CN1631493A - A wet flue gas desulfurization method and device thereof - Google Patents
A wet flue gas desulfurization method and device thereof Download PDFInfo
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- 238000006477 desulfuration reaction Methods 0.000 title claims description 117
- 230000023556 desulfurization Effects 0.000 title claims description 117
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims description 85
- 239000003546 flue gas Substances 0.000 title claims description 83
- 238000000034 method Methods 0.000 title claims description 29
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 79
- 239000007788 liquid Substances 0.000 claims abstract description 56
- 239000003245 coal Substances 0.000 claims abstract description 12
- 239000002253 acid Substances 0.000 claims abstract description 10
- 239000000126 substance Substances 0.000 claims description 51
- 238000004090 dissolution Methods 0.000 claims description 39
- 239000010797 grey water Substances 0.000 claims description 38
- 239000000428 dust Substances 0.000 claims description 33
- 239000002893 slag Substances 0.000 claims description 24
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 claims description 18
- 230000018044 dehydration Effects 0.000 claims description 14
- 238000006297 dehydration reaction Methods 0.000 claims description 14
- 238000001914 filtration Methods 0.000 claims description 11
- 239000010865 sewage Substances 0.000 claims description 11
- 230000002378 acidificating effect Effects 0.000 claims description 8
- 239000010419 fine particle Substances 0.000 claims description 7
- 238000005406 washing Methods 0.000 claims description 7
- 238000011010 flushing procedure Methods 0.000 claims description 6
- 239000002002 slurry Substances 0.000 claims description 6
- 238000000926 separation method Methods 0.000 claims description 5
- 238000002485 combustion reaction Methods 0.000 claims description 4
- 239000000203 mixture Substances 0.000 claims description 4
- 239000003344 environmental pollutant Substances 0.000 claims description 3
- 238000002156 mixing Methods 0.000 claims description 3
- 231100000719 pollutant Toxicity 0.000 claims description 3
- 239000007787 solid Substances 0.000 claims description 2
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 abstract description 7
- 239000000779 smoke Substances 0.000 abstract description 6
- 238000004064 recycling Methods 0.000 abstract description 4
- 239000003595 mist Substances 0.000 abstract description 3
- 239000005864 Sulphur Substances 0.000 abstract 6
- 238000006243 chemical reaction Methods 0.000 abstract 1
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 239000002699 waste material Substances 0.000 description 6
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 4
- 239000006227 byproduct Substances 0.000 description 4
- 239000011575 calcium Substances 0.000 description 4
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 3
- 239000003513 alkali Substances 0.000 description 3
- 229910052791 calcium Inorganic materials 0.000 description 3
- 239000003795 chemical substances by application Substances 0.000 description 3
- 150000001875 compounds Chemical class 0.000 description 3
- 238000010438 heat treatment Methods 0.000 description 3
- 239000011777 magnesium Substances 0.000 description 3
- 239000004570 mortar (masonry) Substances 0.000 description 3
- 229910001415 sodium ion Inorganic materials 0.000 description 3
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- 235000019738 Limestone Nutrition 0.000 description 2
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 2
- UIIMBOGNXHQVGW-UHFFFAOYSA-M Sodium bicarbonate Chemical compound [Na+].OC([O-])=O UIIMBOGNXHQVGW-UHFFFAOYSA-M 0.000 description 2
- FKNQFGJONOIPTF-UHFFFAOYSA-N Sodium cation Chemical group [Na+] FKNQFGJONOIPTF-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 2
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 2
- 238000013019 agitation Methods 0.000 description 2
- 230000009977 dual effect Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005342 ion exchange Methods 0.000 description 2
- 239000006028 limestone Substances 0.000 description 2
- 229910052749 magnesium Inorganic materials 0.000 description 2
- 239000000395 magnesium oxide Substances 0.000 description 2
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 2
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 235000017550 sodium carbonate Nutrition 0.000 description 2
- 229910000029 sodium carbonate Inorganic materials 0.000 description 2
- 235000011121 sodium hydroxide Nutrition 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 1
- 239000000809 air pollutant Substances 0.000 description 1
- 231100001243 air pollutant Toxicity 0.000 description 1
- 229910001038 basic metal oxide Inorganic materials 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 229940043430 calcium compound Drugs 0.000 description 1
- 159000000007 calcium salts Chemical class 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 230000003009 desulfurizing effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 150000002681 magnesium compounds Chemical class 0.000 description 1
- 159000000003 magnesium salts Chemical class 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 1
- CHWRSCGUEQEHOH-UHFFFAOYSA-N potassium oxide Chemical compound [O-2].[K+].[K+] CHWRSCGUEQEHOH-UHFFFAOYSA-N 0.000 description 1
- 229910001950 potassium oxide Inorganic materials 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 235000017557 sodium bicarbonate Nutrition 0.000 description 1
- 229910000030 sodium bicarbonate Inorganic materials 0.000 description 1
- KKCBUQHMOMHUOY-UHFFFAOYSA-N sodium oxide Chemical compound [O-2].[Na+].[Na+] KKCBUQHMOMHUOY-UHFFFAOYSA-N 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
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Abstract
Description
技术领域:Technical field:
本发明涉及一种适用于大中型燃煤工业锅炉的烟气脱硫技术领域,特别涉及大中型燃煤工业锅炉以废治废的湿式烟气脱硫方法及装置。The invention relates to the technical field of flue gas desulfurization applicable to large and medium-sized coal-fired industrial boilers, in particular to a wet-type flue gas desulfurization method and device for large and medium-sized coal-fired industrial boilers.
背景技术:Background technique:
众所周知,脱除燃煤烟气中二氧化硫的方法有多种,包括石灰石/石灰—石膏法、双碱法、烟气循环硫化床法等烟气脱硫技术,在这些方法中均需要将石灰石(CaCO3)、石灰(CaO)、烧碱(NaOH)等脱硫剂制备成脱硫液,注入脱硫反应器与烟气中的二氧化硫发生反应,生成亚硫酸盐和硫酸盐,并予以去除。为此,这些方法均需要在脱硫工艺系统中设置一套脱硫剂的制备、储存、输送和脱硫剂副产物的收集、去除装置,使全套脱硫系统庞大、配套设备众多,加之需购置脱硫剂,造成系统设备投资和运行费用增大。As we all know, there are many ways to remove sulfur dioxide in coal-fired flue gas, including limestone/lime-gypsum method, double alkali method, flue gas circulating fluidized bed method and other flue gas desulfurization technologies. In these methods, limestone (CaCO 3 ), lime (CaO), caustic soda (NaOH) and other desulfurization agents are prepared into desulfurization liquid, which is injected into the desulfurization reactor to react with sulfur dioxide in the flue gas to generate sulfite and sulfate and remove them. For this reason, these methods all need to set up a set of desulfurization agent preparation, storage, transportation, and desulfurization by-product collection and removal devices in the desulfurization process system, so that the complete desulfurization system is huge and there are many supporting equipment. In addition, desulfurization agents need to be purchased. Cause system equipment investment and operating costs to increase.
发明内容:Invention content:
本发明的目的在于提供一种利用燃煤锅炉自身排放的碱性废物作为脱硫剂,以去除燃煤烟气中携带的二氧化硫的湿式烟气脱硫方法及其装置,该方法气液传质性强,脱硫液循环利用,用水量小,适用范围广、投资和运行费用低、在脱硫的同时还可以除去细微烟尘。The purpose of the present invention is to provide a wet flue gas desulfurization method and its device which use the alkaline waste discharged by the coal-fired boiler itself as a desulfurizer to remove sulfur dioxide carried in the coal-fired flue gas, and the method has strong gas-liquid mass transfer , Desulfurization liquid recycling, small water consumption, wide application range, low investment and operating costs, while desulfurization can also remove fine dust.
为达到上述目的,本发明所采用的技术方案是:一种湿式烟气脱硫方法:In order to achieve the above object, the technical solution adopted in the present invention is: a wet flue gas desulfurization method:
1)溶出煤渣中的碱性物质,并形成冲渣水的循环:冲渣水从碱性物质溶出池的后部经冲渣泵引出,使锅炉内煤炭燃烧后生成的灰渣随冲渣水一起流入碱性物质溶出池,与湿式烟气脱硫除尘器排出的酸性灰水混合汇合,在酸性灰水和水力搅拌的双重作用下,将灰渣中的碱性物质逐渐溶出,同时,形成冲渣水的循环;1) Dissolve the alkaline substances in the coal slag and form a cycle of slag flushing water: the slag flushing water is drawn from the rear of the alkaline substance dissolution tank through the slag flushing pump, so that the ash generated after the coal combustion in the boiler is washed with the slag flushing water Together, they flow into the dissolution tank of alkaline substances, and mix and merge with the acid gray water discharged from the wet flue gas desulfurization dust collector. circulation of slag water;
2)一次过滤:上述灰渣水与酸性灰水混合液经过滤后,流入集水池;2) Primary filtration: the above-mentioned mixture of ash water and acidic ash water flows into the sump after being filtered;
3)混合:上述溶液在集水池中与锅炉排出的碱性排污水汇合;3) Mixing: the above solution merges with the alkaline sewage discharged from the boiler in the sump;
4)二次过滤:汇合后的溶液,经过滤进一步滤除细小颗粒后流入脱硫液池,形成脱硫液;4) Secondary filtration: the combined solution flows into the desulfurization liquid pool after filtering to further filter out fine particles to form a desulfurization liquid;
5)烟气脱硫:上述的脱硫液进入湿式烟气脱硫除尘器,与进入该装置内的燃煤锅炉排出的烟气发生化学反应,脱除二氧化硫污染物;5) Flue gas desulfurization: the above-mentioned desulfurization liquid enters the wet type flue gas desulfurization dust collector, and chemically reacts with the flue gas discharged from the coal-fired boiler entering the device to remove sulfur dioxide pollutants;
6)脱硫液循环:上述脱硫液使烟气脱硫后,产生的酸性灰水,流入碱性物质溶出池的前端,形成脱硫液循环;6) Desulfurization liquid circulation: After the above-mentioned desulfurization liquid desulfurizes the flue gas, the acid gray water produced flows into the front end of the alkaline substance dissolution tank to form a desulfurization liquid circulation;
7)烟气脱水除雾:脱硫后的烟气经脱水除雾器脱水除雾后,排入大气;7) Flue gas dehydration and defogging: the desulfurized flue gas is dehydrated and defogged by the demister demister, and then discharged into the atmosphere;
8)定时灰水分离:定时将集水池中溶液注入灰水分离器,分离后的水从灰水分离器顶部出水管排出,重新使用;浆液从泥浆斗流入碱性物质溶出池,同时系统补充适量清水,形成外排水的循环;8) Timing gray water separation: regularly inject the solution in the sump into the gray water separator, and the separated water is discharged from the outlet pipe at the top of the gray water separator for reuse; the slurry flows from the mud hopper into the alkaline substance dissolution tank, and the system supplement Appropriate amount of water to form a circulation of external drainage;
锅炉碱性排污水的碱度为8mmol/L-20mmol/L,pH值为10-12;The alkalinity of boiler alkaline sewage is 8mmol/L-20mmol/L, and the pH value is 10-12;
经灰水分离器分离后的水中的悬浮物浓度小于等于100mg/L;The concentration of suspended solids in the water separated by the gray water separator is less than or equal to 100mg/L;
定时灰水分离的时间为1-24小时。Timed gray water separation time is 1-24 hours.
一种实现湿式烟气脱硫方法的装置,该装置包括湿式烟气脱硫除尘器、脱水除雾器、灰水分离器,该装置还包括碱性物质溶出池、集水池和脱硫液池;燃煤锅炉排出的烟气进入湿式烟气脱硫除尘器的入口;湿式烟气脱硫除尘器的烟气出口连接脱水除雾器的入口;脱水除雾器的出口经引风机连接烟囱;碱性物质溶出池、集水池和脱硫液池分别为混凝土砌筑的水池;碱性物质溶出池连接烟气脱硫除尘器下部的排出口;碱性物质溶出池和集水池之间设置第一道过滤栅;集水池和脱硫液池之间设置第二道过滤栅;集水池连接锅炉排出的碱性排污水口;集水池由灰浆液泵连接灰水分离器的入口;灰水分离器底部设置泥浆斗,泥浆斗连接碱性物质溶出池;在灰水分离器顶部设置出水管,连接碱性物质溶出池;脱硫液池由脱硫液循环泵连接湿式烟气脱硫除尘器的布水系统。A device for realizing a wet flue gas desulfurization method, the device includes a wet flue gas desulfurization dust collector, a dehydration demister, and a gray water separator, and the device also includes an alkaline substance dissolution pool, a water collection pool, and a desulfurization liquid pool; coal-fired The flue gas discharged from the boiler enters the entrance of the wet flue gas desulfurization dust collector; the flue gas outlet of the wet flue gas desulfurization dust collector is connected to the entrance of the dehydration demister; the outlet of the dehydration demister is connected to the chimney through the induced draft fan; the alkaline substance dissolution tank , water collection pool and desulfurization liquid pool are concrete masonry pools respectively; the alkaline substance dissolution pool is connected to the outlet of the lower part of the flue gas desulfurization dust collector; the first filter grid is set between the alkaline substance dissolution pool and the water collection pool; the water collection pool A second filter grid is set between the desulfurization liquid pool; the sump pool is connected to the alkaline sewage outlet discharged from the boiler; the sump pool is connected to the inlet of the gray water separator by a mortar liquid pump; a mud bucket is set at the bottom of the gray water separator, and the mud bucket is connected to the alkali Dissolution tank for alkaline substances; a water outlet pipe is set on the top of the gray water separator to connect to the dissolution tank for alkaline substances; the desulfurization liquid pool is connected to the water distribution system of the wet flue gas desulfurization dust collector by the desulfurization liquid circulating pump.
本发明提供的湿式烟气脱硫方法及其装置的工作原理:煤炭在锅炉中燃烧后生成的灰渣中,氧化钙(CaO)、氧化镁(MgO)、氧化钠(Na2O)、氧化钾(K2O)等碱性金属氧化物的含量范围很宽,在一定条件下(主要是控制浸取液的pH值及与灰渣的接触时间)可把上述碱性物质溶出,并具有中和酸性物质的作用;灰渣中三氧化二铁(Fe2O3)和三氧化二铝(Al2O3)是两性化合物,在酸性条件下,可以把它们溶出,以中和酸性物质。此外,锅炉给水中含有大量的碳酸盐硬度,为了防止给水中这些盐类在锅炉运行中造成锅炉受热面内部结垢,影响锅炉安全经济运行,需将锅炉给水事先经过钠离子交换处理,将给水中的硬度(主要是钙盐和镁盐),即将易生成水垢钙、镁化合物中的Ca2+、Mg2+被交换剂中的Na+离子所替代转变为不形成水垢的碳酸氢钠(NaHCO3),它在锅炉炉水中受热分解成碳酸钠(Na2CO3)也就是纯碱,是一种理想的脱硫剂。其反应如下:The working principle of the wet flue gas desulfurization method and device provided by the present invention: in the ash generated after the coal is burned in the boiler, calcium oxide (CaO), magnesium oxide (MgO), sodium oxide ( Na2O ), potassium oxide The content range of basic metal oxides such as (K 2 O) is very wide. Under certain conditions (mainly controlling the pH value of the leaching solution and the contact time with the ash) the above-mentioned basic substances can be dissolved and have a neutral and acidic substances; iron oxide (Fe 2 O 3 ) and aluminum oxide (Al 2 O 3 ) in ash are amphoteric compounds, and they can be dissolved under acidic conditions to neutralize acidic substances. In addition, the boiler feed water contains a large amount of carbonate hardness. In order to prevent these salts in the feed water from causing fouling on the heating surface of the boiler during boiler operation and affecting the safe and economical operation of the boiler, the boiler feed water needs to be treated with sodium ion exchange in advance. The hardness of the feed water (mainly calcium salts and magnesium salts), that is, the Ca 2+ and Mg 2+ in the calcium and magnesium compounds that are easy to form scales are replaced by Na + ions in the exchanger and transformed into sodium bicarbonate that does not form scales (NaHCO 3 ), which is decomposed into sodium carbonate (Na 2 CO 3 ) or soda ash in the boiler furnace water, and is an ideal desulfurizer. It reacts as follows:
在钠离子交换中:In sodium ion exchange:
在炉内受热后:After heating in the furnace:
为了使炉水中钙镁的生成物,不以水垢的形式粘结在锅炉内部的受热面上,迫使其在锅炉炉水中结晶出来,形成分散状水渣沉淀,必须保持炉水中的碱度为8mmol/L-20mmol/L,pH值为10-12,为保持此值,按锅炉运行的工艺必须按周期排出。所以锅炉排污水也是一种廉价的脱硫剂。In order to prevent the calcium and magnesium products in the boiler water from sticking to the heating surface inside the boiler in the form of scale, forcing it to crystallize out in the boiler boiler water and form dispersed slag precipitation, the alkalinity in the boiler water must be kept at 8 mmol /L-20mmol/L, the pH value is 10-12, in order to maintain this value, the process operated by the boiler must be discharged periodically. So boiler blowdown water is also a cheap desulfurizer.
本发明提供的湿式烟气脱硫方法的工艺流程是:煤炭在锅炉中燃烧后生成的灰渣在冲渣水的冲击下和冲渣水一起流入碱性物质溶出池,与湿式烟气脱硫除尘器排出的酸性灰水混合,在流经碱性物质溶出池的时间内大部分灰渣逐渐沉积在碱性物质溶出池中,并在酸性灰水和水力搅拌的双重作用下,灰渣中的碱性物质逐渐被溶出,然后,混合灰水从碱性物质溶出池尾部流经第一道过滤栅进入集水池过程中,在除去混合灰水中细小颗粒的同时,灰渣中的碱性物质被进一步溶出;在集水池中混合灰水与锅炉排放的碱性排污水汇集,在流经第二道过滤栅时,进一步除去微小颗粒物后,制备成脱硫液流入水循环系统的脱硫液池。脱硫液经脱硫液循环泵打入湿式烟气脱硫除尘器,在该装置内脱硫液经过三级布水系统和塔板组,与由锅炉流入的烟气充分混合、接触,经脱硫后的洁净烟气经脱水除雾后,由引风机和烟囱排入大气;脱除烟气中的二氧化硫之后产生的酸性灰水,又流入碱性物质溶出池前端,形成脱硫液的循环;灰水分离器,1-24小时一次通过灰浆泵引入集水池中的混合灰水,在该装置内混合灰水经凝聚区、沉淀区和过滤区后,重新使用,并补入适量清水;小部分浓缩灰浆再流经碱性物质溶出池前部形成外排水循环。The process flow of the wet flue gas desulfurization method provided by the present invention is: the ash generated after the coal is burned in the boiler flows into the alkaline substance dissolution pool together with the slag water under the impact of the slag water, and is combined with the wet flue gas desulfurization dust collector The discharged acidic gray water is mixed, and most of the ash is gradually deposited in the alkaline substance dissolution tank during the time of flowing through the alkaline substance dissolution tank, and under the dual action of acidic gray water and hydraulic agitation, the alkali in the ash The alkaline substances are gradually dissolved out, and then, the mixed gray water flows from the tail of the alkaline substance dissolution tank through the first filter grid into the sump, while the fine particles in the mixed gray water are removed, the alkaline substances in the ash residue are further removed Dissolution: In the sump, the gray water is mixed with the alkaline sewage discharged from the boiler, and when it flows through the second filter grid, the fine particles are further removed, and the desulfurization liquid is prepared into the desulfurization liquid pool that flows into the water circulation system. The desulfurization liquid is pumped into the wet flue gas desulfurization dust collector through the desulfurization liquid circulation pump. In this device, the desulfurization liquid passes through the three-stage water distribution system and the tray group, and fully mixes and contacts with the flue gas flowing in from the boiler. After desulfurization, the clean After the flue gas is dehydrated and defogged, it is discharged into the atmosphere by the induced draft fan and the chimney; the acid gray water produced after the removal of sulfur dioxide in the flue gas flows into the front end of the alkaline substance dissolution tank to form a cycle of desulfurization liquid; the gray water separator , once every 1-24 hours, the mixed gray water is introduced into the sump through the mortar pump. After the mixed gray water passes through the coagulation zone, sedimentation zone and filtration zone in the device, it is reused and an appropriate amount of clean water is added; a small part of the concentrated mortar is reused. It flows through the front of the alkaline substance dissolution tank to form an external drainage cycle.
从上述工作原理可以看出,本发明与现有的湿式烟气脱硫方法和装置相比,具有如下的有益效果:It can be seen from the above working principle that, compared with the existing wet flue gas desulfurization method and device, the present invention has the following beneficial effects:
1)脱硫效果好,同时可除去细微的灰尘:1) The desulfurization effect is good, and fine dust can be removed at the same time:
由于本发明采用的湿式烟气脱硫除尘器具有三级布水系统和塔板组,使烟气和脱硫液充分接触,从而达到气液传质性能好的效果,脱硫效率高,同时除去细微的灰尘。Since the wet flue gas desulfurization and dust collector adopted in the present invention has a three-stage water distribution system and a tray group, the flue gas and the desulfurization liquid are fully contacted, thereby achieving the effect of good gas-liquid mass transfer performance, high desulfurization efficiency, and removal of fine particles dust.
2)减少环境污染:2) Reduce environmental pollution:
本发明设置有多个池子组成了其内部的多个水循环系统,减小了废弃物的排放,也就是减小了对环境的污染。The present invention is provided with a plurality of ponds to form a plurality of water circulation systems inside, which reduces the discharge of waste, that is, reduces the pollution to the environment.
3)费用低:3) Low cost:
本发明将锅炉燃烧时排出的废物--灰渣中的碱性物质溶出,并和锅炉排出的废水汇合后作为脱硫液,这种以废治废的方法减小了设备的投资和其运行费用,另外,由于水的循环利用,在节省资源的同时,也降低了费用。In the present invention, the alkaline substances in the waste discharged from the boiler combustion——the ash are dissolved and combined with the waste water discharged from the boiler to be used as desulfurization liquid. This method of treating waste with waste reduces the investment of equipment and its operation cost , In addition, due to the recycling of water, while saving resources, it also reduces costs.
附图说明:Description of drawings:
图1:以废治废湿式烟气脱硫装置示意图。Figure 1: Schematic diagram of a waste-to-waste wet flue gas desulfurization device.
具体实施方式:Detailed ways:
本发明采用燃煤锅炉自身排放碱性物质的湿式烟气脱硫方法及装置,以配用蒸发量35t/h锅炉,处理烟气量为100000m3/h的锅炉烟气。The present invention adopts the wet flue gas desulfurization method and device that the coal-fired boiler itself discharges alkaline substances, and is equipped with a boiler with an evaporation capacity of 35t/h to treat boiler flue gas with a flue gas volume of 100,000m 3 /h.
如图:脱硫方法为:As shown in the figure: the desulfurization method is:
1)溶出煤渣中的碱性物质,并形成冲渣水的循环:冲渣水从碱性物质溶出池14的后部经冲渣泵13引出,使锅炉内煤炭燃烧后生成的灰渣随冲渣水一起流入碱性物质溶出池14,与湿式烟气脱硫除尘器2排出的酸性灰水混合汇合,在酸性灰水和水力搅拌的双重作用下,将灰渣中的碱性物质逐渐溶出,同时,形成冲渣水的循环;1) Dissolving the alkaline substances in the coal slag, and forming a cycle of slag washing water: the slag washing water is drawn from the rear of the alkaline substance dissolution tank 14 through the slag washing pump 13, so that the ash generated after the coal combustion in the boiler is flushed The slag water flows into the alkaline substance dissolution tank 14 together, and is mixed with the acid gray water discharged from the wet flue gas desulfurization dust collector 2. At the same time, a cycle of flushing slag water is formed;
2)一次过滤:上述灰渣水与酸性灰水混合液经过滤后,流入集水池16;2) Primary filtration: the above-mentioned mixture of ash water and acidic ash water flows into the sump 16 after being filtered;
3)混合:上述溶液在集水池16中与锅炉排出的碱性排污水汇合;3) Mixing: the above solution merges with the alkaline sewage discharged from the boiler in the sump 16;
4)二次过滤:汇合后的溶液,经过滤进一步滤除细小颗粒后流入脱硫液池19,形成脱硫液;4) Secondary filtration: the merged solution flows into the desulfurization liquid pool 19 after further filtering out fine particles to form a desulfurization liquid;
5)烟气脱硫:上述的脱硫液进入湿式烟气脱硫除尘器2,与进入该装置内的燃煤锅炉排出的烟气1发生化学反应,脱除二氧化硫污染物;5) Flue gas desulfurization: the above-mentioned desulfurization liquid enters the wet type flue gas desulfurization dust collector 2, and chemically reacts with the flue gas 1 discharged from the coal-fired boiler entering the device to remove sulfur dioxide pollutants;
6)脱硫液循环:上述脱硫液使烟气脱硫后,产生的酸性灰水,流入碱性物质溶出池14的前端,形成脱硫液循环;6) Desulfurization liquid circulation: after the above-mentioned desulfurization liquid desulfurizes the flue gas, the acid gray water produced flows into the front end of the alkaline substance dissolution tank 14 to form a desulfurization liquid circulation;
7)烟气脱水除雾:脱硫后的烟气经脱水除雾器9脱水除雾后,排入大气;7) Flue gas dehydration and defogging: the desulfurized flue gas is discharged into the atmosphere after being dehydrated and defogged by the demister 9;
8)定时灰水分离:每8小时,将集水池16中溶液注入灰水分离器22,分离后的水,其中的悬浮物浓度小于等于100mg/L,从灰水分离器顶部出水管12排出,重新使用,并适量补充清水;浆液从泥浆斗7流入碱性物质溶出池14,形成外排水的循环。8) Regular gray water separation: every 8 hours, inject the solution in the sump 16 into the gray water separator 22, and the separated water, in which the concentration of suspended matter is less than or equal to 100 mg/L, is discharged from the outlet pipe 12 at the top of the gray water separator , re-use, and add an appropriate amount of clear water; the slurry flows from the mud bucket 7 into the alkaline substance dissolution tank 14, forming a circulation of external drainage.
锅炉碱性排污水17的碱度为10mmol/L,pH值为10.5。The alkalinity of boiler alkaline sewage 17 is 10mmol/L, and the pH value is 10.5.
实现湿式烟气脱硫方法的装置,包括湿式烟气脱硫除尘器2、脱水除雾器9、灰水分离器22,碱性物质溶出池14、集水池16和脱硫液池19;燃煤锅炉排出的烟气1进入湿式烟气脱硫除尘器2的入口;湿式烟气脱硫除尘器2的烟气出口通过管道连接脱水除雾器9的入口;脱水除雾器9的出口经引风机10连接烟囱11;碱性物质溶出池14、集水池16和脱硫液池19为混凝土砌筑的水池,整合在一起,由三道水墙和两道过滤栅分割成三个彼此独立又相互连接的容水空间;碱性物质溶出池14连接烟气脱硫除尘器下部的排出口8;碱性物质溶出池14和集水池16之间设置第一道过滤栅15;集水池16和脱硫液池19之间设置第二道过滤栅18;集水池16通过管道连接锅炉排出的碱性排污水口17;集水池16由灰浆液泵21及管道连接灰水分离器22的入口;在灰水分离器22顶部设置出水管12,连接碱性物质溶出池14;脱硫液池19由脱硫液循环泵20连接湿式烟气脱硫除尘器2的布水系统3、4、5。A device for realizing the wet flue gas desulfurization method, including wet flue gas desulfurization dust collector 2, dehydration demister 9, ash water separator 22, alkaline substance dissolution pool 14, water collection pool 16 and desulfurization liquid pool 19; coal-fired boiler discharge The flue gas 1 enters the entrance of the wet flue gas desulfurization dust collector 2; the flue gas outlet of the wet flue gas desulfurization dust collector 2 is connected to the entrance of the dehydration demister 9 through a pipe; the outlet of the dehydration demister 9 is connected to the chimney through the induced draft fan 10 11. Alkaline substance dissolution pool 14, sump pool 16 and desulfurization liquid pool 19 are pools made of concrete masonry, which are integrated together and divided into three independent and interconnected water holding tanks by three water walls and two filter grids. space; the alkaline substance dissolution pool 14 is connected to the outlet 8 of the lower part of the flue gas desulfurization dust collector; the first filter grid 15 is set between the alkaline substance dissolution pool 14 and the water collection pool 16; between the water collection pool 16 and the desulfurization liquid pool 19 The second filter grid 18 is set; the sump 16 is connected to the alkaline sewage outlet 17 discharged from the boiler through pipelines; the sump 16 is connected to the entrance of the gray water separator 22 by the gray slurry pump 21 and the pipeline; The outlet pipe 12 is connected to the alkaline substance dissolution pool 14; the desulfurization liquid pool 19 is connected to the water distribution systems 3, 4, and 5 of the wet flue gas desulfurization and dust collector 2 by the desulfurization liquid circulation pump 20.
其中:湿式烟气脱硫除尘器2采用本所申请的专利(申请号为2004200481440.6),直径为2.5米、总高为13.6米;脱水除雾器9采用本所申请的专利(申请号为03245346.9),为波形折板组型;灰水分离器22采用本所申请的专利(申请号为200420047915.x);碱性物质溶出池14为10米*5米*5米;集水池16和脱硫液池19分别为5米*5米*5米。Among them: the wet flue gas desulfurization dust collector 2 adopts the patent applied by our institute (application number is 2004200481440.6), with a diameter of 2.5 meters and a total height of 13.6 meters; the dehydration demister 9 adopts the patent applied by our institute (application number is 03245346.9) , is a corrugated folded plate group type; gray water separator 22 adopts the patent (application number is 200420047915. Pool 19 is respectively 5 meters * 5 meters * 5 meters.
燃煤锅炉排出的烟气1,通过烟道进入直径为2.5米、总高为13.6米的湿式复合式烟气脱硫除尘器2,在该装置内设置有第一级布水系统3、第二级布水系统4、第三级布水系统5以及塔板组6,烟气在流经上述区域时与由锅炉碱性物质溶出并汇集的脱硫液充分混合、接触,烟气中的二氧化硫与脱硫液中钙、镁等离子发生化学反应,生成的硫酸盐和亚硫酸盐等脱硫副产物随水流从烟气脱硫除尘器下部的排出口8排出,进入水循环系统。当锅炉燃用中低硫煤时,脱硫后烟气中的二氧化硫浓度可达到GB13271“锅炉大气污染物排放标准”规定的限值以下。经脱硫后的烟气再通入阻力仅为100Pa左右、除水雾效率为97-99%的脱水除雾器9,脱除水雾后的烟气再经引风机10排入烟囱11。The flue gas 1 discharged from the coal-fired boiler enters the wet compound flue gas desulfurization and dust collector 2 with a diameter of 2.5 meters and a total height of 13.6 meters through the flue. The device is equipped with a first-stage water distribution system 3 and a second-stage Level water distribution system 4, third level water distribution system 5 and tray group 6, when the flue gas flows through the above areas, it is fully mixed and contacted with the desulfurization liquid dissolved and collected by the boiler alkaline substances, the sulfur dioxide in the flue gas and Calcium, magnesium and other ions in the desulfurization liquid react chemically, and the generated desulfurization by-products such as sulfate and sulfite are discharged from the outlet 8 at the lower part of the flue gas desulfurization dust collector along with the water flow, and enter the water circulation system. When the boiler burns medium-low sulfur coal, the concentration of sulfur dioxide in the flue gas after desulfurization can reach below the limit value specified in GB13271 "Emission Standard of Air Pollutants for Boilers". The desulfurized flue gas passes into the dehydration demister 9 with a resistance of only about 100 Pa and a mist removal efficiency of 97-99%.
当锅炉内煤炭燃烧后生成的灰渣流入碱性物质溶出池14并与脱硫除尘器排出的酸性灰水汇合,在酸性灰水和水力搅拌的双重作用下,灰渣中的碱性物质逐渐被溶出,大颗粒灰渣沉积在碱性物质溶出池14中,然后经第一道过滤栅15去除细小的灰渣颗粒后流入集水池16,与锅炉排出的碱性排污水17汇合后,再流经第二道过滤栅18,在进一步滤除细小颗粒后流入脱硫液池19。When the ash generated after coal combustion in the boiler flows into the alkaline substance dissolution tank 14 and merges with the acid ash water discharged from the desulfurization dust collector, under the dual action of acid ash water and hydraulic agitation, the alkaline substances in the ash are gradually dissolved Dissolution, large particles of ash and slag are deposited in the alkaline substance dissolution pool 14, and then flow into the sump 16 after the first filter grid 15 removes the fine ash and slag particles, merge with the alkaline sewage 17 discharged from the boiler, and then flow After passing through the second filter grid 18, it flows into the desulfurization liquid pool 19 after further filtering out fine particles.
脱硫液循环泵20从脱硫液池一侧汲取脱硫液后,打入湿式复合式烟气脱硫除尘器,从而实现烟气脱硫工艺的流程。The desulfurization liquid circulation pump 20 draws the desulfurization liquid from one side of the desulfurization liquid pool, and pumps it into the wet compound flue gas desulfurization dust collector, thereby realizing the flow of the flue gas desulfurization process.
本发明中为防止水循环系统中因脱硫副产物浓缩而产生的结垢现象,设置了灰水分离器22、灰浆液泵21,每8小时从集水池一侧汲水后打入,经分离后,水中的悬浮物浓度可低于100mg/L,并从灰水分离器顶部出水管12排出系统外,以降低水中脱硫副产物的浓度,防止结垢。浓缩后的浆液从泥浆斗7排出器外,流入碱性物质溶出池14。In the present invention, in order to prevent the fouling phenomenon caused by the concentration of desulfurization by-products in the water circulation system, the gray water separator 22 and the gray slurry liquid pump 21 are set up, and the water is pumped in from one side of the sump every 8 hours. , the concentration of suspended matter in the water can be lower than 100mg/L, and it is discharged out of the system from the outlet pipe 12 at the top of the gray water separator to reduce the concentration of desulfurization by-products in the water and prevent scaling. The concentrated slurry is discharged from the mud hopper 7 and flows into the alkaline substance dissolution tank 14 .
从上述工作原理可以看出,本发明与现有的湿式烟气脱硫方法和装置相比,具有气液传质性强、脱硫液循环利用、用水量小、适用范围广、投资和运行费用低、在脱硫的同时还可以除去细微烟尘等优点。It can be seen from the above working principle that compared with the existing wet flue gas desulfurization methods and devices, the present invention has strong gas-liquid mass transfer, desulfurization liquid recycling, small water consumption, wide application range, low investment and operating costs , It can also remove fine smoke and dust while desulfurizing.
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Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
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CN100448512C (en) * | 2005-10-19 | 2009-01-07 | 中国石油化工股份有限公司 | Coal burning boiler flue gas desulfurization method and device |
CN101972578A (en) * | 2010-09-10 | 2011-02-16 | 西昌新钒钛有限公司 | Rotary kiln flue gas treating device capable of automatically controlling blowing rate of draught fan |
CN102824825A (en) * | 2012-09-12 | 2012-12-19 | 无锡光初科技服务有限公司 | Multi-effect U-shaped tube type dedusting and desulfurization integrated device of coal-fired boiler and dedusting and desulfurization method thereof |
CN108939896A (en) * | 2018-08-30 | 2018-12-07 | 西北矿冶研究院 | Waste heat boiler water desulfurization device and method |
CN109589767A (en) * | 2018-12-17 | 2019-04-09 | 郑州大学 | The method and apparatus of pollutant integration removing in a kind of glass furnace fume |
CN109745813A (en) * | 2018-03-29 | 2019-05-14 | 王雅珍 | Nitre dehydration integrated tower and its application method drop in YZ type vortex mixed desulfurization and dedusting |
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2004
- 2004-11-10 CN CN 200410090734 patent/CN1631493A/en active Pending
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100448512C (en) * | 2005-10-19 | 2009-01-07 | 中国石油化工股份有限公司 | Coal burning boiler flue gas desulfurization method and device |
CN101972578A (en) * | 2010-09-10 | 2011-02-16 | 西昌新钒钛有限公司 | Rotary kiln flue gas treating device capable of automatically controlling blowing rate of draught fan |
CN102824825A (en) * | 2012-09-12 | 2012-12-19 | 无锡光初科技服务有限公司 | Multi-effect U-shaped tube type dedusting and desulfurization integrated device of coal-fired boiler and dedusting and desulfurization method thereof |
CN109745813A (en) * | 2018-03-29 | 2019-05-14 | 王雅珍 | Nitre dehydration integrated tower and its application method drop in YZ type vortex mixed desulfurization and dedusting |
CN108939896A (en) * | 2018-08-30 | 2018-12-07 | 西北矿冶研究院 | Waste heat boiler water desulfurization device and method |
CN109589767A (en) * | 2018-12-17 | 2019-04-09 | 郑州大学 | The method and apparatus of pollutant integration removing in a kind of glass furnace fume |
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