CN103285805A - Mercury removal agent and preparation method thereof - Google Patents
Mercury removal agent and preparation method thereof Download PDFInfo
- Publication number
- CN103285805A CN103285805A CN2013102421354A CN201310242135A CN103285805A CN 103285805 A CN103285805 A CN 103285805A CN 2013102421354 A CN2013102421354 A CN 2013102421354A CN 201310242135 A CN201310242135 A CN 201310242135A CN 103285805 A CN103285805 A CN 103285805A
- Authority
- CN
- China
- Prior art keywords
- removal agent
- carrier
- mercury removal
- mercury
- oxide
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
- B01D53/04—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/64—Heavy metals or compounds thereof, e.g. mercury
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/06—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/06—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
- B01J20/08—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04 comprising aluminium oxide or hydroxide; comprising bauxite
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/10—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
- B01J20/103—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate comprising silica
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/10—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
- B01J20/14—Diatomaceous earth
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/10—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
- B01J20/16—Alumino-silicates
- B01J20/18—Synthetic zeolitic molecular sieves
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/20—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28054—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
- B01J20/28057—Surface area, e.g. B.E.T specific surface area
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28054—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
- B01J20/28069—Pore volume, e.g. total pore volume, mesopore volume, micropore volume
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/3078—Thermal treatment, e.g. calcining or pyrolizing
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
- B01J20/3202—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the carrier, support or substrate used for impregnation or coating
- B01J20/3204—Inorganic carriers, supports or substrates
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
- B01J20/3231—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
- B01J20/3234—Inorganic material layers
- B01J20/3236—Inorganic material layers containing metal, other than zeolites, e.g. oxides, hydroxides, sulphides or salts
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/30—Alkali metal compounds
- B01D2251/304—Alkali metal compounds of sodium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/30—Alkali metal compounds
- B01D2251/306—Alkali metal compounds of potassium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/10—Inorganic adsorbents
- B01D2253/102—Carbon
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/10—Inorganic adsorbents
- B01D2253/106—Silica or silicates
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/10—Inorganic adsorbents
- B01D2253/112—Metals or metal compounds not provided for in B01D2253/104 or B01D2253/106
- B01D2253/1124—Metal oxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/30—Physical properties of adsorbents
- B01D2253/302—Dimensions
- B01D2253/306—Surface area, e.g. BET-specific surface
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/30—Physical properties of adsorbents
- B01D2253/302—Dimensions
- B01D2253/311—Porosity, e.g. pore volume
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/2073—Manganese
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20746—Cobalt
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20753—Nickel
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20776—Tungsten
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2256/00—Main component in the product gas stream after treatment
- B01D2256/24—Hydrocarbons
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/60—Heavy metals or heavy metal compounds
- B01D2257/602—Mercury or mercury compounds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0283—Flue gases
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
Abstract
The invention discloses a mercury removal agent and a preparation method thereof. The mercury removal agent comprises the following components in percentage by weight: 40wt%-90wt% of carriers, 1wt%-40wt% of active ingredients and 0-30wt% of modifying agent, wherein the modifying agent is halogen or halide; and the active ingredients are a mixture of oxides of at least two oxidizing metals. The preparation method of the mercury removal agent comprises the following steps of: placing the carriers into one or more soluble oxidizing metal salt solutions, soaking and drying, roasting and placing in one or more soluble metal salt solutions except from the aforementioned soluble metal salts, soaking, drying and roasting to obtain the mercury removal agent. The mercury removal agent disclosed by the invention is unnecessary to vulcanize, capable of using the oxidizing metal oxides as the active ingredient and using the halogen or the halide as the modifying agent, and provided with the beneficial effects of having mercury capacity bigger than 10wt% and the mercury removing efficiency higher than 99.9%. Moreover, the mercury removal agent further can be extensively applied to the removing process of the mercury metal in smoke gas, synthesis gas, natural gas as well as a mercury-containing gas source in liquid substance.
Description
Technical field
The present invention relates to aerochemistry adsorption cleaning field, particularly relate to a kind of mercury removal agent that removes for flue gas, synthesis gas and natural gas and liquid mercury metal and preparation method thereof.
Background technology
At present, discharge mercury in the process because coal burning, vaporizing system synthesis gas and natural gas extraction etc. utilize, wherein, this mercury mainly exists with three kinds of forms, element mercury (Hg
0), oxidation state mercury (Hg
2+) and particle mercury (Hg
P).Hg
0Because its fusing point is low, volatility is high and be insoluble in characteristics such as water, be difficult to be caught by cleaner, be discharged in the atmosphere, form is relatively stable, present coal-fired mercury emissions has become maximum artificial mercury pollution emission source, the energy resource consumption of China is based on coal, and controlling coal-fired mercury emissions is the environmental problem that solution is badly in need of in China.Therefore, develop promising mercury control technology and effectively remove mercury, particularly Hg in coal gas, synthesis gas and the natural gas
0It is one of environmental pollution improvement's urgent problem.
And disclosed mercury removal agent in the present prior art, its demercuration performance is undesirable, because the mercury of this kind mercury removal agent holds and demercuration efficient is all less, and a lot of mercury removal agents all needs sulfuration just can work, this makes not only all may exist the secondary pollution problem in preparation of adsorbent also is to use. in addition, the oxidability of currently used monometallic mercury removal agent is low, be difficult to the mercury of metallic state is converted into the mercury of the oxidation state that steam forces down, so press for a kind of high-performance and don't produce many metal actives mercury removal agent of secondary pollution.
Summary of the invention
Based on this, the invention provides a kind of mercury removal agent and preparation method thereof.
The concrete technical scheme that solves the problems of the technologies described above is as follows:
A kind of mercury removal agent, described mercury removal agent comprise the carrier of 40-90wt%, the active component of 1-40wt% and the modifier of 0-30wt%; Described modifier is halogen or halide; Described active component is the mixture of at least two kinds oxidisability metal oxide; Described modifier can have been strengthened the ability of oxidation simple substance mercury by chemical reaction, also with regard to the corresponding amount that has increased oxidized and fixing mercury, is conducive to the raising that demercuration efficient and mercury hold.
Among some embodiment, described halogen is bromine therein, and described halide is soluble bromine salt.
Among some embodiment, described bromine salt is ammonium bromide, KBr or sodium bromide therein.
Among some embodiment, described oxidisability metal oxide is manganese dioxide, cobalt oxide, cerium oxide, iron oxide, tungsten oxide, molybdenum oxide, cupric oxide or nickel oxide therein.
Therein among some embodiment, described carrier is at least a in activated alumina, modified active aluminium oxide, silica, kaolin, diatomite, active carbon, aluminium hydroxide or the molecular sieve; Preferred activated alumina, modified active aluminium oxide or active carbon.
Among some embodiment, the percentage by weight of described modifier is 0-25wt% therein; Preferably, the percentage by weight of modifier is 5-21wt%.
Among some embodiment, the percentage by weight of described active component is 5-35wt% therein; The percentage by weight of described carrier is 50-80wt%; The specific area of described carrier is 20-500m
2/ g, pore volume are 0.1-1.0cm
3/ g; Preferably, the percentage by weight of described active component is 10-35wt%; The percentage by weight of described carrier is 55-75wt%; Described carrier can improve dispersion degree of active components in the mercury removal agent, and with the absorption area that contacts of mercury, and the adsorbance of mercury, thus improved the demercuration efficient of mercury removal agent.
Among some embodiment, the specific area of described carrier is 50-450m therein
2/ g, pore volume are 0.2-0.7cm
3/ g; The mercury that the specific area of described carrier and pore volume more help to improve mercury removal agent holds and demercuration efficient.
The preparation method of above-mentioned mercury removal agent comprises the steps:
(1) carrier is placed a kind of solution of soluble metallic salt, dipping 1-24h gets load salt carrier;
(2) after the load salt carrier drying or roasting with step (1) gained, place one or more the soluble metal salting liquid except the described soluble metallic salt of step (1), dry behind the dipping 1-24h, at aerobic (with active carbon during as carrier, anaerobic) under the condition, in 350-600 ℃ of following calcining 2-10h, get the metal oxide-loaded carrier after the calcining;
(3) the metal oxide-loaded carrier after the calcining of step (2) gained is placed modifier solution, dry behind the dipping 1-24h, in 100-300 ℃ of following roasting 1-6h, get final product again.Sometimes hold in order to increase mercury, can place modifier solution dipping, dry, roasting to above metal oxide-loaded carrier again.
Among some embodiment, described soluble metallic salt is nitrate, sulfate, acylate or the halide salt of oxidisability metal oxide therein; Described oxidisability metal oxide is that soluble oxidized metal salt is prepared from through calcining;
The above acylate comprises: formates, acetate, citrate, oxalates etc.Certainly be not limited to above several salt, the stable acylate that forms solution of various energy and solvent for use is all included.
Among some embodiment, temperature dry described in step (2) and the step (3) is 50-200 ℃ therein, and the time is 1-8h; Preferred temperature is 100-120 ℃.
A kind of mercury removal agent of the present invention and preparation method thereof has the following advantages and beneficial effect:
(1) mercury removal agent of the present invention sulfur-bearing not, as active component, halogen or halide are as modifier with the oxidisability metal oxide for it, and the mercury that the mercury removal agent that makes has greater than 10wt% holds, and demercuration efficient reaches more than 99.9%.
(2) mercury removal agent of the present invention can be widely used in flue gas, synthesis gas and natural gas and the liquid in the mercurous source of the gas in the removing process of mercury metal.
(3) preparation method's preferred aqueous solutions infusion process of the present invention, active component is the metal oxide of oxidation state, preparation process does not need to need to vulcanize just and can work as a lot of existing mercury removal agents, comparatively flexible aspect the carrier selection, as required, can prepare flexibly and be applicable to that different occasions possess the mercury removal agent of different performance.
The specific embodiment
The present invention adopts active constituent loading on carrier, and can select for use modifier to carry out modification in order to realize its removing mercury; Wherein carrier comprises activated alumina, modified active aluminium oxide, kaolin, diatomite, active carbon, aluminium hydroxide, molecular sieve etc., active component is selected manganese dioxide, cobalt oxide, cerium oxide, iron oxide, tungsten oxide, molybdenum oxide for use, the compound of transition metal such as cupric oxide and nickel oxide, modifier is halogen and halide, by oxidation mechanism mercury vapour is converted into mercury oxide.
Halide of the present invention refers to chloride, bromide or iodide;
Described halogen refers to fluorine, chlorine, bromine or iodine;
Described halide salt refers to ammonium chloride, potassium chloride, ammonium bromide, sodium bromide or KBr etc.;
Described molecular sieve refers to the molecular sieve of series such as A series, X series, Y. series, ZSM;
Activated alumina is available from Qingdao connection letter chemical company and Chalco Zibo Aluminium Factory among the following embodiment;
The modified active aluminium oxide is for to use titanium oxide, alkali metal such as potassium or sodium, and alkaline-earth metal such as calcium, magnesium or barium etc. carry out modification to activated alumina, as: the titaniferous activated alumina is available from Qingdao connection letter chemical company.
The present invention will be further described below with reference to specific embodiment.
Embodiment 1
A kind of mercury removal agent comprises the active aluminum oxide carrier of 90wt%, the manganese dioxide of 5wt% and the cobalt oxide active component of 5wt%; The preparation method of this kind mercury removal agent comprises the steps:
(1) choose the 40-60 order, specific surface is 80m
2/ g, pore volume are 0.1cm
3The active aluminum oxide carrier 40g of/g puts into 20ml and contains 7.0gCoCl
26H
2In the solution of O, flooded 1 hour, treat that above-mentioned maceration extract immerses carrier fully after, carrier is taken out;
(2) under 110 ℃ with the carrier drying of step (1) gained 8 hours, remove moisture in the carrier, will have the active aluminum oxide carrier of cobalt chloride to put into through dried load again and contain 5.1gMnCl
24H
2In the solution of O, flooded 24 hours, carrier is taken out, in 120 ℃ of dryings 1 hour, under aerobic conditions, in 400 ℃ of following calcination activations 2 hours, make chlorate decompose, and and then obtain the active aluminum oxide carrier that load has manganese dioxide and cobalt oxide active component, namely obtain mercury removal agent, be designated as A.
Embodiment 2
A kind of mercury removal agent comprises the absorbent charcoal carrier of 56wt%, the cupric oxide of 14wt% and the manganese dioxide active component of 18wt%, the NH of 12wt%
4Cl modifier; The preparation method of this kind mercury removal agent comprises the steps:
(1) get the 40-60 order, specific surface is 400m
2/ g, pore volume are 1.0cm
3The absorbent charcoal carrier 40g of/g puts into 15ml and contains 30.5gCu (NO
3)
23H
2In the solution of O, flooded 12 hours, treat that above-mentioned maceration extract immerses carrier fully after, carrier is taken out;
(2) under 100 ℃ with the carrier drying of step (1) gained 5 hours, remove moisture in the carrier, will have the absorbent charcoal carrier of copper nitrate to put into 12ml through dried load again and contain 29.1gMnCl
24H
2In the solution of O, flooded 12 hours, this carrier taken out, in 120 ℃ of dryings 6 hours, under oxygen free condition, in 450 ℃ of following calcination activations 3 hours, make chlorate decompose, and and then obtain the absorbent charcoal carrier that load has cupric oxide and manganese dioxide active component;
(3) there is the carrier of active component to put into 10ml above-mentioned load and contains 8.7gNH
4In the solution of Cl, flooded 10 hours, carrier is taken out, in 100 ℃ of dryings 3 hours, afterwards under oxygen free condition, in 200 ℃ of following calcination activations 3 hours, namely obtain mercury removal agent, be designated as B.
Embodiment 3
A kind of mercury removal agent comprises the titaniferous active aluminum oxide carrier of 60wt%, the cupric oxide of 22wt% and manganese dioxide active component, the 6wt%NH of 12wt%
4Br modifier; The preparation method of this kind mercury removal agent comprises the steps:
(1) get the 40-60 order, specific surface is 240m
2/ g, pore volume are 0.4cm
3The titaniferous activated alumina 40g of/g puts into 20ml and contains 36.2g (CH
3COO)
2CuH
2In the solution of O, flooded 10 hours, treat that above-mentioned maceration extract immerses carrier fully after, carrier is taken out;
(2) in 110 ℃ times dry 6 hours, remove moisture in the carrier, will have the titaniferous active aluminum oxide carrier of Schweinfurt green to put into 15ml through dried load again and contain 19.1gMnCl
24H
2In the solution of O, flooded 10 hours, carrier is taken out, in 120 ℃ of dryings 6 hours, afterwards under aerobic conditions, in 400 ℃ of following calcination activations 4 hours, make acetate and chlorate decompose, and and then obtain the titaniferous active aluminum oxide carrier that load has cupric oxide and manganese dioxide active component;
(3) there is the carrier of active component to put into 12ml above-mentioned load and contains 3.9gNH
4In the solution of Br, flooded 10 hours, carrier is taken out, in 120 ℃ of dryings 3 hours, afterwards under aerobic conditions, in 250 ℃ of following calcination activations 1 hour, namely obtain mercury removal agent, be designated as C.
Embodiment 4
A kind of mercury removal agent comprises the titaniferous active aluminum oxide carrier of 70wt%, the cupric oxide of 21wt% and the manganese dioxide active component of 9wt%; The preparation method of this kind mercury removal agent comprises the steps:
(1) get the 40-60 order, specific surface is 280m
2/ g, pore volume are 0.6cm
3The titaniferous activated alumina 40g of/g puts into 25ml and contains 26.5gCuCl
22H
2In the solution of O, flooded 12 hours, treat that above-mentioned maceration extract immerses carrier fully after, carrier is taken out;
(2) in 110 ℃ times dry 6 hours, remove moisture in the carrier, will have the titaniferous active aluminum oxide carrier of Schweinfurt green to put into 18ml through dried load more afterwards and contain 12.4gMnCl
24H
2In the solution of O, flooded 10 hours, this carrier is taken out, in 110 ℃ of dryings 5 hours, afterwards under aerobic conditions, in 350 ℃ of following calcination activations 3 hours, make acetate and chlorate decompose, and and then obtain the titaniferous active aluminum oxide carrier that load has cupric oxide and manganese dioxide active component, namely obtain mercury removal agent, be designated as D.
Embodiment 5
A kind of mercury removal agent comprises the active aluminum oxide carrier of 75wt%, the cobalt oxide of 14wt% and the molybdenum oxide active component of 11wt%; The preparation method of this kind mercury removal agent comprises the steps:
(1) get the 40-60 order, specific surface is 200m
2/ g, pore volume are 0.8cm
3The activated alumina 40g of/g puts into 25ml and contains 38.6gCo (NO
3)
2.6H
2In the solution of O, flooded 12 hours, treat that above-mentioned maceration extract immerses carrier fully after, carrier is taken out;
(2) in 100 ℃ times dry 5 hours, remove moisture in the carrier, will have the active aluminum oxide carrier of cobalt nitrate to put into 15ml through dried load more afterwards and contain 7.2g (NH
4)
6Mo
7O
244H
2In the solution of O, flooded 12 hours, this carrier is taken out, in 120 ℃ of dryings 6 hours, afterwards under aerobic conditions, in 400 ℃ of following calcination activations 4 hours, make cobalt nitrate and ammonium molybdate decompose, and and then obtain the active aluminum oxide carrier that load has cobalt oxide and molybdenum oxide active component, namely obtain mercury removal agent, be designated as E.
Embodiment 6
A kind of mercury removal agent comprises the titaniferous active aluminum oxide carrier of 60wt%, molybdenum oxide and the 10wt% manganese dioxide active component of 10wt%, and 20wt%Br
2Modifier; The preparation method of this kind mercury removal agent comprises the steps:
(1) get the 40-60 order, specific surface is 80m
2/ g, pore volume are 0.75cm
3The titaniferous activated alumina 6.5g of/g puts into 25ml and contains (NH
4)
6Mo
7O
244H
2In the solution of O, flooded 24 hours, treat that above-mentioned maceration extract immerses carrier fully after, this carrier is taken out, in 110 ℃ of dryings 6 hours, 400 ℃ of roastings 3 hours in air again obtained the carrier of load molybdenum oxide;
(2) carrier of the above-mentioned load molybdenum oxide that obtains is put into 15ml and contain 12.2gMnCl
24H
2In the solution of O, flooded 12 hours, this carrier is taken out, in 120 ℃ of dry 6h, afterwards under aerobic conditions, in 450 ℃ of following calcination activations 5 hours, make manganese chloride decompose, and and then obtain the titaniferous active aluminum oxide carrier that load has molybdenum oxide and manganese dioxide active component;
(3) there is the carrier of active component to put into 12ml above-mentioned load and contains 13.3gBr
2Solution in, flooded 10 hours, carrier is taken out, in 120 ℃ of dryings 3 hours, afterwards under aerobic conditions, in 250 ℃ of following calcination activations 1 hour, namely obtain mercury removal agent, be designated as F.
Embodiment 7 activity ratings
One, evaluation method
The mercury removal agent that above-described embodiment 1~6 is prepared is particles filled to be in the 1.5ml demercuration clean-up bed of 6mm to internal diameter.Be 8000h at normal temperature, normal pressure, volume space velocity
-1Condition under, be 10500 μ g/m to contain hydrogen sulfide 70ppm and mercury concentration
3The methane of (± 2%) is estimated resulting result such as table 1 through this clean-up bed to the demercuration effect of mercury removal agent.
Two, evaluation result
Demercuration effect comparing result before and after table 1 purifies
As known from Table 1, the mercury removal agent demercuration effect that the present invention prepares is very remarkable, and the mercury appearance can reach more than the 10wt%, and the demercuration rate ranges up to 99.999%.Described demercuration rate refers to the percentage of the amount of mercury in the amount of the mercury that removes and the former source of the gas.As seen, use mercury removal agent of the present invention to have higher demercuration activity, namely mercury holds high and demercuration efficient height.
The above embodiment has only expressed several embodiment of the present invention, and it describes comparatively concrete and detailed, but can not therefore be interpreted as the restriction to claim of the present invention.Should be pointed out that for the person of ordinary skill of the art without departing from the inventive concept of the premise, can also make some distortion and improvement, these all belong to protection scope of the present invention.Therefore, the protection domain of patent of the present invention should be as the criterion with claims.
Claims (10)
1. a mercury removal agent is characterized in that, described mercury removal agent comprises the carrier of 40-90wt%, the active component of 1-40wt% and the modifier of 0-30wt%; Described modifier is halogen or halide; Described active component is the mixture of at least two kinds oxidisability metal oxide.
2. mercury removal agent according to claim 1 is characterized in that, described halogen is bromine, and described halide is soluble bromine salt.
3. mercury removal agent according to claim 2 is characterized in that, described bromine salt is ammonium bromide, KBr or sodium bromide.
4. mercury removal agent according to claim 1 is characterized in that, described oxidisability metal oxide is manganese oxide, cobalt oxide, iron oxide, tungsten oxide, cerium oxide, molybdenum oxide, cupric oxide or nickel oxide; Described carrier is at least a in activated alumina, modified active aluminium oxide, silica, kaolin, diatomite, active carbon, aluminium hydroxide or the molecular sieve.
5. mercury removal agent according to claim 1 is characterized in that, the percentage by weight of described active component is 5-35wt%; The percentage by weight of described carrier is 50-80wt%; The percentage by weight of modifier is 0-25wt%.
6. mercury removal agent according to claim 5 is characterized in that, the specific area of described carrier is 20-500m
2/ g, pore volume are 0.1-1.0cm
3/ g.
7. mercury removal agent according to claim 6 is characterized in that, the specific area of described carrier is 50-450m
2/ g, pore volume are 0.2-0.7cm
3/ g.
8. according to the preparation method of each described mercury removal agent of claim 1-7, it is characterized in that, comprise the steps:
(1) carrier is placed the solution of one or more soluble metallic salts, dipping 1-24h gets load salt carrier;
(2) after the load salt carrier drying or roasting with step (1) gained, place one or more the soluble metal salting liquid except the described soluble metallic salt of step (1), dry behind the dipping 1-24h, in 350-600 ℃ of calcining 2-10h, get the carrier of the load oxidisability metal oxide after the calcining;
(3) carrier with the load oxidisability metal oxide after the calcining of step (2) gained places modifier solution, and is dry behind the dipping 1-24h, in 100-300 ℃ of following roasting 1-6h, gets final product again.
9. the preparation method of mercury removal agent according to claim 8 is characterized in that, described soluble metallic salt is nitrate, sulfate, acylate or the halide salt of oxidisability metal oxide.
10. according to the preparation method of the described mercury removal agent of claim 9, it is characterized in that temperature dry described in step (2) and the step (3) is 50-200 ℃, the time is 1-8h.
Priority Applications (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201310242135.4A CN103285805B (en) | 2013-06-18 | 2013-06-18 | Mercury removal agent and preparation method thereof |
PCT/CN2013/084801 WO2014201782A1 (en) | 2013-06-18 | 2013-09-30 | Mercury-removing agent and preparation method therefor |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201310242135.4A CN103285805B (en) | 2013-06-18 | 2013-06-18 | Mercury removal agent and preparation method thereof |
Publications (2)
Publication Number | Publication Date |
---|---|
CN103285805A true CN103285805A (en) | 2013-09-11 |
CN103285805B CN103285805B (en) | 2015-09-23 |
Family
ID=49087646
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201310242135.4A Expired - Fee Related CN103285805B (en) | 2013-06-18 | 2013-06-18 | Mercury removal agent and preparation method thereof |
Country Status (2)
Country | Link |
---|---|
CN (1) | CN103285805B (en) |
WO (1) | WO2014201782A1 (en) |
Cited By (18)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104107631A (en) * | 2014-07-30 | 2014-10-22 | 沈阳三聚凯特催化剂有限公司 | Desulfurization and demercuration agent and preparation method thereof |
WO2014201782A1 (en) * | 2013-06-18 | 2014-12-24 | 广州博能能源科技有限公司 | Mercury-removing agent and preparation method therefor |
CN104289232A (en) * | 2014-10-10 | 2015-01-21 | 南京正森环保科技有限公司 | Environment-friendly active carbon catalyst as well as preparation method and application thereof to flue gas mercury removal |
CN105107362A (en) * | 2015-09-17 | 2015-12-02 | 昆明理工大学 | Method for deep removal of zero valence mercury in mercury smelting flue gas |
CN105126880A (en) * | 2015-07-24 | 2015-12-09 | 广州博能能源科技有限公司 | Demercuration agent and preparation method thereof |
CN105536499A (en) * | 2014-10-28 | 2016-05-04 | 中国石油天然气股份有限公司 | Mercury removing agent, preparation method and applications thereof |
CN105688819A (en) * | 2016-04-07 | 2016-06-22 | 安庆师范学院 | Adsorbent for removing elemental mercury from coal gas and preparation method of adsorbent for removing elemental mercury from coal gas |
CN106466590A (en) * | 2015-08-14 | 2017-03-01 | Ada碳解决方案有限责任公司 | The adsorbent composition with amorphous halogen species for pollutant chelating |
CN107790152A (en) * | 2017-06-26 | 2018-03-13 | 湖南大学 | It is a kind of to be used to remove catalyst of pernicious gas and its preparation method and application |
US20190184369A1 (en) * | 2017-12-20 | 2019-06-20 | Uop Llc | Enhancement of reduction resistance for manganese oxide adsorbents |
CN110343542A (en) * | 2019-04-23 | 2019-10-18 | 西南石油大学 | A kind of mercury removal agent and preparation method thereof for high mercurous liquid hydrocarbon demercuration |
CN111250042A (en) * | 2020-02-18 | 2020-06-09 | 上海电力大学 | Carbon-based adsorbent for demercuration and preparation method and application thereof |
CN111569834A (en) * | 2020-06-01 | 2020-08-25 | 新疆兵团现代绿色氯碱化工工程研究中心(有限公司) | Mercury removing adsorbent for crude chloroethylene gas |
CN112191226A (en) * | 2020-08-31 | 2021-01-08 | 山东大学 | Method for preparing mercury removal adsorbent by modifying low-temperature plasma and application |
CN112337442A (en) * | 2020-10-15 | 2021-02-09 | 华中科技大学 | Modified algae base, preparation thereof and application of modified algae base as mercury removal adsorbent |
CN112756003A (en) * | 2021-01-12 | 2021-05-07 | 武汉科林化工集团有限公司 | Natural gas catalytic oxidation mercury removal agent and preparation method thereof |
CN113171747A (en) * | 2021-06-02 | 2021-07-27 | 山西格盟中美清洁能源研发中心有限公司 | Preparation method of kaolin-based porous material for adsorbing mercury in coal-fired flue gas |
CN113499664A (en) * | 2021-06-28 | 2021-10-15 | 中国神华煤制油化工有限公司 | Mercury removal agent, preparation method thereof and method for removing elemental mercury in flue gas |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20050247635A1 (en) * | 2001-08-27 | 2005-11-10 | Vo Toan P | Adsorbents for removing heavy metal cations and methods for producing and using these adsorbents |
CN1748868A (en) * | 2005-08-25 | 2006-03-22 | 上海交通大学 | Process for preparing bromine blended metal oxide catalyst |
CN101844074A (en) * | 2010-05-20 | 2010-09-29 | 宁夏华辉活性炭股份有限公司 | Method for preparing activated carbon used for flue gas demercuration |
Family Cites Families (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US8906823B2 (en) * | 2007-09-24 | 2014-12-09 | Basf Corporation | Pollutant emission control sorbents and methods of manufacture and use |
CN101574660A (en) * | 2009-06-11 | 2009-11-11 | 上海交通大学 | Method for preparing mixed compound catalyst used for catalyzing null-valence mercury in flue-gas to be oxidized |
CN102101007B (en) * | 2011-01-27 | 2013-08-14 | 华电环保系统工程有限公司 | Method for removing mercury from smoke in coal fired power plant and mercury removing agent used by same |
CN102366722B (en) * | 2011-11-21 | 2013-06-12 | 国电科学技术研究院 | Denitrition catalyst with mercury removal effect and its preparation method |
CN102698753B (en) * | 2012-05-15 | 2014-09-24 | 中国科学院过程工程研究所 | Catalyst for mercury oxidation and preparation method and purpose thereof |
CN103285805B (en) * | 2013-06-18 | 2015-09-23 | 广州博能能源科技有限公司 | Mercury removal agent and preparation method thereof |
-
2013
- 2013-06-18 CN CN201310242135.4A patent/CN103285805B/en not_active Expired - Fee Related
- 2013-09-30 WO PCT/CN2013/084801 patent/WO2014201782A1/en active Application Filing
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20050247635A1 (en) * | 2001-08-27 | 2005-11-10 | Vo Toan P | Adsorbents for removing heavy metal cations and methods for producing and using these adsorbents |
CN1748868A (en) * | 2005-08-25 | 2006-03-22 | 上海交通大学 | Process for preparing bromine blended metal oxide catalyst |
CN101844074A (en) * | 2010-05-20 | 2010-09-29 | 宁夏华辉活性炭股份有限公司 | Method for preparing activated carbon used for flue gas demercuration |
Non-Patent Citations (1)
Title |
---|
张续光: "《催化剂制备过程技术》", 30 June 2004, 中国石化出版社 * |
Cited By (23)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2014201782A1 (en) * | 2013-06-18 | 2014-12-24 | 广州博能能源科技有限公司 | Mercury-removing agent and preparation method therefor |
CN104107631A (en) * | 2014-07-30 | 2014-10-22 | 沈阳三聚凯特催化剂有限公司 | Desulfurization and demercuration agent and preparation method thereof |
CN104289232A (en) * | 2014-10-10 | 2015-01-21 | 南京正森环保科技有限公司 | Environment-friendly active carbon catalyst as well as preparation method and application thereof to flue gas mercury removal |
CN105536499A (en) * | 2014-10-28 | 2016-05-04 | 中国石油天然气股份有限公司 | Mercury removing agent, preparation method and applications thereof |
CN105126880A (en) * | 2015-07-24 | 2015-12-09 | 广州博能能源科技有限公司 | Demercuration agent and preparation method thereof |
CN106466590A (en) * | 2015-08-14 | 2017-03-01 | Ada碳解决方案有限责任公司 | The adsorbent composition with amorphous halogen species for pollutant chelating |
CN106466590B (en) * | 2015-08-14 | 2021-03-23 | Ada碳解决方案有限责任公司 | Sorbent compositions with amorphous halogen species for contaminant sequestration |
CN105107362A (en) * | 2015-09-17 | 2015-12-02 | 昆明理工大学 | Method for deep removal of zero valence mercury in mercury smelting flue gas |
CN105688819A (en) * | 2016-04-07 | 2016-06-22 | 安庆师范学院 | Adsorbent for removing elemental mercury from coal gas and preparation method of adsorbent for removing elemental mercury from coal gas |
CN107790152A (en) * | 2017-06-26 | 2018-03-13 | 湖南大学 | It is a kind of to be used to remove catalyst of pernicious gas and its preparation method and application |
WO2019126405A1 (en) * | 2017-12-20 | 2019-06-27 | Uop Llc | Enhancement of reduction resistance for manganese oxide adsorbents |
US20190184369A1 (en) * | 2017-12-20 | 2019-06-20 | Uop Llc | Enhancement of reduction resistance for manganese oxide adsorbents |
US11000821B2 (en) | 2017-12-20 | 2021-05-11 | Uop Llc | Enhancement of reduction resistance for manganese oxide adsorbents |
US11938459B2 (en) | 2017-12-20 | 2024-03-26 | Uop Llc | Enhancement of reduction resistance for manganese oxide adsorbents |
CN110343542A (en) * | 2019-04-23 | 2019-10-18 | 西南石油大学 | A kind of mercury removal agent and preparation method thereof for high mercurous liquid hydrocarbon demercuration |
CN110343542B (en) * | 2019-04-23 | 2020-10-02 | 西南石油大学 | Mercury removing agent for removing mercury from high-mercury-content liquid hydrocarbon and preparation method thereof |
CN111250042A (en) * | 2020-02-18 | 2020-06-09 | 上海电力大学 | Carbon-based adsorbent for demercuration and preparation method and application thereof |
CN111569834A (en) * | 2020-06-01 | 2020-08-25 | 新疆兵团现代绿色氯碱化工工程研究中心(有限公司) | Mercury removing adsorbent for crude chloroethylene gas |
CN112191226A (en) * | 2020-08-31 | 2021-01-08 | 山东大学 | Method for preparing mercury removal adsorbent by modifying low-temperature plasma and application |
CN112337442A (en) * | 2020-10-15 | 2021-02-09 | 华中科技大学 | Modified algae base, preparation thereof and application of modified algae base as mercury removal adsorbent |
CN112756003A (en) * | 2021-01-12 | 2021-05-07 | 武汉科林化工集团有限公司 | Natural gas catalytic oxidation mercury removal agent and preparation method thereof |
CN113171747A (en) * | 2021-06-02 | 2021-07-27 | 山西格盟中美清洁能源研发中心有限公司 | Preparation method of kaolin-based porous material for adsorbing mercury in coal-fired flue gas |
CN113499664A (en) * | 2021-06-28 | 2021-10-15 | 中国神华煤制油化工有限公司 | Mercury removal agent, preparation method thereof and method for removing elemental mercury in flue gas |
Also Published As
Publication number | Publication date |
---|---|
WO2014201782A1 (en) | 2014-12-24 |
CN103285805B (en) | 2015-09-23 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN103285805B (en) | Mercury removal agent and preparation method thereof | |
TWI826408B (en) | A catalyst for catalyzing formaldehyde oxidation and the preparation and use of the same | |
CN102139234B (en) | Loaded reduced precious metal catalyst as well as preparation method and application thereof | |
CN101804325A (en) | Preparation method of modified activated carbon adsorption desulfurizing agent | |
KR100432992B1 (en) | Sorbent compositions for sulfur removal | |
CN104014331B (en) | The preparation method of the Mn-Ce-W composite oxides denitrating catalyst of mesoporous TiO 2 ball load | |
WO2015149499A1 (en) | Low-temperature and highly efficient denitration catalyst and preparation method therefor | |
CN102247746B (en) | Formaldehyde elimination agent and preparation method thereof | |
CN105854577A (en) | Smoke desulfurizer and preparation method thereof | |
CN102806062B (en) | Preparation method of palladium adsorbent for benzene refining desulfurization as well as product and application of palladium adsorbent | |
Liu et al. | Mercury removal from coal combustion flue gas by modified palygorskite adsorbents | |
CN104226240B (en) | Preparation method with catalysis/adsorbing material that kieselguhr is carrier | |
CN104874393A (en) | Preparation method of ozone catalyst | |
CN101322915A (en) | Composite adsorption desulfurizing agent and preparation method thereof | |
CN107126962B (en) | A kind of ammonia nitrogen waste water catalysts for treating and its preparation method and application | |
CN106590728B (en) | One kind is with Cu2O/SiO2-Al2O3The method that composite aerogel removes thiophene sulphur in fuel oil for adsorbent | |
CN104667861B (en) | A kind of sulfur method of the desulfuration adsorbent for gasoline and gasoline | |
CN108479762A (en) | A kind of manganese oxide catalyst and its preparation method and application | |
CN104107631A (en) | Desulfurization and demercuration agent and preparation method thereof | |
CN107413350A (en) | Mischmetal denitrating catalyst and preparation method thereof | |
CN110773224B (en) | Preparation method of alkali metal-resistant denitration catalyst | |
CN106914253B (en) | Active carbon catalyst | |
CN107033946B (en) | One kind is with Cu2O/SiO2-TiO2Composite aerogel is the method that adsorbent removes thiophene sulphur in fuel oil | |
CN105642339A (en) | Catalyst for simultaneous desulfurization and denitration without reducing gas and preparation method | |
CN107597115A (en) | It is a kind of can high-efficient purification high concentration arsenic hydride catalyst and preparation method thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20150923 Termination date: 20200618 |