CN101818092B - Integrated fluidized bed mild-gasification lignite upgrading system and technology - Google Patents
Integrated fluidized bed mild-gasification lignite upgrading system and technology Download PDFInfo
- Publication number
- CN101818092B CN101818092B CN2009102191271A CN200910219127A CN101818092B CN 101818092 B CN101818092 B CN 101818092B CN 2009102191271 A CN2009102191271 A CN 2009102191271A CN 200910219127 A CN200910219127 A CN 200910219127A CN 101818092 B CN101818092 B CN 101818092B
- Authority
- CN
- China
- Prior art keywords
- gasification
- fluidized bed
- upgrading
- lignite
- brown coal
- 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.)
- Active
Links
- 239000003077 lignite Substances 0.000 title claims abstract description 114
- 238000002309 gasification Methods 0.000 title claims abstract description 63
- 238000005516 engineering process Methods 0.000 title description 3
- 238000000034 method Methods 0.000 claims abstract description 22
- 238000002485 combustion reaction Methods 0.000 claims abstract description 13
- 238000006243 chemical reaction Methods 0.000 claims abstract description 9
- 238000000197 pyrolysis Methods 0.000 claims abstract description 3
- 239000003245 coal Substances 0.000 claims description 44
- 239000007789 gas Substances 0.000 claims description 37
- 239000011362 coarse particle Substances 0.000 claims description 22
- 239000010419 fine particle Substances 0.000 claims description 21
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 14
- 239000003546 flue gas Substances 0.000 claims description 14
- 238000012216 screening Methods 0.000 claims description 10
- 239000000463 material Substances 0.000 claims description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 9
- 239000002245 particle Substances 0.000 claims description 7
- 239000002893 slag Substances 0.000 claims description 7
- 238000005243 fluidization Methods 0.000 claims description 6
- 239000000843 powder Substances 0.000 claims description 6
- 235000019738 Limestone Nutrition 0.000 claims description 5
- 239000006028 limestone Substances 0.000 claims description 5
- 239000007787 solid Substances 0.000 claims description 3
- 239000004449 solid propellant Substances 0.000 claims description 3
- 239000010881 fly ash Substances 0.000 claims 9
- 239000000567 combustion gas Substances 0.000 claims 2
- 239000000779 smoke Substances 0.000 claims 2
- 239000002817 coal dust Substances 0.000 claims 1
- 238000001816 cooling Methods 0.000 claims 1
- 238000007599 discharging Methods 0.000 claims 1
- 239000012530 fluid Substances 0.000 claims 1
- 239000002737 fuel gas Substances 0.000 claims 1
- 238000000926 separation method Methods 0.000 claims 1
- 239000003344 environmental pollutant Substances 0.000 abstract description 3
- 231100000719 pollutant Toxicity 0.000 abstract description 3
- 238000005265 energy consumption Methods 0.000 abstract description 2
- 239000002351 wastewater Substances 0.000 abstract 1
- 239000000047 product Substances 0.000 description 35
- 239000000428 dust Substances 0.000 description 20
- 239000011265 semifinished product Substances 0.000 description 9
- 230000002269 spontaneous effect Effects 0.000 description 3
- QJZYHAIUNVAGQP-UHFFFAOYSA-N 3-nitrobicyclo[2.2.1]hept-5-ene-2,3-dicarboxylic acid Chemical compound C1C2C=CC1C(C(=O)O)C2(C(O)=O)[N+]([O-])=O QJZYHAIUNVAGQP-UHFFFAOYSA-N 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 239000002802 bituminous coal Substances 0.000 description 2
- 230000018044 dehydration Effects 0.000 description 2
- 238000006297 dehydration reaction Methods 0.000 description 2
- 238000004880 explosion Methods 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 239000004021 humic acid Substances 0.000 description 2
- 238000005065 mining Methods 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000003763 carbonization Methods 0.000 description 1
- 238000012824 chemical production Methods 0.000 description 1
- 238000005056 compaction Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 239000002803 fossil fuel Substances 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000003415 peat Substances 0.000 description 1
- 230000009257 reactivity Effects 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
Images
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/129—Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
Landscapes
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
Abstract
整体流化床轻度气化褐煤提质系统及工艺,利用由低值燃气焚烧炉产生的高温空气对褐煤进行预干燥处理,脱去褐煤中的一部分水分;随后褐煤被送入流化床轻度气化褐煤提质反应器,褐煤在流化床轻度气化褐煤提质反应器内发生部分气化、干馏及燃烧反应,反应产生的热量一部分用于维持反应器内的温度,一部分用于褐煤水分的脱除,经过流化床轻度气化褐煤提质反应器提质的褐煤送入成品冷却器冷却后送入成品仓,产生的低值燃气送入后续的低值燃气焚烧炉焚烧利用;具有工艺简单、操作方便、能耗低、污染物排放少、无废水排放的特点。
Integral fluidized bed mild gasification lignite upgrading system and process, using high temperature air generated by low-value gas incinerators to pre-dry lignite to remove part of the moisture in lignite; then lignite is sent to the fluidized bed for light High-degree gasification lignite upgrading reactor, lignite undergoes partial gasification, dry distillation and combustion reactions in the fluidized bed mild gasification lignite upgrading reactor, part of the heat generated by the reaction is used to maintain the temperature in the reactor, and part of it is used to For the removal of lignite moisture, the lignite upgraded by the fluidized bed light gasification lignite upgrading reactor is sent to the finished product cooler to cool and then sent to the finished product warehouse, and the low-value gas generated is sent to the subsequent low-value gas incinerator Incineration utilization; it has the characteristics of simple process, convenient operation, low energy consumption, less pollutant discharge and no waste water discharge.
Description
技术领域 technical field
本发明涉及一种物料干燥提质系统及工艺,特别涉及一种整体流化床轻度气化褐煤提质系统及工艺。The invention relates to a material drying and upgrading system and process, in particular to an integral fluidized bed mild gasification lignite upgrading system and process.
背景技术 Background technique
褐煤是一种煤化程度较低的常见煤种,是由泥炭沉积后经脱水、压实转变为有机生物岩的初期产物,因外表呈褐色或者暗褐色而得名。褐煤大多数无光泽,真密度在1.10~1.40g/cm3之间,水分高达30~60%,挥发分高,燃点低,不粘结,易风化变质,含原生腐殖酸,含氧高,化学反应性强,热稳定性差,是一种易燃的化石燃料。原生腐殖酸是褐煤区别于其它煤种的主要特征组分。Lignite is a common coal with a low degree of coalification. It is the initial product of organic biorock after peat deposition after dehydration and compaction. It is named for its brown or dark brown appearance. Lignite is mostly dull, with a true density of 1.10-1.40g/cm 3 , a moisture content of 30-60%, high volatile content, low ignition point, non-bonding, easy weathering and deterioration, containing native humic acid, and high oxygen content , strong chemical reactivity, poor thermal stability, is a flammable fossil fuel. Primary humic acid is the main characteristic component that distinguishes lignite from other coals.
中国已探明的褐煤储量达到1300亿t,占到全国煤炭总储量的13%左右。中国的褐煤资源主要分布在内蒙古自治区东部和西南地区的云南省境内。China's proven lignite reserves have reached 130 billion tons, accounting for about 13% of the country's total coal reserves. China's lignite resources are mainly distributed in Yunnan Province in the east and southwest of the Inner Mongolia Autonomous Region.
从中国褐煤的形成时代看,以中生代侏罗纪(距今约2.05亿年~距今1.44亿年)褐煤储量的比例最大,约占全国褐煤储量的4/5,主要分布在内蒙古东部与东北三省紧密相连的东三盟地区。新生代第三纪(距今6500万年~距今180万年)褐煤资源约占全国褐煤储量的1/5左右,主要分布在云南省境内。此外,四川、广东、广西、海南等省也有少量第三纪褐煤,华东地区的第三纪褐煤主要分布在山东省境内,东北三省也有部分第三纪褐煤。在侏罗纪褐煤中极少有早、中侏罗纪褐煤,一般均为晚侏罗纪褐煤,或者称为老年褐煤,主要分布在我国内蒙古自治区东部海拉尔含煤区霍林河盆地以及黑龙江三江-穆林河含煤区,这一地区是我国褐煤资源的集中地区。From the perspective of the formation age of lignite in China, the Mesozoic Jurassic (about 205 million years ago to 144 million years ago) lignite reserves accounted for the largest proportion, accounting for about 4/5 of the national lignite reserves, mainly distributed in eastern Inner Mongolia and northeast China The three provinces are closely connected to the East Tri-Alliance area. Cenozoic Tertiary (65 million years ago to 1.8 million years ago) lignite resources account for about 1/5 of the national lignite reserves, mainly distributed in Yunnan Province. In addition, Sichuan, Guangdong, Guangxi, Hainan and other provinces also have a small amount of Tertiary lignite. The Tertiary lignite in East China is mainly distributed in Shandong Province, and there are also some Tertiary lignite in the three northeastern provinces. In the Jurassic lignite, there are very few early and middle Jurassic lignites, and they are generally Late Jurassic lignite, or old lignite, which are mainly distributed in the Huolinhe Basin in the Hailaer coal-bearing area in the eastern Inner Mongolia Autonomous Region of my country and Sanjiang, Heilongjiang. - Mulinhe coal-bearing area, which is the concentrated area of lignite resources in my country.
内蒙古自治区是我国褐煤储量占绝对多数的一个省份,占全国褐煤资源的3/4以上。我国储量最大的一些褐煤煤田几乎都集中在内蒙古东部靠近东北三省的边境地区,其中开发较早的有扎赉诺尔、元宝山、平庄等煤田,随后有霍林河、伊敏和大雁煤田,这些煤田的储量都在几十亿吨至上百亿吨。The Inner Mongolia Autonomous Region is a province with an absolute majority of lignite reserves in my country, accounting for more than 3/4 of the national lignite resources. Some of the lignite coal fields with the largest reserves in my country are almost concentrated in the eastern part of Inner Mongolia near the border areas of the three northeastern provinces. Among them, coal fields such as Zhalainuoer, Yuanbaoshan, and Pingzhuang were developed earlier, followed by Huolinhe, Yimin, and Dayan coal fields. Coal reserves are in the range of several billion tons to tens of billion tons.
随着世界优质煤炭资源越来越少,开采费用日益增高,许多国家开始或更加重视开发丰富的褐煤资源。褐煤与其他煤种相比,含氧量高、灰分及灰熔点变化较大、密度小、容易自燃、煤粉容易爆炸。褐煤直接利用存在诸多问题,褐煤中较高的水分含量,增加了褐煤的运输成本,限制了褐煤由矿区向较远地区用户的运输。褐煤属于极易自燃的煤种,因此在长距离运输过程中还会带来自燃和爆炸的问题。As the world's high-quality coal resources are becoming less and less and mining costs are increasing, many countries have begun or paid more attention to the development of rich lignite resources. Compared with other types of coal, lignite has high oxygen content, large changes in ash content and ash melting point, low density, easy spontaneous combustion, and easy explosion of coal powder. There are many problems in the direct utilization of lignite. The high moisture content in lignite increases the transportation cost of lignite and limits the transportation of lignite from mining areas to users in remote areas. Lignite is a kind of coal that is highly prone to spontaneous combustion, so it will also cause problems of spontaneous combustion and explosion during long-distance transportation.
目前褐煤提质技术处于试验研究和工程化初始应用阶段,各种不同的褐煤提质技术在具有自身优势的同时,也存在明显的缺陷。大部分技术工艺系统非常复杂,褐煤提质成本高昂,系统运行可靠性低,对环境有着较大的污染等,离真正大规模工业化应用还有相当长的距离。At present, lignite upgrading technology is in the stage of experimental research and initial application of engineering. While various lignite upgrading technologies have their own advantages, they also have obvious defects. Most of the technical process systems are very complex, lignite upgrading costs are high, the system operation reliability is low, and there is a lot of pollution to the environment. There is still a long way to go before the real large-scale industrial application.
褐煤脱水和提质加工后,其成分和性质趋近于烟煤,将更有利于利用、运输和储存。我国现役大量设计燃用烟煤的机组,由于煤源情况变化,燃料供应紧张,成本据高不下。若能利用褐煤提质制成的燃料在不对原锅炉机组进行大的技术改造的情况下,直接掺烧燃用,可以有效利用褐煤资源,大幅提高褐煤的利用价值,具有十分重要的现实意义和良好的经济性。After dehydration and upgrading, the composition and properties of lignite tend to be similar to those of bituminous coal, which will be more conducive to utilization, transportation and storage. There are a large number of units designed to burn bituminous coal in active service in my country. Due to changes in coal sources, fuel supply is tight, and the cost is said to be high. If the fuel made from lignite upgrading can be directly blended and used without major technical transformation of the original boiler unit, lignite resources can be effectively utilized and the utilization value of lignite can be greatly improved, which has very important practical significance and Good economy.
发明内容 Contents of the invention
为了克服上述现有技术的缺点,本发明的目的在于提供一种整体流化床轻度气化褐煤提质系统及工艺,具有工艺简单、操作方便、能耗低、耗水少、能满足大型化生产要求的特点。In order to overcome the above-mentioned shortcomings of the prior art, the object of the present invention is to provide a system and process for upgrading the quality of lignite by integral fluidized bed light gasification, which has the advantages of simple process, convenient operation, low energy consumption, less water consumption, and can meet the needs of large-scale characteristics of chemical production requirements.
为了实现上述目的,本发明采用的技术解决方案为:In order to achieve the above object, the technical solution adopted in the present invention is:
整体流化床轻度气化褐煤提质系统,包括一破碎筛分系统1,破碎筛分系统1的物料出口端与预干燥器原煤仓2和低值燃气焚烧炉原煤仓20的进料口端相连,预干燥器原煤仓2的出料口端与给料机3的进料口端相连接,给料机3的出料口端与预干燥器4的入料口端相连接,送风机6的出风口端与低值燃气焚烧炉空气预热器5的进风口端相连接,低值燃气焚烧炉空气预热器5的出风口端与预干燥器4的进风口端相连接,预干燥器4的出风口端与旋风分离器7的入口端相连接,旋风分离器7的出风口端与除尘器8的入口端相连接,旋风分离器7的出料口端与半成品仓10的进料口端相连接,除尘器8的出口端与引风机9的入口端相连接,除尘器8的物料出口端与半成品仓10的进料口端相连接。The integrated fluidized bed light gasification lignite upgrading system includes a crushing and screening system 1, the material outlet of the crushing and screening system 1, the raw coal bunker 2 of the pre-dryer and the raw coal bunker 20 of the low-value gas incinerator. The outlet end of the raw coal bunker 2 of the pre-dryer is connected with the inlet end of the feeder 3, the outlet end of the feeder 3 is connected with the inlet end of the pre-dryer 4, and the blower The air outlet end of 6 is connected to the air inlet end of the air preheater 5 of the low-value gas incinerator, and the air outlet end of the air preheater 5 of the low-value gas incinerator is connected to the air inlet end of the pre-dryer 4. The air outlet end of the dryer 4 is connected with the inlet end of the cyclone separator 7, the air outlet end of the cyclone separator 7 is connected with the inlet end of the dust collector 8, and the outlet end of the cyclone separator 7 is connected with the
整体流化床轻度气化褐煤提质系统,其半成品仓10的出料口端与给料机11的进料口端相连接,给料机11的出料口端与流化床轻度气化褐煤提质反应器12的进料口端相连接,流化床轻度气化褐煤提质反应器12的粗颗粒成品出料口端与粗颗粒成品冷却器13的进料口端相连接,粗颗粒成品冷却器13的出料口端与粗颗粒成品仓14的进料口端相连接;流化床轻度气化褐煤提质反应器12的烟气出口端与旋风分离器19的烟气进口端相连接,旋风分离器19的出风口端与低值燃气焚烧炉22的低值燃气入口端相连接,旋风分离器19的出料口端与细颗粒成品冷却器18的入料口端相连接,细颗粒成品冷却器18的出料口端与细颗粒成品仓17的进料口端相连接;送风机16的出风口端与低值燃气焚烧炉空气预热器15的进风口端相连接,低值燃气焚烧炉空气预热器15的出风口端与流化床轻度气化褐煤提质反应器12的风室相连接。In the integrated fluidized bed mild gasification lignite upgrading system, the discharge port of the
整体流化床轻度气化褐煤提质系统,其原煤仓20的出料口端与给料机21的进料口端相连接,给料机21的出料口端与低值燃气焚烧炉22的进料口端相连接,低值燃气焚烧炉22的烟气出口端与旋风分离器24的进口端相连接,旋风分离器24的出风口端与尾部烟道32的进口端相连接,尾部烟道32的出口端与除尘器29的进口端相连接,除尘器29的出口端与引风机30的进口端相连接,引风机30的出口端与烟囱31的进口端相连接;低值燃气焚烧炉22的出渣口端与冷渣器25的进口端相连接;送风机27的出风口端与低值燃气焚烧炉22的空气预热器26的进风口端相连接,空气预热器26的出口端与低值燃气焚烧炉22的风室相连接;石灰石系统23的出料口端与低值燃气焚烧炉22的返料器斜管相连接;罗茨风机28的出风口与低值燃气焚烧炉22的返料器底部风室相连接。In the overall fluidized bed mild gasification lignite upgrading system, the discharge port of the raw coal bunker 20 is connected to the feed port of the feeder 21, and the discharge port of the feeder 21 is connected to the low-value gas incinerator 22 are connected to each other, the flue gas outlet port of the low-value gas incinerator 22 is connected to the inlet port of the cyclone separator 24, and the air outlet port of the cyclone separator 24 is connected to the inlet port of the tail flue 32, The outlet end of tail flue 32 is connected with the inlet end of dust collector 29, the outlet end of dust collector 29 is connected with the inlet end of induced draft fan 30, and the outlet end of induced draft fan 30 is connected with the inlet end of chimney 31; The slag outlet end of the gas incinerator 22 is connected with the inlet end of the slag cooler 25; the air outlet end of the blower 27 is connected with the air inlet end of the air preheater 26 of the low-value gas incinerator 22, and the air preheater The outlet end of 26 is connected with the wind chamber of low-value gas incinerator 22; The air chamber at the bottom of the feeder of the value gas incinerator 22 is connected.
整体流化床轻度气化褐煤提质工艺,褐煤经过破碎筛分系统1破碎到小于50mm粒度的颗粒后,输送进入原煤仓2和原煤仓20,褐煤从原煤仓2的出料口由给料机3控制进入预干燥器4,高温空气通过预干燥器4之后,温度降到100℃以下,经过尾部的旋风分离器7分离后,送入除尘器8,经除尘器8把大部分固体颗粒脱除后直接由引风机9排空,由旋风分离器7和除尘器8捕集下来的细粉送入半成品仓10;半成品仓10中的预干燥煤经由给料机11给入流化床轻度气化褐煤提质反应器12进行深度提质,预干燥煤在流化床轻度气化褐煤提质反应器12内经热空气流化后,在流化床轻度气化褐煤提质反应器12内发生轻度气化、燃烧、干馏反应,褐煤中的全部水分被释放到烟气中,流化床轻度气化褐煤提质反应器12的温度由褐煤发生的化学反应产生的热量来维持。Integral fluidized bed mild gasification lignite upgrading process. After the lignite is crushed into particles smaller than 50mm in size by the crushing and screening system 1, it is transported into the raw coal bunker 2 and the raw coal bunker 20. The lignite is fed from the outlet of the raw coal bunker 2 to The feeder 3 is controlled to enter the pre-dryer 4. After the high-temperature air passes through the pre-dryer 4, the temperature drops below 100°C. After being separated by the cyclone separator 7 at the tail, it is sent to the dust collector 8, and most of the solids are removed by the dust collector 8. After the particles are removed, it is directly emptied by the induced draft fan 9, and the fine powder captured by the cyclone separator 7 and the dust collector 8 is sent to the
经深度提质,会产生两种不同粒径的提质褐煤,即粗颗粒成品与细颗粒成品,其中粗颗粒成品由流化床轻度气化褐煤提质反应器12底部的排料口排入粗颗粒成品冷却器13,经冷却至温度低于75℃后送入粗颗粒成品仓14;烟气携带的一部分细颗粒成品经由旋风分离器19分离后,大部分被分离下来,由旋风分离器19下部的排料口排入细颗粒成品冷却器18,经冷却至温度低于75℃后送入细颗粒成品仓17。After deep upgrading, two kinds of upgraded lignite with different particle sizes will be produced, i.e. coarse-grained finished product and fine-grained finished product, wherein the coarse-grained finished product is discharged from the discharge port at the bottom of the fluidized bed mild gasification lignite upgrading reactor 12. into the coarse particle finished product cooler 13, and after being cooled to a temperature lower than 75°C, it is sent to the coarse particle finished product bin 14; a part of the fine particle finished product carried by the flue gas is separated by the
由流化床轻度气化褐煤提质反应器12排出的低值燃气经旋风分离器19除去大部分煤粉后送入低值燃气焚烧炉22焚烧利用;低值燃气焚烧炉22为一炉膛绝热的循环流化床锅炉,通过补燃部分固体燃料和添加石灰石来实现低值燃气的充分燃烧和降低污染物(SO2)的排放;低值燃烧焚烧炉22产生的高温烟气经由布置在尾部烟道32内的空气预热器5、15、26换热冷却后经除尘器29排出后,由引风机30送入烟囱31排空;冷风被送入空气预热器5、15、26换热升温后送至预干燥器4、流化床轻度气化褐煤提质反应器12和低值燃气焚烧炉22利用。The low-value gas discharged from the fluidized bed mild gasification lignite upgrading reactor 12 is sent to the low-value gas incinerator 22 for incineration after the
预干燥器4内的流化速度控制在1.0~6.0m/s之间,温度控制在20~90℃之间。The fluidization velocity in the pre-dryer 4 is controlled between 1.0-6.0 m/s, and the temperature is controlled between 20-90°C.
流化床轻度气化褐煤提质反应器12内的流化速度控制在1.0~6.0m/s之间,主反应区的温度控制在300℃~700℃之间。经提质的褐煤,其水分最终可以控制到<10%。The fluidization velocity in the fluidized bed mild gasification lignite upgrading reactor 12 is controlled between 1.0-6.0 m/s, and the temperature of the main reaction zone is controlled between 300°C and 700°C. The water content of the upgraded lignite can be controlled to <10%.
附图说明 Description of drawings
附图为本发明的系统结构示意图。The accompanying drawing is a schematic diagram of the system structure of the present invention.
具体实施方式 Detailed ways
下面将结合附图对本发明的结构原理和工艺原理做进一步的详细说明。The structural principles and process principles of the present invention will be further described in detail below in conjunction with the accompanying drawings.
参见附图,本发明的整体流化床轻度气化褐煤提质系统,包括一破碎筛分系统1,破碎筛分系统1的物料出口端与预干燥器原煤仓2和低值燃气焚烧炉原煤仓20的进料口端相连,预干燥器原煤仓2的出料口端与给料机3的进料口端相连接,给料机3的出料口端与预干燥器4的入料口端相连接,送风机6的出风口端与低值燃气焚烧炉空气预热器5的进风口端相连接,低值燃气焚烧炉空气预热器5的出风口端与预干燥器4的进风口端相连接,预干燥器4的出风口与旋风分离器7的入口端相连接,旋风分离器7的出风口端与除尘器8的入口端相连接,旋风分离器7的出料口端与半成品仓10的进料口端相连接,除尘器8的出口端与引风机9的入口端相连接,除尘器8的物料出口端与半成品仓10的进料口端相连接。Referring to the accompanying drawings, the integral fluidized bed mild gasification lignite upgrading system of the present invention includes a crushing and screening system 1, the material outlet end of the crushing and screening system 1, the raw coal bunker 2 of the pre-dryer and the low-value gas incinerator The feed port of the raw coal bunker 20 is connected, the discharge port of the raw coal bunker 2 of the pre-dryer is connected with the feed port of the feeder 3, and the discharge port of the feeder 3 is connected with the feed port of the pre-dryer 4. The feed port ends are connected, the air outlet end of the blower 6 is connected with the air inlet end of the low-value gas incinerator air preheater 5, and the air outlet end of the low-value gas incinerator air preheater 5 is connected with the air outlet end of the pre-dryer 4 The air inlet ends are connected, the air outlet of the pre-dryer 4 is connected with the inlet end of the cyclone separator 7, the air outlet end of the cyclone separator 7 is connected with the inlet end of the dust collector 8, and the discharge port of the cyclone separator 7 The outlet end of the dust collector 8 is connected with the inlet end of the induced draft fan 9, and the material outlet end of the dust collector 8 is connected with the feed port end of the
半成品仓10的出料口端与给料机11的进料口端相连接,给料机11的出料口端与流化床轻度气化褐煤提质反应器12的进料口端相连接,流化床轻度气化褐煤提质反应器12的粗颗粒成品出料口端与粗颗粒成品冷却器13的进料口端相连接,粗颗粒成品冷却器13的出料口端与粗颗粒成品仓14的进料口端相连接;流化床轻度气化褐煤提质反应器12的烟气出口端与旋风分离器19的烟气进口端相连接,旋风分离器19的出风口端与低值燃气焚烧炉22的低值燃气入口端相连接,旋风分离器19的出料口端与细颗粒成品冷却器18的入料口端相连接,细颗粒成品冷却器18的出料口端与细颗粒成品仓17的进料口端相连接;送风机16的出风口端与低值燃气焚烧炉空气预热器15的进风口端相连接,低值燃气焚烧炉空气预热器15的出风口端与流化床轻度气化褐煤提质反应器12的风室相连接。The discharge port end of the
原煤仓(20)的出料口端与给料机21的进料口端相连接,给料机21的出料口端与低值燃气焚烧炉22的进料口端相连接,低值燃气焚烧炉22的烟气出口与旋风分离器24的进口端相连接,旋风分离器24的出风口端与尾部烟道32的进口端相连接,尾部烟道32的出口端与除尘器29的进口端相连接,除尘器29的出口端与引风机30的进口端相连接,引风机30的出口端与烟囱31的进口端相连接;低值燃气焚烧炉22的出渣口端与冷渣器25的进口端相连接;送风机27的出风口端与低值燃气焚烧炉22的空气预热器26的进风口端相连接,空气预热器26的出风口端与低值燃气焚烧炉22的风室相连接;石灰石系统23的出料口端与低值燃气焚烧炉22的返料器斜管相连接;罗茨风机28的出风口与低值燃气焚烧炉22的返料器底部风室相连接。The discharge port end of the raw coal bunker (20) is connected with the feed port end of the feeder 21, and the discharge port end of the feeder 21 is connected with the feed port end of the low-value gas incinerator 22, and the low-value gas The flue gas outlet of the incinerator 22 is connected to the inlet end of the cyclone separator 24, the air outlet end of the cyclone separator 24 is connected to the inlet end of the tail flue 32, and the outlet end of the tail flue 32 is connected to the inlet of the dust collector 29. The outlet end of dust collector 29 is connected with the inlet end of induced draft fan 30, and the outlet end of induced draft fan 30 is connected with the inlet end of chimney 31; the slag outlet end of low-value gas incinerator 22 is connected with slag cooler The inlet end of 25 is connected; the air outlet end of blower 27 is connected with the air inlet end of the air preheater 26 of low value gas incinerator 22, and the air outlet end of air preheater 26 is connected with the air outlet end of low value gas incinerator 22 The air chamber is connected; the discharge port of the
参见附图,本发明的整体流化床轻度气化褐煤提质工艺是:褐煤经过破碎筛分系统1破碎到小于50mm粒度的颗粒后,输送进入原煤仓2和原煤仓20,褐煤从原煤仓2的出料口由给料机3控制进入预干燥器4,高温空气通过预干燥器4之后,温度降到100℃以下,经过尾部的旋风分离器7分离后,送入除尘器8,经除尘器8把大部分固体颗粒脱除后直接由引风机9排空,由旋风分离器7和除尘器8捕集下来的细粉送入半成品仓10;Referring to the accompanying drawings, the integral fluidized bed mild gasification lignite upgrading process of the present invention is: after the lignite is broken into particles less than 50 mm in size through the crushing and screening system 1, it is transported into the raw coal bunker 2 and the raw coal bunker 20, and the lignite is extracted from the raw coal The outlet of bin 2 is controlled by the feeder 3 and enters the pre-dryer 4. After the high-temperature air passes through the pre-dryer 4, the temperature drops below 100°C. After being separated by the cyclone separator 7 at the tail, it is sent to the dust collector 8. After most of the solid particles are removed by the dust collector 8, it is directly emptied by the induced draft fan 9, and the fine powder captured by the cyclone separator 7 and the dust collector 8 is sent into the
半成品仓10中的预干燥煤经由给料机11给入流化床轻度气化褐煤提质反应器12进行深度提质,预干燥煤在流化床轻度气化褐煤提质反应器12内经热空气流化后,在流化床轻度气化褐煤提质反应器12内发生轻度气化、燃烧、干馏反应,褐煤中的全部水分被释放到烟气中,流化床轻度气化褐煤提质反应器12的温度由褐煤发生的化学反应产生的热量来维持。The pre-dried coal in the
经深度提质,会产生两种不同粒径的提质褐煤,即粗颗粒成品与细颗粒成品,其中粗颗粒成品由流化床轻度气化褐煤提质反应器12底部的排料口排入粗颗粒成品冷却器13,经冷却至温度低于75℃后送入粗颗粒成品仓14;烟气携带的一部分细颗粒成品经由旋风分离器19分离后,大部分被分离下来,由旋风分离器19下部的排料口排入细颗粒成品冷却器18,经冷却至温度低于75℃后送入细颗粒成品仓17。After deep upgrading, two kinds of upgraded lignite with different particle sizes will be produced, i.e. coarse-grained finished product and fine-grained finished product, wherein the coarse-grained finished product is discharged from the discharge port at the bottom of the fluidized bed mild gasification lignite upgrading reactor 12. into the coarse particle finished product cooler 13, and after being cooled to a temperature lower than 75°C, it is sent to the coarse particle finished product bin 14; a part of the fine particle finished product carried by the flue gas is separated by the
由流化床轻度气化褐煤提质反应器12排出的低值燃气经旋风分离器19除去大部分煤粉后送入低值燃气焚烧炉22焚烧利用;低值燃气焚烧炉22为一炉膛绝热的循环流化床锅炉,通过补燃部分固体燃料和添加石灰石来实现低值燃气的充分燃烧和降低污染物(SO2)的排放;低值燃烧焚烧炉22产生的高温烟气经由布置在尾部烟道32内的空气预热器5、15、26换热冷却后经除尘器29出城后,由引风机30送入烟囱31排空;冷风被送入空气预热器5、15、26换热升温后送至预干燥器4、流化床轻度气化褐煤提质反应器12和低值燃气焚烧炉22利用。The low-value gas discharged from the fluidized bed mild gasification lignite upgrading reactor 12 is sent to the low-value gas incinerator 22 for incineration after the
预干燥器4内的流化速度控制在1.0~6.0m/s之间,温度控制在20~90℃之间。The fluidization velocity in the pre-dryer 4 is controlled between 1.0-6.0 m/s, and the temperature is controlled between 20-90°C.
流化床轻度气化褐煤提质反应器12内的流化速度控制在1.0~6.0m/s之间,主反应区的温度控制在300℃~700℃之间。The fluidization velocity in the fluidized bed mild gasification lignite upgrading reactor 12 is controlled between 1.0-6.0 m/s, and the temperature of the main reaction zone is controlled between 300°C and 700°C.
经提质的褐煤,其水分最终可以控制到<10%。The water content of the upgraded lignite can be controlled to <10%.
附图中,1为破碎筛分系统;2为原煤仓;3为给料机;4为预干燥器;5为空气预热器;6为送风机;7为旋风分离器;8为除尘器;9为引风机;10为半成品仓;11为给料机;12为流化床轻度气化褐煤提质反应器;13为粗颗粒成品冷却器;14为粗颗粒成品仓;15为空气预热器;16为送风机;17为细颗粒成品仓;18为细颗粒成品冷却器;19为旋风分离器;20为原煤仓;21为给料机;22为低值燃气焚烧炉;23为石灰石系统;24为旋风分离器;25为冷渣器;26为空气预热器;27为送风机;28为罗茨风机;29为除尘器;30为引风机;31为烟囱;32为尾部烟道。In the accompanying drawings, 1 is a crushing and screening system; 2 is a raw coal bunker; 3 is a feeder; 4 is a pre-dryer; 5 is an air preheater; 6 is a blower; 7 is a cyclone separator; 8 is a dust collector; 9 is an induced draft fan; 10 is a semi-finished product warehouse; 11 is a feeder; 12 is a fluidized bed light gasification lignite upgrading reactor; 13 is a coarse particle finished product cooler; 14 is a coarse particle finished product warehouse; Heater; 16 is air blower; 17 is fine particle product warehouse; 18 is fine particle product cooler; 19 is cyclone separator; 20 is raw coal bunker; 21 is feeder; 22 is low-value gas incinerator; 23 is limestone 24 is cyclone separator; 25 is slag cooler; 26 is air preheater; 27 is blower; 28 is Roots fan; 29 is dust collector; 30 is induced draft fan; 31 is chimney; 32 is tail flue .
Claims (9)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2009102191271A CN101818092B (en) | 2009-11-25 | 2009-11-25 | Integrated fluidized bed mild-gasification lignite upgrading system and technology |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2009102191271A CN101818092B (en) | 2009-11-25 | 2009-11-25 | Integrated fluidized bed mild-gasification lignite upgrading system and technology |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN101818092A CN101818092A (en) | 2010-09-01 |
| CN101818092B true CN101818092B (en) | 2012-11-21 |
Family
ID=42653372
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN2009102191271A Active CN101818092B (en) | 2009-11-25 | 2009-11-25 | Integrated fluidized bed mild-gasification lignite upgrading system and technology |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN101818092B (en) |
Families Citing this family (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102506575B (en) * | 2011-09-21 | 2014-06-18 | 千秋能源(上海)有限公司 | Treatment process for lignite upgrading waste water and lignite upgrading system |
| CN102925179B (en) * | 2012-11-26 | 2014-04-02 | 北京碧瑞能科技发展有限公司 | Lignite complete cycle high-efficiency dry distillation quality improving system and method |
| CN104610991A (en) * | 2015-01-27 | 2015-05-13 | 西澳大学 | Coal-fired power plant and low-rank coal upgrading integrated system and comprehensive utilization of upgraded product |
| CN106765204A (en) * | 2016-12-29 | 2017-05-31 | 安徽今朝环保科技有限公司 | A kind of abraum salt annealing device |
| CN106766683A (en) * | 2016-12-29 | 2017-05-31 | 安徽今朝环保科技有限公司 | A kind of floated abraum salt annealing device |
| CN106765205A (en) * | 2016-12-29 | 2017-05-31 | 安徽今朝环保科技有限公司 | A kind of abraum salt drying and incinerating purifier based on injection rotary drying |
| CN106766682A (en) * | 2016-12-29 | 2017-05-31 | 安徽今朝环保科技有限公司 | A kind of abraum salt drying and incinerating purifier based on radiation rotary drying |
| CN107227174A (en) * | 2017-07-18 | 2017-10-03 | 枣庄学院 | A kind of Novel brown coal gasification system and method |
| CN107892950A (en) * | 2017-11-08 | 2018-04-10 | 中科合肥煤气化技术有限公司 | A kind of high temperature heating gas waste-heat recovery device |
| CN108940135B (en) * | 2018-06-20 | 2019-10-15 | 东南大学 | Multi-stage temperature difference frequency vibratory fluidization system and method for oxidizing and non-melting coal tar pitch pellets |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101412930A (en) * | 2008-10-28 | 2009-04-22 | 西安热工研究院有限公司 | Quality improving reaction device for high-moisture solid fuel and process thereof |
-
2009
- 2009-11-25 CN CN2009102191271A patent/CN101818092B/en active Active
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101412930A (en) * | 2008-10-28 | 2009-04-22 | 西安热工研究院有限公司 | Quality improving reaction device for high-moisture solid fuel and process thereof |
Non-Patent Citations (2)
| Title |
|---|
| 整体流化床式轻度气化褐煤提质技术研究;肖平等;《2009年清洁高效燃煤发电技术协作网年会》;20091031;1-6 * |
| 肖平等.整体流化床式轻度气化褐煤提质技术研究.《2009年清洁高效燃煤发电技术协作网年会》.2009,1-6. |
Also Published As
| Publication number | Publication date |
|---|---|
| CN101818092A (en) | 2010-09-01 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101818092B (en) | Integrated fluidized bed mild-gasification lignite upgrading system and technology | |
| CN102798133B (en) | Fan grinding hot blast powder feeding and pulverizing system utilizing flue gas drying and water recycling | |
| CN202229208U (en) | Furnace smoke drying and water recycling warehouse-type fan mill hot air powder supplying and making system | |
| CN102889608B (en) | Direct fired pulverizing system of smoke pre-drying lignite fan mill | |
| CN102798134B (en) | Furnace smoke drying and water recycling warehouse-type fan mill hot air powder supplying and making system | |
| CN102533296B (en) | Oil shale rotary kiln dry distillation and circulating fluidized bed combustion process | |
| CN101476814A (en) | Low-rank coal drying method and system | |
| CN102798132A (en) | Fan mill front counter flow type furnace-smoke drying dewatering direct blowing pulverization system | |
| CN103604121B (en) | Adopt the oil shale semi-coke fluidized bed combustion syste of triple channel flow-dividing control material returning device | |
| CN101412930B (en) | Quality improving reaction device for high-moisture solid fuel and process thereof | |
| CN101117584A (en) | Integrated process of oil shale dry distillation refining and semi-coke combustion power generation | |
| CN101717681A (en) | Solid fuel upgrading reaction device and process thereof | |
| CN115899676B (en) | A device and method for the resource utilization and combustion of low-calorific-value fuels | |
| CN103528342A (en) | Coal slime drying system and coal slime drying process | |
| CN102759118A (en) | Lignite drum smoke pre-drying power generation integrated system and process | |
| CN203534059U (en) | Coal slime drying system | |
| JP2017040414A (en) | Biomass utilization method and apparatus | |
| CN202132964U (en) | Counterflow Fume Drying and Dehydration Direct Blowing Powder Milling System Before Fan Grinding | |
| CN102889606A (en) | Direct fired pulverizing system of smoke pre-drying lignite steel ball mill | |
| CN201046952Y (en) | A circulating fluidized bed coal gasification device | |
| CN103409156B (en) | Heat carrier destructive distillation system for coal and method thereof | |
| CN218001483U (en) | Low-calorific-value fuel resource combustion utilization device | |
| CN116293703A (en) | Multi-furnace forward and reverse combination staged gasification combustion furnace | |
| CN202132966U (en) | Smoke-predrying fan mill direct blowing type powder making system for brown coal | |
| CN205590629U (en) | Biomass gasification device and system |
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 |
