CN103908886A - Method for desulphurizing by zinc oxide slurry containing novel additive - Google Patents
Method for desulphurizing by zinc oxide slurry containing novel additive Download PDFInfo
- Publication number
- CN103908886A CN103908886A CN201410134961.1A CN201410134961A CN103908886A CN 103908886 A CN103908886 A CN 103908886A CN 201410134961 A CN201410134961 A CN 201410134961A CN 103908886 A CN103908886 A CN 103908886A
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- CN
- China
- Prior art keywords
- zinc oxide
- slurries
- oxide slurries
- sulfur dioxide
- absorption tower
- 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.)
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- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 title claims abstract description 197
- 239000000654 additive Substances 0.000 title claims abstract description 42
- 230000000996 additive effect Effects 0.000 title claims abstract description 42
- 238000000034 method Methods 0.000 title claims abstract description 33
- 239000002002 slurry Substances 0.000 claims abstract description 109
- 239000011787 zinc oxide Substances 0.000 claims abstract description 94
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 claims abstract description 64
- 239000004094 surface-active agent Substances 0.000 claims abstract description 15
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 7
- 238000010521 absorption reaction Methods 0.000 claims description 44
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 claims description 16
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 15
- GSEJCLTVZPLZKY-UHFFFAOYSA-N Triethanolamine Chemical compound OCCN(CCO)CCO GSEJCLTVZPLZKY-UHFFFAOYSA-N 0.000 claims description 14
- 239000011593 sulfur Substances 0.000 claims description 14
- 229910052717 sulfur Inorganic materials 0.000 claims description 14
- 239000003795 chemical substances by application Substances 0.000 claims description 13
- 150000003839 salts Chemical class 0.000 claims description 13
- 239000007921 spray Substances 0.000 claims description 12
- 229940058020 2-amino-2-methyl-1-propanol Drugs 0.000 claims description 11
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 claims description 11
- CBTVGIZVANVGBH-UHFFFAOYSA-N aminomethyl propanol Chemical compound CC(C)(N)CO CBTVGIZVANVGBH-UHFFFAOYSA-N 0.000 claims description 11
- 229920002538 Polyethylene Glycol 20000 Polymers 0.000 claims description 8
- 239000011780 sodium chloride Substances 0.000 claims description 8
- 239000013589 supplement Substances 0.000 claims description 6
- 239000001110 calcium chloride Substances 0.000 claims description 5
- 229910001628 calcium chloride Inorganic materials 0.000 claims description 5
- 239000000203 mixture Substances 0.000 claims description 5
- 235000010482 polyoxyethylene sorbitan monooleate Nutrition 0.000 claims description 5
- 229920000053 polysorbate 80 Polymers 0.000 claims description 5
- 229940052228 zinc oxide paste Drugs 0.000 claims description 4
- 230000000694 effects Effects 0.000 abstract description 4
- 238000002156 mixing Methods 0.000 abstract description 4
- 229910017053 inorganic salt Inorganic materials 0.000 abstract 2
- 238000007599 discharging Methods 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 23
- 239000003546 flue gas Substances 0.000 description 17
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 13
- 239000011701 zinc Substances 0.000 description 13
- 229910052725 zinc Inorganic materials 0.000 description 13
- 238000006477 desulfuration reaction Methods 0.000 description 12
- 230000023556 desulfurization Effects 0.000 description 12
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 9
- 238000005516 engineering process Methods 0.000 description 8
- NWONKYPBYAMBJT-UHFFFAOYSA-L zinc sulfate Chemical compound [Zn+2].[O-]S([O-])(=O)=O NWONKYPBYAMBJT-UHFFFAOYSA-L 0.000 description 6
- 229960001763 zinc sulfate Drugs 0.000 description 6
- 229910000368 zinc sulfate Inorganic materials 0.000 description 6
- 239000007787 solid Substances 0.000 description 5
- 239000002699 waste material Chemical group 0.000 description 4
- 230000002745 absorbent Effects 0.000 description 3
- 239000002250 absorbent Substances 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- HSYFJDYGOJKZCL-UHFFFAOYSA-L zinc;sulfite Chemical group [Zn+2].[O-]S([O-])=O HSYFJDYGOJKZCL-UHFFFAOYSA-L 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- 238000003723 Smelting Methods 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 239000003792 electrolyte Substances 0.000 description 2
- 239000003500 flue dust Chemical group 0.000 description 2
- 239000012530 fluid Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 235000019738 Limestone Nutrition 0.000 description 1
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 1
- 239000005864 Sulphur Substances 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 239000012298 atmosphere Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 238000010310 metallurgical process Methods 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 238000005979 thermal decomposition reaction Methods 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Gas Separation By Absorption (AREA)
Abstract
The invention relates to a method for desulphurizing by zinc oxide slurry containing an additive formed by mixing alkanolamine, an inorganic salt and a surfactant. The method comprises the following steps: firstly, mixing water and zinc oxide to form zinc oxide slurry; then mixing the alkanolamine, the inorganic salt and the surfactant to form the zinc oxide slurry additive; adding the additive into the zinc oxide slurry to prepare the zinc oxide slurry containing the novel additive, and placing the slurry in a slurry circulating pond; introducing a to-be-treated gas containing sulfur dioxide into a booster fan for pressurizing; and introducing the pressurized gas into an absorbing tower bottom layer, making the pressurized gas react with the zinc oxide slurry downwards sprayed from an absorbing tower top to absorb sulfur dioxide, discharging the gas without the sulfur dioxide out from the absorbing tower top, and returning the zinc oxide slurry containing the sulfur dioxide to the slurry circulating pond. The method provided by the invention is simple, is low in cost, has a good effect of absorbing sulfur dioxide, ensures low viscosity of the zinc oxide slurry, is free from pollution, and can save resources and increase economic benefits.
Description
Technical field
The invention belongs to environmental technology field, be specifically related to the zinc oxide slurries sulfur method that a kind of employing contains the additive being mixed into by alkanolamine, inorganic salts and surfactant.
Background technology
Sulfur dioxide, as one of main gas of atmosphere pollution, has caused people's extensive concern.Flue gas desulfurization is the effective ways that reduce sulphur emissions, the countries in the world desulfur technology that begins one's study from the 1950's, so far desulfur technology has reached kind more than 200, and main method has the multiple sulfur removal technologies such as wet desulphurization, semi-dry desulphurization, dry desulfurization, the desulfurization of rotary spraying and drying method, E-beam absorption.Use at present more generally limestone/lime method, soda method, renewable solvent absorption cycle and ammonia process both at home and abroad.
But for Lead And Zinc Smelter, these methods exist that raw material sources are difficult for, byproduct is disposed difficulty or processing cost and crossed the problems such as high.
Zinc oxide method is a kind of sulfur method for zinc smeltery flue gas, flue dust, waste residue and waste electrolyte that its raw material oxide powder and zinc can utilize zinc metallurgical process to produce make, for absorbing the sulfur dioxide gas of flue gas, generating product is zinc sulfite solid, zinc sulfate liquid or zinc sulfate solid.Zinc sulfite solid can be decomposed into zinc oxide and sulfur dioxide by adding thermal decomposition or acid, and zinc oxide returns and makees absorbent, and sulfur dioxide can be produced sulfuric acid or sulfur dioxide liquid processed; Also can zinc sulfite be oxidized to soluble zinc sulfate by oxidizing process, zinc sulfate liquid or the zinc sulfate solid obtaining by evaporative crystallization all can return to smelting shop and re-use.As can be seen here, this technology is combined closely sulfur removal technology and original smelting process, absorbent adopts the flue dust containing zinc oxide in factory, waste residue and waste electrolyte, the solution of zinc sulfate producing, solid slags etc. all can return to relevant workshop in factory and again utilize, the source of absorbent and the processing problem of product are well solved, reach the maximization of the utilization of resources, reduce circulating fund, reduce operating cost, but in actual application, find that the method exists assimilation effect poor, zinc oxide paste fluid viscosity is large, the problems such as easy obstruction, not only absorb and not exclusively can continue to cause environmental pollution, also can affect normal production simultaneously.
Summary of the invention
For solving the problems of the technologies described above, the invention provides that a kind of employing contains that the additive, the viscosity that are mixed into by alkanolamine, inorganic salts and surfactant are low, good absorbing effect, be not easy the zinc oxide slurries sulfur method that stops up, energy consumption is little, cost is low.
For achieving the above object, the technical solution used in the present invention is:
The zinc oxide slurries sulfur method that employing contains new additive agent, comprises the following steps:
(1) water, zinc oxide are mixed and made into zinc oxide slurries;
(2) alkanolamine, inorganic salts and surfactant are mixed into zinc oxide paste solution additive;
(3) additive of step (2) gained is added in the zinc oxide slurries of step (1) and make the zinc oxide slurries that contain new additive agent, and it is for subsequent use that the zinc oxide slurries that contain new additive agent are put into slurries circulatory pool;
(4) the pending gas that contains sulfur dioxide is passed into booster fan, compressor flow mates with gas flow, more than blast reaches 5000Pa;
(5) the pending gas after pressurization enters the bottom on the absorption tower of three layers of sieve plate, from bottom to top in flow process with squeeze into from slurries circulatory pool top, Bing Cong absorption tower, top, absorption tower downwards the zinc oxide slurries of spray react and absorb the sulfur dioxide pending gas, regulate the pH value of the zinc oxide slurries that spray in absorption tower by supplement a certain amount of zinc oxide slurries in slurries simultaneously, the pH value that makes zinc oxide slurries in absorption tower is 2.2-5.2, the gas of sloughing after sulfur dioxide is discharged by top, absorption tower, zinc oxide slurries after sulfur dioxide absorption return to slurries circulatory pool.
In described step (1), in zinc oxide slurries, the weight percentage of zinc oxide is 35%-75%.
In described step (2), the part by weight of alkanolamine, inorganic salts, surfactant is (1-2): (0.2-0.5): (0.5-1.5).
Described alkanolamine is one or both combination of triethanolamine or 2-amino-2-methyl-1-propanol.
Described inorganic salts are one or both combination of calcium chloride or sodium chloride.
Described surfactant is one or more the combination in neopelex, Tween 80, PEG 20000.
The weight of the mixture being made up of alkanolamine, inorganic salts and surfactant adding in zinc oxide slurries in described step (3) accounts for the 0.05%-0.5% of zinc oxide slurries gross weight.
Adopt after technique scheme, the beneficial effect that the present invention reaches is:
(1) alkanolamine of the present invention, inorganic salts and surfactant add to after mixing has increased contacting of flue gas and zinc oxide slurries in zinc oxide slurries, the oxidized zinc slurries of sulfur dioxide in flue gas are fully absorbed, thereby reach the object of thorough desulfurization;
(2) the present invention has reduced the viscosity of zinc oxide slurries by add the additive being made up of alkanolamine, inorganic salts and surfactant in zinc oxide slurries, has reduced sedimentation, has significantly improved zinc oxide slurries and has flowed, and has avoided the phenomenons such as obstruction.
Therefore, the inventive method is simple, pollution-free, cost is low, and the zinc oxide slurries that simultaneously contain the additive being made up of alkanolamine, inorganic salts and surfactant can significantly improve the assimilation effect of sulfur dioxide, reduces zinc oxide paste fluid viscosity, avoid the obstruction in production process, further reduce pollution, saved resource, improved economic benefit.
The specific embodiment
The invention will be further described by the following examples, its objective is in order to understand better content of the present invention, but it does not limit the scope of the invention.
embodiment 1
(1) first water and zinc oxide are mixed and made into zinc oxide slurries by weight the ratio that is 1:1;
(2) triethanolamine (TEA), sodium chloride (NaCl), Tween 80 are mixed and made into additive in the ratio of 1.2:0.4:0.5;
(3) additive of being made up of triethanolamine (TEA), sodium chloride (NaCl), Tween 80 is added and in zinc oxide slurries, made the flue gas desulfurization zinc oxide slurries that contain the additive being made up of triethanolamine (TEA), sodium chloride (NaCl), Tween 80 in 0.2% ratio of zinc oxide slurries gross weight, and the zinc oxide slurries containing additive are put into slurries circulatory pool;
(4) zinc smeltery is contained to SO
2concentration is 12000 mg/m
3flue gas pass into booster fan, compressor flow mates with gas flow, more than blast reaches 5000Pa;
(5) the zinc smeltery after pressurization is containing SO
2concentration is 12000 mg/m
3flue gas enter the bottom on the absorption tower of three layers of sieve plate, from bottom to top in flow process with squeeze into from slurries circulatory pool top, Bing Cong absorption tower, top, absorption tower downwards the zinc oxide slurries of spray react and absorb the sulfur dioxide pending gas, regulate the pH value of the zinc oxide slurries that spray in absorption tower by supplement a certain amount of zinc oxide slurries in slurries circulatory pool simultaneously, the pH value that makes zinc oxide slurries in absorption tower is 2.2, the gas of sloughing after sulfur dioxide is discharged by top, absorption tower, after testing, SO in the gas after desulfurization
2content is 450 mg/m
3, the zinc oxide slurries after sulfur dioxide absorption return to slurries circulatory pool.
Embodiment 2
(1) first water and zinc oxide are mixed and made into zinc oxide slurries by weight the ratio that is 1:0.54;
(2) by triethanolamine (TEA), calcium chloride (CaCl
2), PEG 20000 is in 2:0:5: 1.5 ratio is mixed and made into additive;
(3) will be by triethanolamine (TEA), calcium chloride (CaCl
2), the additive made of PEG 20000 adds in zinc oxide slurries and makes and contain by triethanolamine (TEA), calcium chloride (CaCl in 0.05% ratio of zinc oxide slurries gross weight
2), the flue gas desulfurization zinc oxide slurries of the additive of PEG 20000 composition, and the zinc oxide slurries that contain additive are put into slurries circulatory pool;
(4) zinc smeltery is contained to SO
2concentration is 10000 mg/m
3flue gas pass into booster fan, compressor flow mates with gas flow, more than blast reaches 5000Pa;
(5) the zinc smeltery after pressurization is containing SO
2concentration is 10000 mg/m
3flue gas enter the bottom on the absorption tower of three layers of sieve plate, from bottom to top in flow process with squeeze into from slurries circulatory pool top, Bing Cong absorption tower, top, absorption tower downwards the zinc oxide slurries of spray react and absorb the sulfur dioxide pending gas, regulate the pH value of the zinc oxide slurries that spray in absorption tower by supplement a certain amount of zinc oxide slurries in slurries circulatory pool simultaneously, the pH value that makes zinc oxide slurries in absorption tower is 3.5, the gas of sloughing after sulfur dioxide is discharged by top, absorption tower, after testing, SO in the gas after desulfurization
2content is 200 mg/m
3, the zinc oxide slurries after sulfur dioxide absorption return to slurries circulatory pool.
embodiment 3
(1) first water and zinc oxide are mixed and made into zinc oxide slurries by weight the ratio that is 1:3;
(2) by 2-amino-2-methyl-1-propanol, calcium chloride (CaCl
2), neopelex is mixed and made into additive in the ratio of 1:0.2:0.5;
(3) by 2-amino-2-methyl-1-propanol, calcium chloride (CaCl
2), the additive made of neopelex adds in zinc oxide slurries and makes and contain by 2-amino-2-methyl-1-propanol, calcium chloride (CaCl in 0.5% ratio of zinc oxide slurries gross weight
2), the flue gas desulfurization zinc oxide slurries of the additive of neopelex composition, and the zinc oxide slurries that contain additive are put into slurries circulatory pool;
(4) zinc smeltery is contained to SO
2concentration is 15000 mg/m
3flue gas pass into booster fan, compressor flow mates with gas flow, more than blast reaches 5000Pa;
(5) the zinc smeltery after pressurization is containing SO
2concentration is 15000 mg/m
3flue gas enter the bottom on the absorption tower of three layers of sieve plate, from bottom to top in flow process with squeeze into from slurries circulatory pool top, Bing Cong absorption tower, top, absorption tower downwards the zinc oxide slurries of spray react and absorb the sulfur dioxide pending gas, regulate the pH value of the zinc oxide slurries that spray in absorption tower by supplement a certain amount of zinc oxide slurries in slurries circulatory pool simultaneously, the pH value that makes zinc oxide slurries in absorption tower is 4.5, the gas of sloughing after sulfur dioxide is discharged by top, absorption tower, after testing, SO in the gas after desulfurization
2content is 190mg/m
3, the zinc oxide slurries after sulfur dioxide absorption return to slurries circulatory pool.
embodiment 4
(1) first water and zinc oxide are mixed and made into zinc oxide slurries by weight the ratio that is 1:2;
(2) by 2-amino-2-methyl-1-propanol (AMP), calcium chloride (CaCl
2), PEG 20000 is mixed and made into additive in the ratio of 2:0.3:1.2;
(3) by 2-amino-2-methyl-1-propanol (AMP), calcium chloride (CaCl
2), the additive made of PEG 20000 adds in zinc oxide slurries and makes and contain by 2-amino-2-methyl-1-propanol (AMP), calcium chloride (CaCl in 0.3% ratio of zinc oxide slurries gross weight
2), the flue gas desulfurization zinc oxide slurries of the additive of PEG 20000 composition, and the zinc oxide slurries that contain additive are put into slurries circulatory pool;
(4) zinc smeltery is contained to SO
2concentration is 12000 mg/m
3flue gas pass into booster fan, compressor flow mates with gas flow, more than blast reaches 5000Pa;
(5) the zinc smeltery after pressurization is containing SO
2concentration is 12000 mg/m
3flue gas enter the bottom on the absorption tower of three layers of sieve plate, from bottom to top in flow process with squeeze into from slurries circulatory pool top, Bing Cong absorption tower, top, absorption tower downwards the zinc oxide slurries of spray react and absorb the sulfur dioxide pending gas, regulate the pH value of the zinc oxide slurries that spray in absorption tower by supplement a certain amount of zinc oxide slurries in slurries circulatory pool simultaneously, the pH value that makes zinc oxide slurries in absorption tower is 5.2, the gas of sloughing after sulfur dioxide is discharged by top, absorption tower, after testing, SO in the gas after desulfurization
2content is 180mg/m
3, the zinc oxide slurries after sulfur dioxide absorption return to slurries circulatory pool.
Claims (7)
1. the zinc oxide slurries sulfur method that employing contains new additive agent, comprises the following steps:
(1) water, zinc oxide are mixed and made into zinc oxide slurries;
(2) alkanolamine, inorganic salts and surfactant are mixed into zinc oxide paste solution additive;
(3) additive of step (2) gained is added in the zinc oxide slurries of step (1) and make the zinc oxide slurries that contain new additive agent, and it is for subsequent use that the zinc oxide slurries that contain new additive agent are put into slurries circulatory pool;
(4) the pending gas that contains sulfur dioxide is passed into booster fan, compressor flow mates with gas flow, more than blast reaches 5000Pa;
(5) the pending gas after pressurization enters the bottom on the absorption tower of three layers of sieve plate, from bottom to top in flow process with squeeze into from slurries circulatory pool top, Bing Cong absorption tower, top, absorption tower downwards the zinc oxide slurries of spray react and absorb the sulfur dioxide pending gas, regulate the pH value of the zinc oxide slurries that spray in absorption tower by supplement a certain amount of zinc oxide slurries in slurries simultaneously, the pH value that makes zinc oxide slurries in absorption tower is 2.2-5.2, the gas of sloughing after sulfur dioxide is discharged by top, absorption tower, zinc oxide slurries after sulfur dioxide absorption return to slurries circulatory pool.
2. the zinc oxide slurries sulfur method that a kind of employing according to claim 1 contains new additive agent, is characterized in that: in described step (1), in zinc oxide slurries, the weight percentage of zinc oxide is 35%-75%.
3. the zinc oxide slurries sulfur method that a kind of employing according to claim 1 contains new additive agent, is characterized in that: in described step (2), the part by weight of alkanolamine, inorganic salts, surfactant is (1-2): (0.2-0.5): (0.5-1.5).
4. the zinc oxide slurries sulfur method that a kind of employing according to claim 1 contains new additive agent, is characterized in that: described alkanolamine is one or both combination of triethanolamine or 2-amino-2-methyl-1-propanol.
5. the zinc oxide slurries sulfur method that a kind of employing according to claim 1 contains new additive agent, is characterized in that: described inorganic salts are one or both combination of calcium chloride or sodium chloride.
6. the zinc oxide slurries sulfur method that a kind of employing according to claim 1 contains new additive agent, is characterized in that: described surfactant is one or more the combination in neopelex, Tween 80, PEG 20000.
7. the zinc oxide slurries sulfur method that a kind of employing according to claim 1 contains new additive agent, is characterized in that: the weight of the mixture being made up of alkanolamine, inorganic salts and surfactant adding in zinc oxide slurries in described step (3) accounts for the 0.05%-0.5% of zinc oxide slurries gross weight.
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
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CN104174281A (en) * | 2014-08-26 | 2014-12-03 | 山东瑞爱特环保科技有限公司 | Flue gas desulfurization synergistic agent and preparation method thereof |
CN110559818A (en) * | 2019-09-27 | 2019-12-13 | 广东金宇环境科技有限公司 | Flue gas desulfurization method using secondary zinc oxide soot as desulfurizer |
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CN102755826A (en) * | 2012-07-06 | 2012-10-31 | 江苏恒丰伟业科技工程有限公司 | Tail gas desulfuration adopting zinc oxide method in smelting industry |
CN103316576A (en) * | 2013-05-14 | 2013-09-25 | 宜兴市化工成套设备有限公司 | Desulfurizing and demisting combined tower |
CN103349901A (en) * | 2013-06-14 | 2013-10-16 | 中国恩菲工程技术有限公司 | Flue gas processing method and device thereof |
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US6080281A (en) * | 1994-04-18 | 2000-06-27 | Attia; Yosry A. | Scrubbing of contaminants from contaminated air streams with aerogel materials with optional photocatalytic destruction |
CN1531991A (en) * | 2003-03-18 | 2004-09-29 | 于文波 | Sulfur dioxide removing agent |
CN102755826A (en) * | 2012-07-06 | 2012-10-31 | 江苏恒丰伟业科技工程有限公司 | Tail gas desulfuration adopting zinc oxide method in smelting industry |
CN103316576A (en) * | 2013-05-14 | 2013-09-25 | 宜兴市化工成套设备有限公司 | Desulfurizing and demisting combined tower |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
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CN104174281A (en) * | 2014-08-26 | 2014-12-03 | 山东瑞爱特环保科技有限公司 | Flue gas desulfurization synergistic agent and preparation method thereof |
CN110559818A (en) * | 2019-09-27 | 2019-12-13 | 广东金宇环境科技有限公司 | Flue gas desulfurization method using secondary zinc oxide soot as desulfurizer |
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CN103908886B (en) | 2016-08-31 |
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