH was held constant at the pH set point for the duration of the approximate 45 minute production time.
  • the pH set point of 1.85 was reached within two minutes of the solution reaching 100°C
  • the Eh increased from 1150 to about 1380 within about 12 minutes.
  • the Eh remained at about 1380 for the remainder of the 45 minute reaction time.
  • the pH set point of 3.5 was reached within two minutes of the solution reaching 100°C, the Eh increased to a lower value of 1325 within about 10 minutes.
  • Example 1 where the pH set point of 1.85 was reached within two minutes of the solution reaching 100°C, the Eh increased from 1150 to about 1380 within about 12 minutes. The Eh remained at about 1380 for the remainder of the 45 minute reaction time.
  • Example 2 where the pH set point of 3.5 was reached within two minutes of the solution reaching 100°C, the Eh increased to a lower value of 1325 within about 10 minutes.
  • Both Examples 1 and 2 were conducted with the same ratio of oxidant to manganese sulfate; however, their respective pH set points resulted in differing Eh solution values.
  • the resulting solution Eh value for the uncontrolled case is approximately 50 millivolts below the controlled case, but additionally the controlled case reached its stable Eh value at about 12 minutes where the uncontrolled case took about 19 minutes to reach its stable Eh value.
  • One possible result of the decreased solution Eh and the loss of time at the stable Eh condition would be to move the solution outside of the MnO2 stability area, producing oxides of manganese with decreased target pollutant loading rates or to require additional reaction time, which could negatively affect the overall economics of the regeneration, pretreatment, or precipitation process.
  • Applicants utilize there system for electronic process controls (discussed in this application) to avoid such negative impacts.

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PCT/US2003/007098 2002-03-06 2003-03-06 Regeneration, pretreatment and precipitation of oxides of manganese WO2003076070A1 (en)

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AU2003218018A AU2003218018A1 (en) 2002-03-06 2003-03-06 Regeneration, pretreatment and precipitation of oxides of manganese
JP2003574330A JP2005518938A (ja) 2002-03-06 2003-03-06 マンガン酸化物の再生、前処理および沈殿
PCT/US2003/018419 WO2004009232A1 (en) 2002-06-11 2003-06-11 Disassociation processing of metal oxides
AU2003239975A AU2003239975A1 (en) 2002-06-11 2003-06-11 Disassociation processing of metal oxides
US10/461,888 US20040101457A1 (en) 2002-06-11 2003-06-11 Disassociation processing of metal oxides

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CN106582253A (zh) * 2016-12-22 2017-04-26 贵州大学 一种锰酸铁用于烟气脱硫脱汞处理方法
CN114212828A (zh) * 2021-12-31 2022-03-22 湖南烯富环保科技有限公司 一种硫酸锰溶液除杂方法

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WO2010073350A1 (ja) * 2008-12-25 2010-07-01 ズードケミー触媒株式会社 ＮＯｘ吸収剤及びその製造方法並びにその除去方法
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CN106582253A (zh) * 2016-12-22 2017-04-26 贵州大学 一种锰酸铁用于烟气脱硫脱汞处理方法
CN106582253B (zh) * 2016-12-22 2019-08-02 贵州大学 一种锰酸铁用于烟气脱硫脱汞处理方法
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