JPS63159589A - Apparatus for burning alkali pulp waste liquid - Google Patents
Apparatus for burning alkali pulp waste liquidInfo
- Publication number
- JPS63159589A JPS63159589A JP30376286A JP30376286A JPS63159589A JP S63159589 A JPS63159589 A JP S63159589A JP 30376286 A JP30376286 A JP 30376286A JP 30376286 A JP30376286 A JP 30376286A JP S63159589 A JPS63159589 A JP S63159589A
- Authority
- JP
- Japan
- Prior art keywords
- combustion furnace
- waste liquid
- fluidized bed
- iron oxide
- circulating fluidized
- 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.)
- Pending
Links
- 239000007788 liquid Substances 0.000 title claims description 19
- 239000002699 waste material Substances 0.000 title claims description 19
- 239000003513 alkali Substances 0.000 title claims description 14
- 238000002485 combustion reaction Methods 0.000 claims description 62
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 claims description 58
- 239000002245 particle Substances 0.000 claims description 43
- 238000010411 cooking Methods 0.000 claims description 15
- 238000000034 method Methods 0.000 claims description 9
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 7
- 238000009993 causticizing Methods 0.000 claims description 7
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 6
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 claims description 5
- 239000000567 combustion gas Substances 0.000 claims description 5
- 238000011084 recovery Methods 0.000 claims description 5
- 229910052708 sodium Inorganic materials 0.000 claims description 5
- 239000011734 sodium Substances 0.000 claims description 5
- 229910000462 iron(III) oxide hydroxide Inorganic materials 0.000 claims description 3
- 235000011121 sodium hydroxide Nutrition 0.000 claims description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 2
- 238000006243 chemical reaction Methods 0.000 description 14
- 238000001816 cooling Methods 0.000 description 5
- 238000010586 diagram Methods 0.000 description 4
- 238000009826 distribution Methods 0.000 description 4
- 239000002655 kraft paper Substances 0.000 description 4
- 239000007789 gas Substances 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- 239000002912 waste gas Substances 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 239000006185 dispersion Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 235000019645 odor Nutrition 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 238000004537 pulping Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 229910000272 alkali metal oxide Inorganic materials 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000003518 caustics Substances 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 239000011362 coarse particle Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 230000003134 recirculating effect Effects 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
Landscapes
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
- Paper (AREA)
Abstract
(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明はアルカリパルプ蒸解廃液を燃焼してソーダ及び
熱を回収するアルカリパルプ蒸解廃液燃焼装置に関する
。DETAILED DESCRIPTION OF THE INVENTION [Industrial Field of Application] The present invention relates to an alkaline pulp cooking waste liquid combustion apparatus for recovering soda and heat by burning the alkaline pulp cooking waste liquid.
従来のパルプ製造法はクラフトパルプが主流であるが、
クラフトパルプ化法は悪臭などの公害発生の完全な解決
が難しいことと共に、経済面においても石灰焼成キルン
での重油の消費があシ、かつ得られる白液濃度が低く、
シかも燃焼装置に設置した回収ボイラの蒸気条件に制限
があることなどから、パルプ工場での熱利用面での効率
化はほぼ限界に近づいている。直接苛性化法はこの限界
をこえて悪臭公害がなくかつ効率、経済面でクラフトパ
ルプ化法を凌駕し、パルプ品質はクラフトパルプに匹敵
するものを作シうる可能性があるため各方面で研究開発
が進められている。The traditional pulp manufacturing method is kraft pulp, but
The kraft pulping method is difficult to completely eliminate pollution such as bad odors, and from an economic perspective, heavy oil is consumed in the lime kiln, and the resulting white liquor concentration is low.
Due to limitations on the steam conditions of the recovery boiler installed in the Shikamo combustion equipment, efficiency improvements in terms of heat utilization at pulp mills are almost reaching their limits. The direct causticization method overcomes this limit and is free from odor pollution, surpasses the kraft pulping method in terms of efficiency and economy, and has the potential to produce pulp comparable in quality to kraft pulp, so it is being researched in various fields. Development is underway.
この従来の直接苛性化法を実施する循環流動床燃焼装置
の構成図を第2図に示す。A configuration diagram of a circulating fluidized bed combustion apparatus for carrying out this conventional direct causticizing method is shown in FIG.
下方に空気分散板aを内装し、かつ、空気分散板aよシ
も上方の側壁にアルカリパルプ蒸解廃液(以下、黒液と
略記する)投入口す及び酸化鉄粒子投入口Cと、下端部
に空気投入口dとが配設された循環流動未燃床炉本体e
は、上端部が配管を介してサイクロンfVc接続されて
いる。サイクロンfの上端部は燃焼排ガス出口gへ接続
し、又下端部は移送管りへ接続されている0なお、移送
管りは一方が循環流動床燃焼炉本体・の空気分散板aよ
シも上方の位置に接続された粒子投入口IK他方が生成
物取り出し口jへ導く配管に分枝している〇
黒液と酸化鉄粒子は、それぞれの黒液投入口す及び酸化
鉄粒子投入口Cから循環流動床燃焼炉本体8に投入され
、炉底部の空気投入口dから供給され空気分散板a#/
cよって分散供給される空気によシ、高温の循環流動床
燃焼炉本体eの内部で燃焼し、同時に黒液中のアルカリ
は酸化鉄に捕捉され、一部は反応して反応生成物である
鉄酸ソーダを生成する。反応及び未反応の酸化鉄粒子は
燃焼ガスとともに循環流動床燃焼炉本体eから排出し、
サイクロンfによ)補集され循環系統を通って粒子投入
口1から再び循環流動床燃焼炉本体eに戻される。粒子
循環系統から一部の粒子が生成物取り出し口jから系外
に出される。即ち、この形式の燃焼炉においては、黒液
の燃焼と黒液中アルカリの酸化鉄粒子表面への捕捉、捕
捉したアルカリと酸化鉄との反応の王者、即ち、燃焼、
捕捉、反応が循環流動床燃焼炉本体eの中で行なわれる
。An air dispersion plate a is installed in the lower part, and an alkaline pulp cooking waste liquid (hereinafter abbreviated as black liquor) inlet C and an iron oxide particle inlet C are installed in the upper side wall of the air dispersion plate A, and the lower end thereof A circulating fluidized unburnt bed furnace body e, which is provided with an air inlet d and an air inlet d.
The upper end is connected to the cyclone fVc via piping. The upper end of the cyclone f is connected to the flue gas outlet g, and the lower end is connected to the transfer pipe.The transfer pipe has one side connected to the air distribution plate a of the circulating fluidized bed combustion furnace main body. The particle inlet IK connected to the upper position and the other branch to the piping leading to the product outlet j. Black liquor and iron oxide particles are transferred to the respective black liquor inlet and iron oxide particle inlet C. The air is introduced into the circulating fluidized bed combustion furnace main body 8, and is supplied from the air inlet d at the bottom of the furnace to the air distribution plate a#/
c, the black liquor is burned inside the high-temperature circulating fluidized bed combustion furnace main body e by the dispersed air supplied, and at the same time, the alkali in the black liquor is captured by iron oxide, and some of it reacts and becomes a reaction product. Produces sodium ferrate. Reacted and unreacted iron oxide particles are discharged from the circulating fluidized bed combustion furnace body e along with the combustion gas,
The particles are collected by the cyclone f) and returned to the circulating fluidized bed combustion furnace main body e through the particle inlet 1 through the circulation system. Some of the particles from the particle circulation system are taken out of the system through the product outlet j. That is, in this type of combustion furnace, the combustion of black liquor, the capture of alkali in the black liquor on the surface of iron oxide particles, and the reaction between the captured alkali and iron oxide are the two main processes.
The capture and reaction takes place in the circulating fluidized bed combustion furnace body e.
従来の装置では、上記黒液の燃焼、アルカリの捕捉、ア
ルカリと酸化鉄との反応(以下苛性化反応という)のう
ち、特に反応上の問題から使用する酸化鉄の粒径に制限
を受ける。循環流動床では燃焼炉内のガス流速は5〜1
0 m / 8のようKかなシ速く、燃焼炉内のガスの
滞留時間はせいぜい1〜3秒程度である。酸化鉄粒子が
この程度の滞留時間で燃焼ガスと共に燃焼炉を飛び出し
たのでは、酸化鉄とアルカリから鉄酸ソーダを作る苛性
化反応は酸化鉄の粒径にもよるがかなシ遅く反応が完結
しない。そこで燃焼炉を飛び出した酸化鉄粒子を再度燃
焼炉に循環させるとともに1酸化鉄粒子の粒径として2
00〜500ミクロン程度のやや粗い粒子を用い、燃焼
炉内における粒子の重力落下を利用して高温の燃焼炉内
における酸化鉄粒子の滞留時間を長くするなどの工夫を
行っている。In the conventional apparatus, the particle size of the iron oxide used is limited due to problems in the combustion of the black liquor, the capture of the alkali, and the reaction between the alkali and the iron oxide (hereinafter referred to as causticizing reaction). In a circulating fluidized bed, the gas flow rate in the combustion furnace is between 5 and 1
The gas velocity in the combustion furnace is as fast as 0 m/8, and the residence time of the gas in the combustion furnace is about 1 to 3 seconds at most. If the iron oxide particles flew out of the combustion furnace together with the combustion gas within this residence time, the causticizing reaction to create ferric acid soda from iron oxide and alkali would be slow and complete, depending on the particle size of the iron oxide. do not. Therefore, the iron oxide particles that flew out of the combustion furnace are recirculated to the combustion furnace, and the particle size of 1 iron oxide particle is 2.
Slightly coarse particles of about 0.00 to 500 microns are used, and the residence time of the iron oxide particles in the high-temperature combustion furnace is lengthened by utilizing the gravitational fall of the particles in the combustion furnace.
その一つの工夫として、反応に必要な滞留時間を稼ぐ手
段として、燃焼炉出口に設置したサイクロンで捕集した
粒子を高温に保持する装置、すなわちアルカリパルプ蒸
解廃液と共に酸化鉄粉末を吹き込んで燃焼させ熱及び前
記アルカリパルプ蒸解廃液中のアルカリな鉄酸ソーダと
して回収する流動床燃焼炉、同流動床燃焼炉からの燃焼
廃ガスに伴われる固体粉末を捕集するサイクロンを備え
たアルカリパルプ蒸解廃液回収装置において、前記サイ
クロンの下流に前記サイクロンで捕集した固体粉末を高
温、高酸素雰囲気に保つ流動床反応炉を配設したことを
特徴とするアルカリパルプ蒸解廃液回収装置を提案(特
願昭60−115347号)したが、サイクロン出口で
950〜1000°0の高温を保つ必要があった。すな
わち、この先に提案した装置ではサイクロンの下流に設
けた流動床反応炉によってサイクロンで捕集した粒子を
高温に保ち未燃炭素を燃焼させ反応を進める必要があっ
た。As a means of gaining the residence time necessary for the reaction, one device is a device that maintains the particles collected by a cyclone installed at the outlet of the combustion furnace at a high temperature.In other words, iron oxide powder is injected and combusted together with the alkaline pulp cooking waste liquid. Alkaline pulp cooking waste liquid recovery equipped with a fluidized bed combustion furnace that recovers heat and alkaline ferric acid sodium from the alkaline pulp cooking waste liquid, and a cyclone that collects solid powder accompanying combustion waste gas from the fluidized bed combustion furnace. An alkali pulp cooking waste liquid recovery apparatus was proposed, characterized in that a fluidized bed reactor was disposed downstream of the cyclone to maintain a high temperature and high oxygen atmosphere for the solid powder collected by the cyclone (Japanese Patent Application No. 1983). -115347), but it was necessary to maintain a high temperature of 950 to 1000°0 at the cyclone outlet. In other words, in the previously proposed device, it was necessary to maintain the particles collected by the cyclone at a high temperature in a fluidized bed reactor installed downstream of the cyclone to burn unburned carbon and proceed with the reaction.
本発明は従来及び先に提案の直接苛性法を実施する装置
の欠点を解消し得て、酸化鉄粒子の滞留時間を長くする
ことができる簡単な構造の黒液の燃焼装置を提供しよう
とするものである。The present invention seeks to provide a black liquor combustion device with a simple structure that can overcome the drawbacks of the conventional and previously proposed devices implementing the direct caustic method and can increase the residence time of iron oxide particles. It is something.
本発明の黒液燃焼装置は、酸化鉄粒子とアルカリの反応
を十分進めるため、循環流動床燃焼炉本体上部の燃焼炉
断面積を大きくし燃焼ガス流速を低下させて燃焼炉内で
の酸化鉄粒子の保持量を増すことで、粒子の該燃焼炉内
での滞留時間を増し反応率を改善し得るようKしたもの
である。In order to sufficiently promote the reaction between iron oxide particles and alkali, the black liquor combustion device of the present invention increases the cross-sectional area of the combustion furnace at the top of the circulating fluidized bed combustion furnace main body and reduces the flow rate of combustion gas, thereby reducing the amount of iron oxide in the combustion furnace. By increasing the amount of particles retained, the residence time of the particles in the combustion furnace is increased and the reaction rate is improved.
すなわち、本発明はアルカリパルプ蒸解廃液をソーダ回
収ボイラで燃焼して熱及びソーダを回収するに際し、上
記アルカリパルプ蒸解廃液と共に酸化鉄粒子を燃焼炉に
供給し、上記アルカリパルプ蒸解廃液中のアルカリを鉄
酸ソーダとして上記燃焼炉外に取り出し、熱水抽出して
苛性ソーダを回収するいわゆる直接苛性化法に用いる循
環流動床燃焼炉において、燃焼ガス流速が速く炉断面積
が小さい炉底部をもち、その上部に炉断面積を大きくし
た上記循環流動床燃焼炉本体を備えてなることを特徴と
するアルカリパルプ蒸解廃液燃焼装置である。That is, when the present invention burns the alkaline pulp cooking waste liquid in a soda recovery boiler to recover heat and soda, iron oxide particles are supplied to the combustion furnace together with the alkaline pulp cooking waste liquid, and the alkali in the alkaline pulp cooking waste liquid is recovered. In a circulating fluidized bed combustion furnace used for the so-called direct causticizing method, in which sodium ferrate is taken out of the combustion furnace and caustic soda is recovered by extraction with hot water, the furnace bottom has a high combustion gas flow rate and a small furnace cross-sectional area. This is an alkaline pulp cooking waste liquid combustion apparatus characterized in that the above-mentioned circulating fluidized bed combustion furnace main body with a large furnace cross-sectional area is provided in the upper part.
本発明に係る一実施例である循環流動床燃焼装置の構成
図を第1図によって説明する。A configuration diagram of a circulating fluidized bed combustion apparatus which is an embodiment of the present invention will be explained with reference to FIG.
第1図において、1は循環流動床燃焼炉本体、2は循環
流動床燃焼炉本体1の下部を構成する炉底部、3は空気
投入口、4は燃焼空気の均圧室、5は循環流動床燃焼炉
1下部の空気分散板、6は黒液投入口、7は酸化鉄粒子
投入口、8は換
燃焼炉出口に配設された熱交器、9は熱交換器△
出口に隣接するサイクロン、10は燃焼廃ガス出口、1
1は熱交換器8及びサイクロン9で捕集された捕集粒子
の冷却装置、12は熱交換器8及びサイクロン9で捕集
された粒子を冷却装置11に送る移送管、13は冷却装
置11から粒子を循環流動床燃焼炉本体1の炉底部2へ
再循環させる連接管、14は循環流動床燃焼炉本体1か
らの反応粒子取出口である。In Fig. 1, 1 is the circulating fluidized bed combustion furnace main body, 2 is the furnace bottom constituting the lower part of the circulating fluidized bed combustion furnace main body 1, 3 is the air inlet, 4 is the pressure equalization chamber for combustion air, and 5 is the circulating fluidized bed combustion furnace. Air distribution plate at the bottom of the bed combustion furnace 1, 6 is a black liquor inlet, 7 is an iron oxide particle inlet, 8 is a heat exchanger installed at the exchange combustion furnace outlet, 9 is a heat exchanger △ adjacent to the outlet Cyclone, 10 is combustion waste gas outlet, 1
1 is a cooling device for the collected particles collected by the heat exchanger 8 and the cyclone 9; 12 is a transfer pipe that sends the particles collected by the heat exchanger 8 and the cyclone 9 to the cooling device 11; and 13 is a cooling device 11. A connecting pipe 14 for recirculating the particles from the reactor to the furnace bottom 2 of the circulating fluidized bed combustion furnace main body 1 is an outlet for taking out reactive particles from the circulating fluidized bed combustion furnace main body 1.
黒液は酸化鉄粒子と共にそれぞれ黒液投入口6及び酸化
鉄粒子投入ロアから循環流動床燃焼炉本体1に投入され
、炉底の空気投入口3がら空気分散板5を経て供給され
る空気によシ、高温の循環流動床燃焼炉本体1及び炉底
部2で燃焼する。同時に黒液中のアルカリは酸化鉄粒子
に捕捉され、一部は反応して鉄酸ソーダを生成する。反
応及び未反応の酸化鉄粒子及びごく一部の未燃焼炭素粒
子は燃焼廃ガスとともに循環流動床燃焼炉本体1から排
出し、熱交換器8、サイクロン9によシ捕集され、移送
管12を通って下部の冷却装置11に落下する。冷却装
置11で冷却された粒子は連接管13から炉底部2に供
給される。これらの循環粒子は循環流動床燃焼炉本体1
の温度を均一に保ち廃液を安定に燃焼させると共に1廃
液の燃焼に際して廃液 −中のアルカリを酸化鉄粒子に
捕捉するのく役立つ。反応粒子取出口14から循環流動
床燃焼炉本体1外に排出された粒子は次の苛性化工程に
送られる。The black liquor is introduced into the circulating fluidized bed combustion furnace body 1 together with the iron oxide particles through the black liquor inlet 6 and the iron oxide particle inlet lower, respectively, and the air is supplied through the air distribution plate 5 from the air inlet 3 at the bottom of the furnace. The combustion occurs in the high-temperature circulating fluidized bed combustion furnace main body 1 and furnace bottom 2. At the same time, the alkali in the black liquor is captured by iron oxide particles, and some of it reacts to form sodium ferrate. Reacted and unreacted iron oxide particles and a small portion of unburned carbon particles are discharged from the circulating fluidized bed combustion furnace main body 1 together with combustion waste gas, collected by a heat exchanger 8 and a cyclone 9, and transferred to a transfer pipe 12. and falls to the cooling device 11 at the bottom. The particles cooled by the cooling device 11 are supplied to the furnace bottom 2 from the connecting pipe 13. These circulating particles are transferred to the circulating fluidized bed combustion furnace main body 1.
It maintains a uniform temperature and stably burns the waste liquid, and also serves to capture the alkali in the waste liquid into iron oxide particles when the waste liquid is burned. The particles discharged from the reactant particle outlet 14 to the outside of the circulating fluidized bed combustion furnace main body 1 are sent to the next causticizing step.
本発明の装置によシ次のような効果が期待できる。 The following effects can be expected from the apparatus of the present invention.
+1) 高温の燃焼炉内における酸化鉄粒子の滞留時
間を長くでき、苛性化反応の反応率が高くなる。反応率
が高く維持できれば不純物としての炭酸ソーダ及び未反
応の酸化鉄が少なくなり熱経済が良くなる。+1) The residence time of iron oxide particles in the high-temperature combustion furnace can be extended, and the reaction rate of the causticizing reaction can be increased. If the reaction rate can be maintained high, soda carbonate and unreacted iron oxide as impurities will be reduced, resulting in better thermal economy.
(2) 先に提案した発明(特願昭60−11534
7号)のようにサイクロン捕集粒子を高温に保つ方法に
比べて、反応に必要な高温部分を燃焼炉内に限定できる
ので装置が簡略化される。また循環流動床燃焼炉本体出
口は反応に必要な高温に保つ必要がなく、燃焼条件の余
裕が大きくなシ操作が楽になる。(2) Previously proposed invention (Patent application 11534/1986)
Compared to the method of keeping the cyclone-collected particles at a high temperature as in No. 7), the apparatus is simplified because the high-temperature area necessary for the reaction can be limited to the inside of the combustion furnace. In addition, there is no need to maintain the outlet of the circulating fluidized bed combustion furnace at the high temperature required for the reaction, and there is a large margin in combustion conditions, making operation easier.
第1図は本発明の一実施例である循環流動床燃焼炉の構
成図、第2図は従来装置を示す構成図である。FIG. 1 is a block diagram of a circulating fluidized bed combustion furnace which is an embodiment of the present invention, and FIG. 2 is a block diagram showing a conventional apparatus.
Claims (1)
熱及びソーダを回収するに際し、上記アルカリパルプ蒸
解廃液と共に酸化鉄粒子を燃焼炉に供給し、上記アルカ
リパルプ蒸解廃液中のアルカリを鉄酸ソーダとして上記
燃焼炉外に取り出し、熱水抽出して苛性ソーダを回収す
るいわゆる直接苛性化法に用いる循環流動床燃焼炉にお
いて、燃焼ガス流速が速く炉断面積が小さい炉底部をも
ち、その上部に炉断面積を大きくした上記循環流動床燃
焼炉本体を備えてなることを特徴とするアルカリパルプ
蒸解廃液燃焼装置。When the alkaline pulp cooking waste liquid is burned in a soda recovery boiler to recover heat and soda, iron oxide particles are supplied to the combustion furnace together with the alkaline pulp cooking waste liquid, and the alkali in the alkali pulp cooking waste liquid is converted into the above-mentioned sodium ferric acid. In a circulating fluidized bed combustion furnace used for the so-called direct causticizing method, in which caustic soda is recovered by taking it out of the combustion furnace and extracting it with hot water, it has a bottom part with a small furnace cross-sectional area where the combustion gas flow rate is high, and a furnace cross-sectional area in the upper part. An alkaline pulp cooking waste liquid combustion apparatus comprising the circulating fluidized bed combustion furnace main body having a larger size.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP30376286A JPS63159589A (en) | 1986-12-22 | 1986-12-22 | Apparatus for burning alkali pulp waste liquid |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP30376286A JPS63159589A (en) | 1986-12-22 | 1986-12-22 | Apparatus for burning alkali pulp waste liquid |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS63159589A true JPS63159589A (en) | 1988-07-02 |
Family
ID=17924967
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP30376286A Pending JPS63159589A (en) | 1986-12-22 | 1986-12-22 | Apparatus for burning alkali pulp waste liquid |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS63159589A (en) |
-
1986
- 1986-12-22 JP JP30376286A patent/JPS63159589A/en active Pending
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