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JPH0348127B2 - - Google Patents
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JPH0348127B2 - - Google Patents

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Publication number
JPH0348127B2
JPH0348127B2 JP58033627A JP3362783A JPH0348127B2 JP H0348127 B2 JPH0348127 B2 JP H0348127B2 JP 58033627 A JP58033627 A JP 58033627A JP 3362783 A JP3362783 A JP 3362783A JP H0348127 B2 JPH0348127 B2 JP H0348127B2
Authority
JP
Japan
Prior art keywords
fluidized bed
bed furnace
black liquor
caustic soda
reaction
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.)
Expired - Lifetime
Application number
JP58033627A
Other languages
Japanese (ja)
Other versions
JPS59162129A (en
Inventor
Hayamizu Ito
Chiaki Nagai
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Seishi Gijutsu Kenkyu Kumiai
Original Assignee
Seishi Gijutsu Kenkyu Kumiai
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Seishi Gijutsu Kenkyu Kumiai filed Critical Seishi Gijutsu Kenkyu Kumiai
Priority to JP58033627A priority Critical patent/JPS59162129A/en
Publication of JPS59162129A publication Critical patent/JPS59162129A/en
Publication of JPH0348127B2 publication Critical patent/JPH0348127B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P70/00Climate change mitigation technologies in the production process for final industrial or consumer products
    • Y02P70/10Greenhouse gas [GHG] capture, material saving, heat recovery or other energy efficient measures, e.g. motor control, characterised by manufacturing processes, e.g. for rolling metal or metal working

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  • Paper (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、パルプ蒸解廃液(黒液ともいう)か
ら苛性ソーダを効率よく回収する方法にも関する
ものである。
DETAILED DESCRIPTION OF THE INVENTION [Industrial Field of Application] The present invention also relates to a method for efficiently recovering caustic soda from pulp cooking waste liquor (also referred to as black liquor).

〔従来の技術〕[Conventional technology]

従来、木材チツプを蒸解したときに発生するパ
ルプ蒸解廃液(以下、パルプ廃液という)から苛
性ソーダを回収する場合、石灰法が実用化されて
いる。しかしこの石灰法は工程が複雑であり、ま
た廃物を生じるので臭気対策、排水対策が必要で
あり、苛性化率が悪いなどの欠点を有していた。
Conventionally, the lime method has been put into practical use when recovering caustic soda from pulp cooking waste liquor (hereinafter referred to as pulp waste liquor) generated when wood chips are digested. However, this lime method has drawbacks such as a complicated process, the production of waste, which requires measures against odor and drainage, and a poor causticization rate.

これらの欠点を解消するために、特公昭51−
12724号公報に示されるように、繊維素物質の蒸
解および漂白工程より排出される実質的に硫黄化
合物を含まないアルカリ廃液を、濃縮後酸化鉄を
加えて燃焼せしめ、得られた鉄酸ソーダを水中に
投入して抽出水溶液として直接苛性ソーダを回収
するとともに、抽出残渣として得られた酸化鉄を
循環再使用する方法が提案されている。この方法
では、アルカリ廃液からの苛性ソーダの生成は、
おそらく廃液の燃焼によつて廃液中に含まれてい
た有機物は分解し、生成物として得られた炭酸ソ
ーダおよび/または酸化ソーダが下記の(1)式およ
び(2)式の如く酸化鉄と反応して鉄酸ソーダを生成
し、これを水中で処理することによつて(3)式の如
く、苛性ソーダと酸化鉄が得られるものと考えら
れる。
In order to eliminate these shortcomings, the special public
As shown in Publication No. 12724, the alkaline waste liquid, which is substantially free of sulfur compounds, discharged from the process of cooking and bleaching cellulose materials is concentrated, then combusted with the addition of iron oxide, and the resulting sodium ferrate is produced. A method has been proposed in which caustic soda is directly recovered as an extracted aqueous solution by pouring it into water, and the iron oxide obtained as an extraction residue is recycled and reused. In this method, the production of caustic soda from alkaline waste liquid is
The organic matter contained in the waste liquid is probably decomposed by combustion of the waste liquid, and the resulting products, sodium carbonate and/or soda oxide, react with iron oxide as shown in equations (1) and (2) below. It is thought that caustic soda and iron oxide can be obtained as shown in equation (3) by producing sodium ferrate and treating it in water.

Na2CO3+Fe2O3→Na2Fe2O4+CO2 ……(1) Na2O+Fe2O3→Na2Fe2O4 ……(2) Na2Fe2O4+H2O→2NaOH+Fe2O3 ……(3) 〔発明が解決しようとする課題〕 しかし上記の方法を流動床炉に適用するに当た
り、流動床炉下流の集じん機として、砂、砂利な
どの酸化鉄以外の粒状物をろ過材とするグラニユ
ラ方式の集じん機を採用する場合は、加水分散に
供する集じん機捕集の微粉鉄酸ソーダに、摩耗し
たろ過材が含まれ、回収苛性ソーダに不純物が含
まれるという問題があつた。
Na 2 CO 3 +Fe 2 O 3 →Na 2 Fe 2 O 4 +CO 2 ...(1) Na 2 O + Fe 2 O 3 →Na 2 Fe 2 O 4 ...(2) Na 2 Fe 2 O 4 +H 2 O→ 2NaOH + Fe 2 O 3 ...(3) [Problem to be solved by the invention] However, when applying the above method to a fluidized bed furnace, it is necessary to use non-iron oxide materials such as sand and gravel as a dust collector downstream of the fluidized bed furnace. When using a granular type dust collector that uses granular materials as filter media, the fine powdered sodium ferrate collected by the dust collector that is used for hydrodispersion may contain worn filter media, and the recovered caustic soda may contain impurities. There was a problem.

本発明は上記の諸点に鑑みなされたもので、廃
熱を有効に回収することができ、流動床炉内での
反応を効率よく進め得るパルプ廃液から苛性ソー
ダを回収する方法を提供することを目的とするも
のである。
The present invention was made in view of the above points, and an object of the present invention is to provide a method for recovering caustic soda from pulp waste liquid that can effectively recover waste heat and efficiently proceed with the reaction in a fluidized bed furnace. That is.

〔課題を解決するための手段および作用〕[Means and actions for solving the problem]

上記の目的を達成するために、本発明のパルプ
廃液から苛性ソーダを回収する方法は、第1図お
よび第2図を参照して説明すれば、パルプ廃液を
濃縮した後、Fe2O3、TiO2、FeTiO3よりなる群
より選択された物質を苛性化剤として加えて流動
床炉4で燃焼せしめ、ついで生成物を水中に投入
して苛性ソーダおよび苛性化剤を回収する方法に
おいて、 流動床炉4からの排ガスを、苛性化剤の粗粒か
らなるろ過層に導入し通過させて集じん処理し、
排ガスにより予熱されたろ過層の粗粒苛性化剤を
流動床炉4に供給することを特徴としている。
In order to achieve the above object, the method of recovering caustic soda from pulp waste liquid of the present invention will be described with reference to FIGS. 1 and 2. After concentrating pulp waste liquid, Fe 2 O 3 , TiO 2 , FeTiO 3 is added as a causticizing agent and combusted in a fluidized bed furnace 4, and then the product is poured into water to recover caustic soda and the causticizing agent, the method comprising: The exhaust gas from 4 is introduced into a filtration layer made of coarse particles of causticizing agent and passed through it to collect dust.
It is characterized in that the coarse causticizing agent in the filter bed, which has been preheated by exhaust gas, is supplied to the fluidized bed furnace 4.

そして、第1図および第2図に示すように、流
動床炉4下流の集じん機15のろ過材として粗粒
苛性化剤を使用し、予熱された粗粒苛性化剤を流
動床炉4に供給するので廃熱の利用により、流動
床炉での燃焼、反応を効率良く進め得ることがで
きる。
As shown in FIGS. 1 and 2, a coarse causticizing agent is used as a filter material in the dust collector 15 downstream of the fluidized bed furnace 4, and the preheated coarse causticizing agent is transferred to the fluidized bed furnace 4. By using the waste heat, combustion and reactions in the fluidized bed furnace can be carried out efficiently.

〔実施例〕〔Example〕

以下、本発明の実施例を図面に基づいて説明す
る。第1図は本発明の方法を実施する装置の一実
施例を示している。第1図において、希黒液タン
ク1内の希黒液をエバポレータ2に導入し蒸発、
濃縮して濃黒液タンク3に貯留し、この黒液を流
動床炉4へ供給する。この流動床炉4の流動化剤
として、Fe2O3、TiO2、FeTiO3よりなる群より
選択された物質(第1図では一例として品質のよ
い鉄鉱石を苛性化剤として用いる場合を示してい
る)を用いる。濃黒液は流動層内で燃焼し、前記
反応式(1)、(2)の反応が行われる。濃黒液は固形物
50wt%以上となるように濃縮し、反応温度を700
〜1100℃、望ましくは850〜1000℃とする。
Embodiments of the present invention will be described below based on the drawings. FIG. 1 shows an embodiment of an apparatus for carrying out the method of the invention. In FIG. 1, dilute black liquor in a dilute black liquor tank 1 is introduced into an evaporator 2 and evaporated.
The concentrated black liquor is stored in a concentrated black liquor tank 3, and this black liquor is supplied to a fluidized bed furnace 4. As a fluidizing agent for this fluidized bed furnace 4, a material selected from the group consisting of Fe 2 O 3 , TiO 2 , and FeTiO 3 is used (Fig. 1 shows an example in which high-quality iron ore is used as a causticizing agent). ) is used. The thick black liquor is combusted in the fluidized bed, and the reactions of the above-mentioned reaction formulas (1) and (2) take place. Thick black liquor is a solid substance
Concentrate to 50wt% or more, and reduce the reaction temperature to 700%.
~1100°C, preferably 850~1000°C.

ついで流動床炉4における生成物を抜き出し、
冷却器5で冷却した後、加水分解槽6へ導入し水
中に投入して前記反応式(3)の反応を行わせて
NaOHおよびFe2O3を生成させる。このNaOHお
よびFe2O3はクラリフアイヤー7に送られて
NaOHとFe2O3とに分離され、NaOHは苛性ソー
ダタンク8に貯留される。Fe2O3は洗浄槽10、
フイルタ11を経てFe2O3として回収される。こ
のFe2O3は流動床炉4へ供給される。なお12は
純水タンク、13はボイラ、14はガス・エアヒ
ータ、15は集じん機、16は誘引フアン、17
は煙突である。
Then, the product in the fluidized bed furnace 4 is extracted,
After being cooled in a cooler 5, it is introduced into a hydrolysis tank 6 and placed in water to carry out the reaction of the above reaction formula (3).
Generates NaOH and Fe2O3 . This NaOH and Fe 2 O 3 are sent to Clarifair 7.
NaOH and Fe 2 O 3 are separated, and NaOH is stored in a caustic soda tank 8. Fe 2 O 3 is in the cleaning tank 10,
It passes through a filter 11 and is recovered as Fe 2 O 3 . This Fe 2 O 3 is supplied to the fluidized bed furnace 4 . Note that 12 is a pure water tank, 13 is a boiler, 14 is a gas/air heater, 15 is a dust collector, 16 is an induction fan, and 17
is a chimney.

集じん機は粗粒の苛性化剤(第1図の場合は一
例として品質のよい鉄鉱石)を、ルーバ、パンチ
ングメタル、金網などの多孔支持体間に移動可能
に充填した構造のものである。集じん機15から
排出される鉄酸ソーダなどのダストを付着した
Fe2O3は、振動ふるいなどの分級器18に導入さ
れ、鉄酸ソーダおよび微粉のFe2O3と粗粒の
Fe2O3とに分級され、粗粒のFe2O3は流動床炉4
に供給される。微粉は加水分解工程あるいは黒液
との予混合工程において使用することが可能であ
る。
The dust collector has a structure in which coarse-grained causticizing agent (in the case of Figure 1, good quality iron ore) is movably filled between porous supports such as louvers, punched metal, and wire mesh. . Dust such as ferric acid soda discharged from the dust collector 15 is attached.
Fe 2 O 3 is introduced into a classifier 18 such as a vibrating sieve, and is separated from ferric acid soda and fine powder Fe 2 O 3 and coarse powder.
Fe 2 O 3 is classified into Fe 2 O 3 and coarse Fe 2 O 3 is transferred to the fluidized bed furnace 4.
is supplied to The fine powder can be used in the hydrolysis step or in the premixing step with black liquor.

このように本実施例においては、流動床炉4下
流の集じん機15のろ過材として鉄鉱石を使用
し、予熱された鉄鉱石を流動床炉4に供給するの
で廃熱の利用により、流動床炉での燃焼、反応を
効率良く進め得るという利点がある。
In this embodiment, iron ore is used as the filter material for the dust collector 15 downstream of the fluidized bed furnace 4, and since preheated iron ore is supplied to the fluidized bed furnace 4, the waste heat can be used to reduce the flow rate. It has the advantage that combustion and reaction in a bed furnace can proceed efficiently.

第2図は本発明の他の実施例を示している。第
2図において、まず鉄鉱石を苛性化剤として分級
器20に導入して、流動床炉4の流動化剤よりも
粒径の細かい微粉と粗粒とに分級し、微粉を混合
槽21に供給して濃黒液と予め混合した後、この
混合物を流動床炉4に投入して燃焼させ前記反応
式(1)、(2)の反応を行わせる。粗粒は集じん機15
に供給してろ過材として使用する。濃黒液は固形
分50wt%以上となるように濃縮し、FeとNaとの
モル比(Fe/Na)が1以上となるように予混合
する。また流動床炉4における流動化剤は粒径が
0.2〜2.0mmとなるようにし、反応温度を700〜
1100℃、望ましくは850〜1000℃とする。
FIG. 2 shows another embodiment of the invention. In FIG. 2, iron ore is first introduced as a causticizing agent into a classifier 20 and classified into fine powder and coarse particles, which have a particle size smaller than that of the fluidizing agent in the fluidized bed furnace 4, and the fine powder is transferred to a mixing tank 21. After being supplied and premixed with concentrated black liquor, this mixture is charged into the fluidized bed furnace 4 and combusted to carry out the reactions of the above reaction formulas (1) and (2). Dust collector 15 for coarse particles
It is used as a filter material. The concentrated black liquor is concentrated to a solid content of 50 wt% or more, and premixed so that the molar ratio of Fe and Na (Fe/Na) is 1 or more. In addition, the fluidizing agent in the fluidized bed furnace 4 has a particle size of
0.2~2.0mm, and the reaction temperature is 700~
The temperature is 1100°C, preferably 850 to 1000°C.

フイルタ11を経て回収されたFe2O3は、さら
に分級器22に導入されて粗粒と微粉とに分級さ
れ、粗粒は集じん機15へろ過材として供給さ
れ、微粉は混合槽21へ供給される。また集じん
機15から排出される鉄酸ソーダなどダストを付
着したFe2O3は振動ふるいなどの分級器18に導
入され、鉄酸ソーダおよび微粉のFe2O3と粗粒の
Fe2O3とに分級され、粗粒は流動床炉4へ苛性化
剤として供給される。他の構成は第1図の場合と
同様である。
The Fe 2 O 3 recovered through the filter 11 is further introduced into the classifier 22 and classified into coarse particles and fine particles.The coarse particles are supplied to the dust collector 15 as a filter material, and the fine particles are sent to the mixing tank 21. Supplied. In addition, Fe 2 O 3 with dust attached, such as sodium ferrate, discharged from the dust collector 15 is introduced into a classifier 18 such as a vibrating sieve, where it is separated into sodium ferrate and fine Fe 2 O 3 and coarse particles.
The coarse particles are classified into Fe 2 O 3 and fed to the fluidized bed furnace 4 as a causticizing agent. The other configurations are the same as in the case of FIG.

このように本実施例においては、Fe2O3および
黒液の投入を予混合方式とし、混合に使用する
Fe2O3は流動化剤粒径よりも小さい微粉を使用す
るので、微粉Fe2O3単独では流動層に投入して
も、炉外にすぐ飛び出してしまうことを防止し、
かつ燃焼し易い黒液のみを投入する場合に予想さ
れる、流動層に達する前の黒液の燃焼による揮発
分、灰分等の揮発のために、Fe2O3と反応させ回
収すべきNa2Oが損失することを極力抑えること
ができる。なお黒液は流動層内で燃焼させなけれ
ばならない。またFe2O3の比重は4.5〜4.9であり、
珪砂などに比較して約2倍であり、一方、黒液の
みを供給する場合は、黒液は濃縮され固形分濃度
が上昇するに従い比重そのものは大きくなるが、
有機物が揮発して膨潤しやすくなる性質のため
に、見かけの比重は小さくなつて、上昇する燃焼
ガスに対する抵抗力も増加し、流動層内へ至らず
系外にキヤリーオーバーされ易くなり、Na2Oが
損失することになる。また黒液は粘性を有する液
体のため、粒状のFe2O3とは混合し難いが、粉状
のFe2O3とは比較的混合し易く、その混合物は流
動化剤粒径より大きな形(塊状あるいはアメ状)
となるため、炉外への飛び出しはない。また鉄酸
ソーダ(Na2Fe2O4)生成反応は、Fe2O3
Na2CO3との固相反応であり、Fe2O3の反応表面
積の大きいほど(したがつて微粉ほど)、単位容
積当りの反応量は大きくなり、さらに混合物内で
のFe2O3+Na2Oの反応によるNa2Oの回収も期待
できる。さらに前述のように、生成した鉄酸ソー
ダを加水分解してNaOHを回収する際、粗粒の
Fe2O3が次第に微粉化する傾向にあり、また鉄鉱
石中には微粉(0.149mm以下)が5〜30wt%含ま
れており、鉄鉱石を粒度分布の広い状態で流動層
に受け入れた場合、微粉は単独では飛び出してし
まつて利用できないので、本実施例におけるよう
に、微粉のFe2O3を予め黒液と混合する方式は、
黒液を流動層内で燃焼させてNa2CO3とFe2O3
を有効に反応させることができ、さらにNa2Oの
回収反応に利用でき、原材料コストの低減につな
がるという点で、きわめて理に適つている。
As described above, in this example, Fe 2 O 3 and black liquor are introduced using the premixing method, and are used for mixing.
Since Fe 2 O 3 uses fine powder smaller than the fluidizing agent particle size, even if fine powder Fe 2 O 3 alone is put into the fluidized bed, it will prevent it from immediately jumping out of the furnace.
In addition, Na 2 to be recovered by reacting with Fe 2 O 3 due to the volatilization of volatile matter, ash, etc. due to the combustion of black liquor before it reaches the fluidized bed, which is expected when only easily combustible black liquor is input . The loss of O can be suppressed as much as possible. The black liquor must be burned in a fluidized bed. In addition, the specific gravity of Fe 2 O 3 is 4.5 to 4.9,
This is approximately twice as large as that of silica sand, etc. On the other hand, when only black liquor is supplied, the specific gravity itself increases as the black liquor becomes concentrated and the solid content increases;
Due to the property of organic matter to volatilize and swell, the apparent specific gravity decreases, and the resistance to rising combustion gas increases, making it easier for Na 2 to be carried over to the outside of the system without reaching the fluidized bed. O will suffer a loss. In addition, black liquor is a viscous liquid, so it is difficult to mix with granular Fe 2 O 3 , but it is relatively easy to mix with powdered Fe 2 O 3 , and the mixture has a shape larger than the superplasticizer particle size. (lumpy or candy-like)
Therefore, there is no chance of it jumping out of the furnace. In addition, the reaction that produces sodium ferrate (Na 2 Fe 2 O 4 ) is the reaction between Fe 2 O 3 and
This is a solid phase reaction with Na 2 CO 3 , and the larger the reaction surface area of Fe 2 O 3 (and thus the finer the powder), the larger the amount of reaction per unit volume. Recovery of Na 2 O through the reaction of 2 O can also be expected. Furthermore, as mentioned above, when recovering NaOH by hydrolyzing the generated sodium ferrate, coarse particles are
Fe 2 O 3 tends to gradually become fine powder, and iron ore contains 5 to 30 wt% of fine powder (0.149 mm or less), so when iron ore is received in a fluidized bed with a wide particle size distribution Since the fine powder cannot be used alone because it jumps out, the method of mixing fine powder Fe 2 O 3 with black liquor in advance as in this example is as follows:
It is possible to effectively react Na 2 CO 3 and Fe 2 O 3 by burning black liquor in a fluidized bed, and it can also be used for the recovery reaction of Na 2 O, leading to a reduction in raw material costs. It makes perfect sense.

なお鉄鉱石の代りにTiO2、FeTiO3を使用する
ことも勿論可能である。
Note that it is of course possible to use TiO 2 or FeTiO 3 instead of iron ore.

〔発明の効果〕〔Effect of the invention〕

以上説明したように、本発明の方法において
は、Fe2O3、TiO2、FeTiO3よりなる群より選択
された物質を苛性化剤として用い、かつ粗粒の苛
性化剤を流動床炉下流の集じん機のろ過材として
用いるので、集じん機内で予熱されたろ過材を流
動床炉に供給することにより、廃熱を有効に回収
することができ、流動床炉内での反応を効率よく
進め得るなどの効果を奏する。
As explained above, in the method of the present invention, a substance selected from the group consisting of Fe 2 O 3 , TiO 2 , and FeTiO 3 is used as a causticizing agent, and a coarse causticizing agent is added downstream of a fluidized bed furnace. By supplying the filter material preheated in the dust collector to the fluidized bed furnace, waste heat can be effectively recovered, making the reaction in the fluidized bed furnace more efficient. This has the effect of making progress easier.

【図面の簡単な説明】[Brief explanation of drawings]

第1図および第2図は本発明の方法を実施する
装置の一実施例を示すフローシートである。 1……希黒液タンク、2……エバポレータ、3
……濃黒液タンク、4……流動床炉、5……冷却
器、6……加水分解槽、7……クラリフアイヤ
ー、8……苛性ソーダタンク、10……洗浄槽、
11……フイルタ、12……純水タンク、13…
…ボイラ、14……ガス・エアヒータ、15……
集じん機、16……誘引フアン、17……煙突、
18……分級器、20……分級器、21……混合
槽、22……分級器。
FIGS. 1 and 2 are flow sheets showing one embodiment of an apparatus for carrying out the method of the present invention. 1... Dilute black liquor tank, 2... Evaporator, 3
... Concentrated black liquor tank, 4 ... Fluidized bed furnace, 5 ... Cooler, 6 ... Hydrolysis tank, 7 ... Clarifier, 8 ... Caustic soda tank, 10 ... Washing tank,
11... Filter, 12... Pure water tank, 13...
...boiler, 14...gas/air heater, 15...
Dust collector, 16...Induction fan, 17...Chimney,
18... Classifier, 20... Classifier, 21... Mixing tank, 22... Classifier.

Claims (1)

【特許請求の範囲】 1 パルプ廃液を濃縮した後、Fe2O3、TiO2
FeTiO3よりなる群より選択された物質を苛性化
剤として加えて流動床炉4で燃焼せしめ、ついで
生成物を水中に投入して苛性ソーダおよび苛性化
剤を回収する方法において、 流動床炉4からの排ガスを、苛性化剤の粗粒か
らなるろ過層に導入し通過させて集じん処理し、
排ガスにより予熱されたろ過層の粗粒苛性化剤を
流動床炉4に供給することを特徴とするパルプ廃
液から苛性ソーダを回収する方法。
[Claims] 1. After concentrating the pulp waste liquid, Fe 2 O 3 , TiO 2 ,
A method in which a substance selected from the group consisting of FeTiO 3 is added as a causticizing agent and combusted in a fluidized bed furnace 4, and then the product is poured into water to recover caustic soda and the causticizing agent from the fluidized bed furnace 4. The exhaust gas of
A method for recovering caustic soda from pulp waste liquid, characterized in that a coarse causticizing agent in a filter bed preheated by exhaust gas is supplied to a fluidized bed furnace 4.
JP58033627A 1983-02-28 1983-02-28 Recovery of sodium hydroxide from pulp waste Granted JPS59162129A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58033627A JPS59162129A (en) 1983-02-28 1983-02-28 Recovery of sodium hydroxide from pulp waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58033627A JPS59162129A (en) 1983-02-28 1983-02-28 Recovery of sodium hydroxide from pulp waste

Publications (2)

Publication Number Publication Date
JPS59162129A JPS59162129A (en) 1984-09-13
JPH0348127B2 true JPH0348127B2 (en) 1991-07-23

Family

ID=12391679

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58033627A Granted JPS59162129A (en) 1983-02-28 1983-02-28 Recovery of sodium hydroxide from pulp waste

Country Status (1)

Country Link
JP (1) JPS59162129A (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6059190A (en) * 1983-09-12 1985-04-05 川崎重工業株式会社 Recovery of caustic soda from pulp waste liquid
JPS60181392A (en) * 1984-02-06 1985-09-17 製紙技術研究組合 Direct causticizing method using fluidized bed
JPH0650173B2 (en) * 1986-02-14 1994-06-29 株式会社荏原製作所 Fluidized bed combustion method for combustible materials
ZA937252B (en) * 1992-09-30 1994-04-19 North Broken Hill Ltd A process for pelletising particles of alkali metal ferrite
CN103408039B (en) * 2013-08-28 2014-12-10 郑州中南杰特超硬材料有限公司 Process and equipment for recycling alkali from cubic boron nitride synthesis tailings

Also Published As

Publication number Publication date
JPS59162129A (en) 1984-09-13

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