CN107308946A - It is a kind of for shale ashes desulfurizing agent of flue gas desulfurization and preparation method thereof - Google Patents

It is a kind of for shale ashes desulfurizing agent of flue gas desulfurization and preparation method thereof Download PDF

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Publication number
CN107308946A
CN107308946A CN201710234400.2A CN201710234400A CN107308946A CN 107308946 A CN107308946 A CN 107308946A CN 201710234400 A CN201710234400 A CN 201710234400A CN 107308946 A CN107308946 A CN 107308946A
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shale ashes
desulfurizing agent
shale
ashes
flue gas
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Inventor
建伟伟
于凯
贾冯睿
马丹竹
潘颢丹
刘飞
赵磊
李洲
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Liaoning Shihua University
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Liaoning Shihua University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8603Removing sulfur compounds
    • B01D53/8609Sulfur oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/889Manganese, technetium or rhenium
    • B01J23/8892Manganese
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Treating Waste Gases (AREA)

Abstract

The invention discloses a kind of for shale ashes desulfurizing agent of flue gas desulfurization and preparation method thereof, desulfurizing agent is with KMnO4The shale ashes of processing are carrier, and Fe and Ce using 1 11wt% are prepared from as active component through high-temperature roasting.Its preparation method is:First shale ashes are crushed, sieves and chooses the shale lime-ash of the mesh of particle diameter 20 40;KMnO through 0.4mol/L4Solution impregnates to obtain shale ashes carrier;Shale ashes carrier is placed in 800 DEG C of high-temperature roastings, and the shale ashes carrier after roasting, which is placed in dipping in the ferric nitrate of certain concentration and cerous nitrate mixed solution, adheres to active component;Afterwards in N2Lower 800 DEG C of high-temperature roastings are protected to produce.Activity component impregnation process is 1 11wt% using 50kHz, 100W ultrasonication 0.5 2h, Fe and Ce mass fraction.The shale ashes desulfurizing agent that the present invention is implemented, cost is low, and time of break-through is up to 195min, and sulfur capacity realizes reusing for resource up to 159mg/g desulfurizing agents, is adapted in the popularization and application of flue gas desulfurization technique field.

Description

It is a kind of for shale ashes desulfurizing agent of flue gas desulfurization and preparation method thereof
Technical field
The present invention relates to a kind of for shale ashes desulfurizing agent of flue gas desulfurization and preparation method thereof, belong to flue gas desulfurization technique Field.
Background technology
Currently, continuing to develop with China's industry, energy-output ratio is huge, and energy resource supply is with fossils such as coal, oil , will be using coal as main Energy Mix based on fuel, it is contemplated that following a very long time.But, the burning production of fossil fuel Raw substantial amounts of SO2, NO and NO2Deng pollutant, harm can be brought to the mankind's production and living while pollution environment, therefore, flue gas takes off Extensive concern of the sulphur technology by all circles.At present, flue gas desulfurization technique can be divided into two kinds of wet method and dry method, and wet desulphurization is mainly sharp With alkaline matter such as lime stone and SO2Reaction generation calcium sulfate or calcium sulfite carry out SO2Removing, this method has reaction speed The advantages of rate is fast, desulfuration efficiency is high, but there are high investment cost, seriously corroded and secondary pollution problems;Dry desulfurization skill Art is mainly using the physics or chemisorbed of desulfurizing agent by SO2Removing, desulfurizing agent can carry out regeneration cycle using and have a by-product Thing sulfuric acid, dry desulfurization has the advantages that operating cost is low, equipment corrosion is disposable by people's compared with product after light and desulfurization Extensive concern.
Dry-desulphurizer has molecular sieve, metal oxide (such as iron-based, zinc-base, manganese base metal oxide), activated carbon etc.. As desulfurizing agent, molecular sieve is easily regenerated, and SO can be removed simultaneously2、H2S and organic sulfur compound;But molecular sieve Sulfur capacity is low, quick to steam Sense, the presence of vapor can significantly reduce the desulphurizing activated of molecular sieve.Zinc oxide and iron oxide are industrially conventional metal oxygens Compound desulfurizing agent, zinc oxide desulfurization temperature is general at 200-450 DEG C, with the advantage that desulfuration efficiency is high, Sulfur capacity is big, but can not be again It is raw;By contrast, iron oxide is ambient temperature desulfuration agent, and desulfurization condition is gentle, easily regeneration, but its Sulfur capacity is not high;Activated carbon desulphurization agent Also SO can be removed simultaneously2、H2S and organic sulfur compound, but still suffer from the application limitation that desulfuration efficiency is low, Sulfur capacity is low.
Shale ashes are the products after oil shale retorting, belong to the raw material of the similar volcanic ash containing a small amount of carbon residue, mainly into It is divided into SiO2、Al2O3、Fe2O3, CaO, MgO etc., wherein SiO2、Al2O3Content it is higher, it is given up usually as industrial waste Abandon, on the one hand occupied cultivated land area, and on the other hand surrounding environment is polluted.Research shows that shale ashes contain substantial amounts of acid Property, alkalescence and amphoteric oxide, internal pore structure is flourishing, can be de- for preparing with good absorption and catalytic performance Sulphur agent.The pattern of " treatment of wastes with processes of wastes against one another " is realized in the preparation of shale ashes desulfurizing agent, not only reduces cost, saves raw material, and desulfurization energy Power is strong, the effective way that can be comprehensively utilized as oil shale.Current document, which yet there are no, prepares desulfurizing agent by carrier of shale ashes simultaneously Report for flue gas desulfurization field.
The content of the invention
In order to which the raw material for solving existing desulfurizing agent presence is single, preparing the problems such as cost is high, Sulfur capacity is relatively low, there is provided one kind The cheap easy acquisition of raw material, the shale ashes desulfurizing agent that desulfuration efficiency is high, Sulfur capacity is big and preparation method thereof.The desulfurizing agent that the present invention is provided Have the advantages that with low cost, desulfurization performance is good, can realize resource reutilization.
To achieve these goals, the technical solution adopted by the present invention is:
A kind of shale ashes desulfurizing agent for flue gas desulfurization, with KMnO4The shale ashes of processing are carrier, with 1-11wt%'s Fe and Ce is supported in shale ashes as active component, active component using infusion process, and loading process uses ultrasonication.
Described shale ashes are the lime-ash after oil shale retorting, KMnO4The shale ashes of processing refer to shale ashes using leaching Stain method is through KMnO4Handle 12h, KMnO4Solution concentration is 0.4mol/L.
Described active component loading process uses 50kHz, 100W ultrasonication, and processing time is 0.5-2h.
Present invention also offers a kind of preparation method of shale ashes desulfurizing agent, comprise the following steps:
Step one, the shale ashes for choosing certain mass crush, sieved, and choose shale ashes (SA) conduct of particle diameter 20-40 mesh Desulfurization agent carrier, after being cleaned with deionized water, dries 12h at 110 DEG C;
Step 2, by the KMnO of shale ashes 0.4mol/L described in step one4Solution impregnates 12h, 70 DEG C of heating water bath, leaching Stain process need to continue to stir, and form suspension;
Step 3, suspension described in step 2 is first filtered, then is cleaned several times with deionized water, until the solution after cleaning In neutrality, 12h is then dried at 110 DEG C;
Step 4, by shale ashes described in step 3 under the conditions of 800 DEG C high-temperature roasting 2h, natural cooling, the page after cooling Rock ash, which is marked, is;
Step 5, according to Fe and Ce load capacity, ferric nitrate and cerous nitrate quality required for calculating prepare certain concentration Ferric nitrate and cerous nitrate solution, and the two is mixed to form mixed solution;
Step 6, NSA described in step 4 is placed in the ferric nitrate described in step 5 and cerous nitrate mixed solution, Fe matter Amount fraction is 1-11wt%, and Ce mass fraction is 1-11wt%, and dipping process handles 0.5-2h using ultrasonic oscillation, is formed NSA mixed solutions;
Step 7, NSA mixed solutions described in step 6 are positioned in 70 DEG C of water-baths and heated, and are stirred continuously until liquid It is evaporated, dries 12h at 110 DEG C afterwards;
Step 8, by dried NSA described in step 7 in 800 DEG C, N2The lower high-temperature roasting 4h of protection, roasting process needs N2 Protection is produced.
The shale ashes desulfurizing agent that the present invention is provided is constituted in flue gas:O2Volume fraction 5%, SO2Entrance concentration 2000ppm, Vapor volume fraction 10%, N2It is used as Balance Air, gas flow 400mL/min, quality of activated carbon 2g, bed reaction temperature Under conditions of 120 DEG C, the sulfur capacity of desulfurizing agent may be up to 159mg/g desulfurizing agents, and the time of break-through of desulfurization is up to 195min, desulfurization Agent desulfuration efficiency is high, and sulfur capacity is big, and desulfurizing agent is with low cost, and resource recycling can be achieved.
Brief description of the drawings
Fig. 1 is A classes desulfurizing agent SO provided in an embodiment of the present invention2The breakthrough curve figure of removing.
Fig. 2 is B classes desulfurizing agent SO provided in an embodiment of the present invention2The breakthrough curve figure of removing.
Fig. 3 is C classes desulfurizing agent SO provided in an embodiment of the present invention2The breakthrough curve figure of removing.
Fig. 4 is D classes desulfurizing agent SO provided in an embodiment of the present invention2The breakthrough curve figure of removing.
Fig. 5 is E classes desulfurizing agent SO provided in an embodiment of the present invention2The breakthrough curve figure of removing.
Fig. 6 evaluates the system diagram of Desulfurizer for the present invention.
In figure:1 gas cylinder (SO2, O2, N2);2 pressure-reducing valves;3 needle valves;4 mass flowmenters;5 check valves;6 pressure gauges;7 gas Body mixing chamber;8 steam generators;9 wet flow indicators;10 flue gas analyzers;11 cooling de-watering devices;12 temperature sensors;13 is anti- Answer tower;14 vent gas treatments bottle.
Embodiment
The present invention can adjust active component Fe and Ce load capacity and the time of microwave treatment as needed, so as to be made The shale ashes desulfurizing agent of different performance.
The desulfurization performance for the desulfurizing agent that the present invention is provided is evaluated using Fig. 6 systems provided.Simulated flue gas is from steel cylinder 1 Outflow is finally mixed through pressure-reducing valve 2, mass flowmenter 4 and check valve 5 in gas mixer chamber 7, is produced afterwards with steam generator 8 Vapor mixing through wet flow indicator 9 determine flow and enter reaction tower and activated carbon and react.The gas of reaction tower entrance and exit Body composition is determined by flue gas analyzer 10, it is believed that SO2The time that exit concentration is 100ppm is time of break-through, works as exit concentration When reaching the 95% of entrance concentration, it is believed that absorption reaches saturation.According to import and export SO2Change in concentration can draw SO2Penetrate song Line, sulfur capacity is calculated by breakthrough curve.
Embodiment 1
The shale ashes of 2g particle diameter 20-40 mesh are weighed, are cleaned with deionized water five to eight times, its surface impurity are removed, afterwards 110 DEG C of dry 12h in drying box.Dried shale ashes are added to 0.4mol/L KMnO4In solution, KMnO4Solution is placed in 70 DEG C of heating 12h in water-bath, heating process persistently stirs to form KMnO4The suspension mixed with shale ashes.Suspension is filtered And cleaned with deionized water, until eluate is in neutrality, 110 DEG C of dry 12h in drying box, are placed in Muffle furnace afterwards 800 DEG C of roasting 2h, produce shale ashes carrier.Load capacity according to Fe and Ce calculates the quality of ferric nitrate and cerous nitrate and prepares spy Determine the iron nitrate solution and cerous nitrate solution of concentration, Fe and Ce mass fraction are respectively 1wt% and 2wt%, by what is prepared Ferric nitrate and cerous nitrate solution mixing, and shale ashes carrier is added thereto dipping, dipping process uses 50kHz, and 100W's is super Sound wave aid in treatment, ultrasonic treatment time is 60min.Then the solution after ultrasonication is placed in 70 DEG C of water-baths and heated Until liquid is evaporated, then 110 DEG C of dry 12h in drying box are placed in, most after N2800 DEG C of roastings in Muffle furnace under protective condition 4h, is made desulfurizing agent A1.Desulfurizing agent A1For flue gas desulfurization experiment, it is in flue gas composition:O2Volume fraction 5%, SO2Entrance is dense Spend 2000ppm, vapor volume fraction 10%, N2It is used as Balance Air, gas flow 400mL/min, quality of activated carbon 2g, bed Under conditions of 120 DEG C of reaction temperature, the desulfurization performance of desulfurizing agent is evaluated.The breakthrough curve of desulfurizing agent is shown in Fig. 1, C0/ C tables Show that reaction tower imports and exports SO2The ratio between concentration, desulfurizing agent A1Sulfur capacity be 72.28mg/g desulfurizing agents, time of break-through be 81min (tables 1)。
Embodiment 2-4
Be the same as Example 1, difference is that Ce load capacity is different, and Ce load capacity is 5wt%-11wt% (being shown in Table 1), Each embodiment is made desulfurizing agent and is labeled as A2-A4.The breakthrough curve of desulfurizing agent is shown in Fig. 1, the sulfur capacity and time of break-through of desulfurizing agent It is shown in Table 1.
The Fe and Ce of desulfurizing agent load capacity, sulfur capacity and time of break-through is made in the embodiment 1-4 of table 1.
Embodiment Desulfurizing agent Fe-Ce load capacity Sulfur capacity (mg/g desulfurizing agents) Break through (min)
1 A1 1wt%-2wt% 72.28 81
2 A2 1wt%-5wt% 92.87 108
3 A3 1wt%-8wt% 112.70 134
4 A4 1wt%-11wt% 82.95 95
Embodiment 5-8
Be the same as Example 1, difference is that Fe load capacity is 4wt%, and Ce load capacity (is shown in Table for 2wt%-11wt% 2), each embodiment is made desulfurizing agent and is labeled as B1-B4, and the breakthrough curve of desulfurizing agent is shown in Fig. 2, the sulfur capacity of desulfurizing agent and when penetrating Between be shown in Table 2.
The Fe and Ce of desulfurizing agent load capacity, sulfur capacity and time of break-through is made in the embodiment 5-8 of table 2.
Embodiment Desulfurizing agent Fe-Ce load capacity Sulfur capacity (mg/g desulfurizing agents) Break through (min)
5 B1 4wt%-2wt% 102.78 121
6 B2 4wt%-5wt% 127.95 154
7 B3 4wt%-8wt% 146.25 178
8 B4 4wt%-11wt% 115.75 138
Embodiment 9-12
Be the same as Example 1, difference is that Fe load capacity is 7wt%, and Ce load capacity is 2wt%-11wt% (tables 3), each embodiment is made desulfurizing agent and is labeled as C1-C4, and the breakthrough curve of desulfurizing agent is shown in Fig. 3, the sulfur capacity of desulfurizing agent and when penetrating Between be shown in Table 3.
The Fe and Ce of desulfurizing agent load capacity, sulfur capacity and time of break-through is made in the embodiment 9-12 of table 3.
Embodiment Desulfurizing agent Fe-Ce load capacity Sulfur capacity (mg/g desulfurizing agents) Break through (min)
9 C1 7wt%-2wt% 90.58 105
10 C2 7wt%-5wt% 136.34 165
11 C3 7wt%-8wt% 108.12 128
12 C4 7wt%-11wt% 82.95 95
Embodiment 13-16
Be the same as Example 1, difference is that Fe load capacity is 10wt%, and Ce load capacity is 2wt%-11wt%.
The Fe and Ce of desulfurizing agent load capacity, sulfur capacity and time of break-through is made in the embodiment 13-16 of table 4.
Embodiment Desulfurizing agent Fe-Ce load capacity Sulfur capacity (mg/g desulfurizing agents) Break through (min)
13 D1 10wt%-2wt% 75.33 85
14 D2 10wt%-5wt% 82.19 94
15 D3 10wt%-8wt% 127.19 153
16 D4 10wt%-11wt% 91.34 106
Embodiment 17-20
Be the same as Example 7, difference is that ultrasonic treatment time is different (being shown in Table 5), and desulfurizing agent mark is made in each embodiment E1-E4 is designated as, the sulfur capacity and time of break-through of desulfurizing agent are shown in Table 5.
Ultrasonic treatment time, sulfur capacity and the time of break-through of desulfurizing agent is made in the embodiment 17-20 of table 5.

Claims (5)

1. a kind of shale ashes desulfurizing agent for flue gas desulfurization, it is characterised in that KMnO4The shale ashes of processing are carrier, Fe and Ce As active component, active component is supported in shale ashes using infusion process, and loading process uses 50kHz, 100W ultrasonic wave Processing, processing time is 0.5-2h;Wherein, Fe and Ce is the 1-11wt% of carrier.
2. shale ashes desulfurizing agent according to claim 1, it is characterised in that described KMnO4The shale ashes of processing refer to by Shale ashes are using infusion process through KMnO4Handle 12h, KMnO4Solution concentration is 0.4mol/L.
3. shale ashes desulfurizing agent according to claim 1 or 2, it is characterised in that described shale ashes are oil shale retorting Lime-ash afterwards.
4. a kind of preparation method of shale ashes desulfurizing agent for flue gas desulfurization described in claim 1 or 2 or 3, it is characterised in that Comprise the following steps:
(1) shale ashes are chosen to crush, sieve, it is clear with deionized water using the shale ashes SA of particle diameter 20-40 mesh as desulfurizing agent raw material After washing, 12h is dried at 110 DEG C;
(2) by step (1) shale ashes 0.4mol/L KMnO4Solution impregnates 12h, and 70 DEG C of heating water bath, dipping process is needed Lasting stirring, forms suspension;
(3) step (2) described suspension is first filtered, then cleaned several times with deionized water, until the solution after cleaning is in neutrality, 12h is then dried at 110 DEG C;
(4) by step (3) described shale ashes high-temperature roasting 2h under the conditions of 800 DEG C, natural cooling, the shale ashes mark after cooling For NSA;
(5) according to Fe and Ce load capacity, ferric nitrate and cerous nitrate quality required for calculating prepare the ferric nitrate of certain concentration And cerous nitrate solution, and the two is mixed to form mixed solution;
(6) step (4) described NSA is placed in the ferric nitrate and cerous nitrate mixed solution described in step (5), Fe mass fraction For 1-11wt%, Ce mass fraction is 1-11wt%, and dipping process handles 0.5-2h using ultrasonic oscillation, forms NSA and mixes Close solution;
(7) step (6) the NSA mixed solutions are positioned in 70 DEG C of water-baths and heated, and be stirred continuously until that liquid is evaporated, it 12h is dried at 110 DEG C afterwards;
(8) by step (7) the dried NSA in 800 DEG C, N2The lower high-temperature roasting 4h of protection.
5. a kind of shale ashes desulfurizing agent for flue gas desulfurization is applied in flue gas desulfurization, it is characterised in that described flue gas, its Constitute and be:O2Volume fraction 5%, SO2Entrance concentration 2000ppm, vapor volume fraction 10%, N2It is used as Balance Air, gas stream Measure under conditions of 400mL/min, quality of activated carbon 2g, 120 DEG C of bed reaction temperature, the sulfur capacity of desulfurizing agent may be up to 159mg/ G desulfurizing agents, the time of break-through of desulfurization is up to 195min.
CN201710234400.2A 2017-04-12 2017-04-12 It is a kind of for shale ashes desulfurizing agent of flue gas desulfurization and preparation method thereof Withdrawn CN107308946A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110115921A (en) * 2019-05-27 2019-08-13 沈阳三聚凯特催化剂有限公司 A kind of Fe-series desulfurizing agent and preparation method thereof
CN111044681A (en) * 2019-12-20 2020-04-21 中海油天津化工研究设计院有限公司 Normal-pressure evaluation device and method for liquid desulfurizer
CN111189970A (en) * 2018-11-14 2020-05-22 中国石油化工股份有限公司 Method for detecting absorption and elimination performance of hydrogen sulfide

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4069132A (en) * 1975-11-12 1978-01-17 Union Oil Company Of California Oil shale retorting process with desulfurization of flue gas
CN103432897A (en) * 2013-08-16 2013-12-11 四川大学 Nitrogen-rich porous carbon desulfurizer and preparation method thereof
CN105032389A (en) * 2015-07-24 2015-11-11 四川大学 Mn-Ce bimetal doped activated carbon base desulfurization catalyst and preparation method thereof
CN105107521A (en) * 2015-07-24 2015-12-02 四川大学 Mn-Fe double metal-doped active carbon-based desulfurization catalyst, and preparation method thereof
CN106423113A (en) * 2016-11-18 2017-02-22 黑龙江省能源环境研究院 Preparation method of modified oil shale semicoke adsorbent

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4069132A (en) * 1975-11-12 1978-01-17 Union Oil Company Of California Oil shale retorting process with desulfurization of flue gas
CN103432897A (en) * 2013-08-16 2013-12-11 四川大学 Nitrogen-rich porous carbon desulfurizer and preparation method thereof
CN105032389A (en) * 2015-07-24 2015-11-11 四川大学 Mn-Ce bimetal doped activated carbon base desulfurization catalyst and preparation method thereof
CN105107521A (en) * 2015-07-24 2015-12-02 四川大学 Mn-Fe double metal-doped active carbon-based desulfurization catalyst, and preparation method thereof
CN106423113A (en) * 2016-11-18 2017-02-22 黑龙江省能源环境研究院 Preparation method of modified oil shale semicoke adsorbent

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
谭志嘉: ""油页岩灰渣脱除硫化氢的研究"", 《中国优秀硕士学位论文全文数据库 工程科技Ⅰ辑 (月刊) 》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111189970A (en) * 2018-11-14 2020-05-22 中国石油化工股份有限公司 Method for detecting absorption and elimination performance of hydrogen sulfide
CN110115921A (en) * 2019-05-27 2019-08-13 沈阳三聚凯特催化剂有限公司 A kind of Fe-series desulfurizing agent and preparation method thereof
CN111044681A (en) * 2019-12-20 2020-04-21 中海油天津化工研究设计院有限公司 Normal-pressure evaluation device and method for liquid desulfurizer

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