Cleaning stack gas
09737849 · 2017-08-22
Assignee
Inventors
Cpc classification
Y02P20/151
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
B01D53/864
PERFORMING OPERATIONS; TRANSPORTING
B01D53/8637
PERFORMING OPERATIONS; TRANSPORTING
B01D53/8631
PERFORMING OPERATIONS; TRANSPORTING
B01D53/8643
PERFORMING OPERATIONS; TRANSPORTING
B01D53/8665
PERFORMING OPERATIONS; TRANSPORTING
B01D53/8671
PERFORMING OPERATIONS; TRANSPORTING
B01D2257/602
PERFORMING OPERATIONS; TRANSPORTING
F23J2219/10
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F23J15/02
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
B01D53/8693
PERFORMING OPERATIONS; TRANSPORTING
B01D2257/404
PERFORMING OPERATIONS; TRANSPORTING
Y02E20/32
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
Y02C20/10
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
B01D53/885
PERFORMING OPERATIONS; TRANSPORTING
International classification
B01D53/88
PERFORMING OPERATIONS; TRANSPORTING
Abstract
A method and apparatus for cleaning and recycling stack gas from coal-fired power plants, from natural or propane burning heating plants, or from cement kilns by using renewable catalysts of zeolite to separate pollutants into recyclable and reusable materials. The method reduces from the stack gas carbon monoxide (CO), carbon dioxide (CO.sub.2), nitrogen oxide (NOx), sulfur oxide (SOx) as well as halogens such as chloride and fluorides and trace metals particularly, mercury, lead, and zinc. The method and apparatus also result in production of fertilizer products by purging with gaseous or liquid nitrogen the zeolite beds through which the stack gas flows. The oxygen generated may be recycled to the burners in the plant.
Claims
1. Apparatus for cleaning stack gases comprising: (a) a first catalytic flow-through bed of natural calcium zeolite with a porosity of a total surface area of not greater than 1200 m.sup.2/g adapted to reduce sulfur oxides positioned in an exhaust stack; (b) a second catalytic flow-through bed of a blend of natural sodium zeolite and natural calcium zeolite of a porosity with a total surface area of not greater than 1200 m.sup.2/g adapted to reduce nitrogen oxides positioned in the exhaust stack above the first bed; (c) a third catalytic flow-through bed of natural calcium zeolite with a porosity of a total surface area not greater than 1200 m.sup.2/g adapted to reduce carbon oxides and mercury oxides positioned in the exhaust stack above the second bed; (d) the exhaust stack adapted to provide a gas flow selected from the group consisting of volatiles from combustion of coal or combustion of natural gas or from a cement kiln sequential through the first catalytic flow-through bed, the second catalytic flow-through bed, and the third catalytic flow-through bed each catalytic bed collecting solids and providing stack gases exiting the third catalytic flow-through bed with at least 70% reduction in sulfur oxides, nitrogen oxides, and carbon oxide; and (e) the first catalytic flow-through bed, the second catalytic flow-through bed, and the third catalytic flow-through bed are each provided on rotating disks such that the stack gases can be continually passed through the first catalytic flow-through bed, the second catalytic flow-through bed, and the third catalytic flow-through bed to provide collection of solids and/or liquids while other portions or beds of like compositions are purged with nitrogen to collect the solids and/or liquids from the beds.
2. The apparatus as set forth in claim 1 where the first catalytic flow-through bed, the second catalytic flow-through bed, and the third catalytic flow-through bed are each positioned between screens each of between 150 and 250 mesh.
3. The apparatus as set forth in claim 1 where the blend of natural sodium zeolite and natural calcium zeolite in the second catalytic flow-through bed is between 25% and 75%.
4. The apparatus as set forth in claim 1 where the exhaust stack is adapted to exit gases from the third catalytic flow-through bed having at least 90% reduction in sulfur oxides, nitrogen oxides, and carbon oxide compared to the stack gases delivered to the first catalytic flow-through bed.
5. The apparatus as set forth in claim 1 where the exhaust stack is adapted to exit gases from the third catalytic flow-through bed having at least 95% reduction in sulfur oxides, nitrogen oxides, mercury oxide and carbon oxide compared to the stack gases delivered to the first catalytic flow-through bed.
6. The apparatus as set forth in claim 1 where the first catalytic flow-through bed, the second catalytic flow-through bed, and the third catalytic flow-through bed each have a porosity of a total surface area not greater than 800 m.sup.2/g.
7. The apparatus as set forth in claim 1 further comprising at least two series of sequential first catalytic flow-through bed, second catalytic flow-through bed, and third catalytic flow-through bed provided in parallel so stack gases can be cleaned through one of the series of beds while other series of beds can be cleaned.
8. The apparatus as set forth in claim 1 where a fourth catalytic flow-through bed of calcium zeolite is provided in the exhaust stack below the first catalytic flow-through bed with a porosity of a total surface area not greater than 1200 m.sup.2/g adapted to collect bauxite compounds before passage through the first catalytic flow-through bed.
9. The apparatus as set forth in claim 8 where the fourth catalytic flow-through bed is provided in a rotating disk so the stack gases are continuously move there through while another portion of the disk is being purged with nitrogen.
10. The apparatus as set forth in claim 8 where the fourth catalytic flow-through bed has a porosity of a total surface area not greater than 800 m.sup.2/g.
11. The apparatus as set forth in claim 8 where the exhaust stack is adapted to exit gases from the third catalytic flow-through bed with at least 95% reduction in bauxite compounds, sulfur oxides, nitrogen oxides, mercury oxides, and carbon oxide compared to the stack gases delivered to the fourth catalytic flow-through bed.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
(1) The following description is described of the accompanying drawings:
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DETAILED DESCRIPTION OF THE DRAWINGS
(12) Referring to
(13) The stack gases 16, now processed by preheater 14, are conveyed to an emission control unit where the stack gases 16 are circulated to emission control system 18 through inlet 20 and allowed to rise through the emission control system 18 and up through gas cleaning apparatus 22. The stack gases 16 at this point typically include carbon monoxide, carbon dioxide, nitrogen oxides and sulphur oxides. The stack gases 16 also include water and particulates, such as aluminum oxides, mercury compounds and other particulate matters, such as uranium and rare earth metals, as well as halogens, such as fluoride and chloride.
(14) With reference to
(15) First catalytic flow-through bed 24 is calcium zeolite comprised of natural zeolite particles with a majority between 44 μm and 64 μm in size. By a “majority” in the particle size range means here, as well in this application, that is highest in like particle size increments and that it necessarily is not 50% of the particle sizes in the zeolite of the bed. The calcium zeolite is a calcium-sodium-potassium aluminosilicate that is relative high calcium oxide that is available from a natural source. Typical chemical analyses of such calcium zeolite are (i) 2.85% calcium oxide (CaO), 2.85% potassium oxide (K.sub.2O), 0.98% manganese oxide (MgO), 0.06% manganese oxide (MnO), 0.19% titanium dioxide (TiO.sub.2), 0.05% potassium oxide (P.sub.20.sub.5), 0.03% sodium oxide (Na.sub.2O), 11.43% aluminum oxide (Al.sub.2O.sub.3), 1.26% ferric oxide (Fe.sub.2O.sub.3) 66.35% silicon dioxide (SiO.sub.2) and 13.28% LOI; and (ii) 3.4% calcium oxide (CaO), 3.0% potassium oxide (K.sub.2O), 1.5% manganese oxide (MgO), 0.05% potassium oxide (P.sub.20.sub.5), 0.3% sodium oxide (Na.sub.2O), 12.1% aluminum oxide (Al.sub.2O.sub.3), 1.6% ferric oxide (Fe.sub.2O.sub.3), 70.0% silicon dioxide (SiO.sub.2). A source for calcium zeolite, amongst others, is St. Cloud Mining Company mines at Winston and Truth or Consequences, N. Mex. 87901, or a similar mine available in other parts of the world. By natural zeolite here and elsewhere in this description refers to that which is mined as opposed to artificial created.
(16) The depth and breadth of the first bed 24 is determined by the flow rate of the stack gases 16 and desired pressure drop, and the physical dimensions of the stack 32 through which stack gases 16 are conveyed at the gas cleaning apparatus 22. First catalytic flow-through bed 24 is provided as a flow-through bed held in position by lower screen 34 and upper screen 36 each of between 150 and 250 mesh designed to hold the bed of calcium zeolite in position while allowing flow through of the stack gases 16.
(17) The primary function of first catalytic flow-through bed 24 is to splitting carbon monoxide and carbon dioxide retaining the carbon in the zeolite bed. First catalytic flow-through bed 24 also captures ash and other particular matter as well as bauxite compound if the fourth catalytic flow-through bed 30 is not provided as shown in
(18) The stack gases 16 in cleaning apparatus 22 then flow through second catalytic flow-through bed 26 positioned adjacent first catalytic flow-through bed 24. Second catalytic flow-through bed 26 is comprised of a blend between 25 and 75% of sodium zeolite and calcium zeolite with a majority of the natural sodium and calcium zeolite particles between 65 μm and 125 μm in size available from a natural source. The source of the calcium zeolite can be the same as that used to provide first catalytic flow-through bed 24, but with a majority particle size between 65 μm and 125 μm. The sodium zeolite may be natural sodium-potassium clinoptilolite that is relative high sodium oxide. Typical chemical analyses of such sodium zeolite are (i) 3.5% sodium oxide (Na.sub.2O), 3.8% potassium oxide (K.sub.2O), 11.9% aluminum oxide (Al.sub.2O.sub.3), 0.7% ferric oxide (Fe.sub.2O.sub.3), 0.8% calcium oxide (CaO), 0.4% manganese oxide (MgO), 0.02% manganese oxide (MnO), 0.1% titanium oxide (TiO.sub.2) and 69.1% silicon dioxide (SiO.sub.2), and (ii) 3.03% sodium oxide (Na.sub.2O), 3.59% potassium oxide (K.sub.2O), 10.27% aluminum oxide (Al.sub.2O.sub.3), 0.86% ferric oxide (Fe.sub.2O.sub.3), 1.77% calcium oxide (CaO), 0.00% potassium oxide (K.sub.2O), 0.4% manganese oxide (MgO), 0.02% manganese oxide (MnO), 0.11% titanium oxide (TiO.sub.2), 69.1% silicon dioxide (SiO.sub.2), and 13.09% LOI. A source of the sodium zeolite, amongst others, is the St. Cloud mines in Ash Meadows, Nev., or a similar mine in other parts of the world. Again, the size and depth of the second set of the flow though bed is determined by the physical dimensions of the stack 32 and the flow rate and pressure drop through the stack 32 at the gas cleaning apparatus 22.
(19) The primary purpose of the second flow-through bed 26 is to capture and split nitrogen oxides (NOx) in the stack gas 16. The second catalytic flow-through bed 26 is also effective in reduce water and metal compounds such as mercury, lead, uranium and other trace materials. Again, a lower screen 38 and an upper screen 40 may be provided with mesh sizes between 150 and 250 mesh to maintain the second catalytic flow-through bed 28 while allowing appropriate flow through of stack gas 16.
(20) On exiting the second catalytic flow-through bed 26, the stack gases 16 flow through the adjacent third catalytic flow-through bed 28. The third catalytic flow-through bed is comprised of calcium zeolite similar in chemical analysis to the first catalytic flow-through bed 24 with a majority of natural zeolite particles size between 78 μm and 204.
(21) The third catalytic flow-through bed 28 is primarily to split sulfur oxides present in the stack gas 16. The third catalytic flow-through bed may also reduce sulfur acids, calcium compounds and ash in the stack gas 16. The composition of natural calcium zeolite in third catalytic flow-through bed 28 may be of the same composition as the first catalytic flow-through bed 24, but with different zeolite particle size as described. Again, a lower screen 42 and an upper screen 44 is with mesh size between 150 and 250 mesh is provided to maintain the third catalytic flow-through bed 28.
(22) The currently disclosed invention is operative as evidenced by substantial increase in oxygen exiting the third catalytic bed 28 compared to the oxygen levels in the stack gas entering the first catalytic bed 24. The paper by Yoshitaka Toda et al. titled “Activation And Splitting of Carbon Dioxide on The Surface Of An Inorganic Electrode Material” (Published 31 Jul. 2013) suggests a potential mechanism, namely, splitting off oxygen from CO.sub.2 leaving CO to be then reduced. One mechanism to accomplish CO.sub.2 splitting is electrophoresis disassociation of oxygen in the presence of the zeolite catalyst bed into various forms of carbon and oxygen, including oxygen radicals, such as the superoxide O.sub.2-anion. Metal clusters formed in the process in the presence of the zeolite catalyst may also provide additional catalytic activity resulting in CO.sub.2 splitting.
(23) Also, the nitrogen from the stack gas is in large part retained in the zeolite beds and is available for reaction with available oxygen present particularly during purging as described below.
(24) Where a fourth catalytic flow-through bed 30 is provided as shown in
(25) Where the fourth catalytic flow-through catalytic bed 30 is provided as shown in
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(30) It was found by the comparison of the data that carbon dioxide in the stack gas 16 was reduced by at least 95% by the stack gas from coal-fired plant entering cleaning apparatus 22; sulfur dioxide in the stack gas 16 was reduced by at least 95% from the stack gas entering the cleaning apparatus 22; and nitrous oxide in the stack gas 16 was split and reduced by 95% or more by the stack gas entering cleaning apparatus 22. These results demonstrate the high effectiveness of the cleaning apparatus 22 in cleaning stack gas from a coal-fired power plant.
(31) While the cleaning apparatus is in operation, material including carbon, sulfur, nitrogen, and other products are collected by the catalytic through-flow beds. Intermittently, as appropriate, the first catalytic through-flow bed 24, second catalytic through-flow bed 26, third catalytic through-flow bed 28 and fourth catalytic through-flow bed 30 (where present) may be switched between parallel systems as shown in
(32) During the purging process, purge fluid is released from a reservoir 54 and the purging fluid passes through one or more of the first catalytic through-flow bed 24, second catalytic through-flow bed 26, third catalytic through-flow bed 28 and fourth catalytic through-flow bed 30 (where present). The purge fluid may be pressurized or may fall by gravity through one or more of the catalytic through-flow beds, releasing material from the catalytic through-flow beds.
(33) This purging produces a solid waste largely of nitrate composition that is discharged through outlet 50 into a container 52. The nitrate compounds can be formed by reaction of the nitrogen and nitrogen compounds retained by the zeolite beds with the oxygen present during purging. The mechanism of formation of these nitrate fertilizer materials may involve catalytic splitting of the nitrogen compounds present in the stack gas stream into nitrogen retained in the zeolite beds and/or the nitrogen compounds retained in the zeolite beds, which are then available to react with free oxygen atoms and/or oxygen radicals in purging to form nitrate powders. Because large amounts of nitrogen are present in the stack gas stream, relatively large amounts of nitrate compounds may be present in the fertilizers produced. These nitrate fertilizers provide a value byproduct of the present process.
(34) If a fourth catalytic through-flow bed 30 is provided, that bed may be separately purged through a separate outlet into a separate container (not shown) to allow for recovery of bauxite compounds as a separate product. Where a fourth catalytic bed is not provided, the bauxite compounds are collected in the first catalytic through-flow bed 24 and provided as a part of a fertilizer composition and product. Metals such as mercury, zinc, lead and other trace metals are also collected as part of the fertilizer product that is recovered.
(35) The purging may also produce gases, such as oxygen (O.sub.2) and nitrogen (N.sub.2) that may be extracted by a first gas outlet 58 that transports a portion of the gases (e.g. N.sub.2) to a recycler and a second gas outlet 60 that transports a portion of the gases (e.g. O.sub.2) to the burner for combusting the fuel.
(36) A test apparatus is illustrated in
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(38) The tests with the test facility shown in
(39) While the invention has been described with reference to certain embodiments, it will be understood by those skilled in the art that various changes may be made and equivalents may be substituted without departing from the scope of the invention. In addition, many modifications may be made to adapt a particular situation or material to the teachings of the invention without departing from its scope. Therefore, it is intended that the invention not be limited to the particular embodiments disclosed, but that the invention will include all embodiments falling within the scope of the appended claims.