JPS5954621A - Method and apparatus for recovering soda from waste liquid of pulp - Google Patents

Method and apparatus for recovering soda from waste liquid of pulp

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Publication number
JPS5954621A
JPS5954621A JP16216682A JP16216682A JPS5954621A JP S5954621 A JPS5954621 A JP S5954621A JP 16216682 A JP16216682 A JP 16216682A JP 16216682 A JP16216682 A JP 16216682A JP S5954621 A JPS5954621 A JP S5954621A
Authority
JP
Japan
Prior art keywords
soda
fluidized bed
waste liquid
recovery boiler
tank
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
Application number
JP16216682A
Other languages
Japanese (ja)
Inventor
Koji Iwahashi
岩橋 康二
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP16216682A priority Critical patent/JPS5954621A/en
Publication of JPS5954621A publication Critical patent/JPS5954621A/en
Pending legal-status Critical Current

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  • Paper (AREA)

Abstract

PURPOSE:To save the heat of calcination in the titled recovery method, by eliminating a rotary kiln, combining the soda recovery boiler with the fluidized bed calcination apparatus for CaCO3, supplying a part of the waste liquid to the calcination apparatus, and introducing the exhaust gas of the calcination apparatus to the downstream of the boiler. CONSTITUTION:A concentrate alkali pulp waste liquid is sprayed through the burner 12 to the bottom of the combustion furnace of the recovery boiler 10, and burnt at high temperature by the primary and secondary hot air supplied from the lines 13, 14 to form smelt. The smelt is transferred to the soda dissolution tank 16 and dissolved. Separately, the pulp waste liquid supplied through the line 31 is burnt in the fluidized bed calcination apparatus 22 by the hot air supplied through the line 34, to keep the fluidized bed 22A at a high temperature. CaCO3 is calcined at the temperature, and the produced CaO is introduced into the tank 16, and made to react with the smelt component Na2CO3 to form NaOH. The obtained NaOH is introduced into the tank 19, and the produced CaCO3 is returned to the apparatus 22. The hot gas generated in the apparatus 22 is introduced into the cyclone 25 to separate the solid particles and introduced to the downstream of the boiler 10.

Description

【発明の詳細な説明】 本発明は、パルプ廃液ソーダ回収方法及び装置の改善、
特に回□収薬品の苛性□化プロセスの合理′□花対策に
関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention provides improvements to pulp waste soda recovery methods and devices;
In particular, it concerns the rationality of the causticization process for recovered chemicals and countermeasures against blooms.

□第□′1図はアルカリパルプ製造工程を示す概略説明
図である。以下、第1図を参照して従来のアルカリパル
プ製造法について説明す名。
□Figure □'1 is a schematic explanatory diagram showing the alkali pulp manufacturing process. The conventional alkaline pulp manufacturing method will be explained below with reference to FIG.

薫1図にお□いて、1はパルプ蒸解缶、2はパルプ材の
ブルータンク、Phパルプ、3は廃液を濃縮するための
エバポレータ、4は薬品回収ボイラ(以下回収ボイラと
呼ぶ)、5はスメルト浩解タンク、6は苛性化槽、7は
ロータ□リキルン、8は白液タンク、9は蛾気集塵機で
ろ込。
Kaoru In Figure 1, 1 is a pulp digester, 2 is a blue tank for pulp material, Ph pulp, 3 is an evaporator for concentrating waste liquid, 4 is a chemical recovery boiler (hereinafter referred to as recovery boiler), and 5 is a Smelt decomposition tank, 6 is a causticizing tank, 7 is a rotor □ rekiln, 8 is a white liquor tank, and 9 is filtrated with a moth air dust collector.

パルプがmmの薬品は、蒸解缶1又れ苛性化槽6に供給
され以下ブロークンク2、エバポレータ5、回収ボイラ
4.、、スメルト溶解タイク、5、苛性化槽λ、白液タ
ジレ8の順に具)’Lt’l’?蒸−−品循環系統PL
を循環する。苛性化槽6で生成I〜だ炭酸カルシウムは
、ロー、クリキルン7 Q成して酸化力ルシウノ・とし
□苛性化槽6に循環オj1用される1、又、薬品は上記
回収ボイラ4において一部煙道からダストとなって飛散
するが、そのほとんどは電気集塵機9で回収されて黒液
う1 インに戻され上記回収ボイラ4に送られ燃焼される。従
来の方法にヂいて、1アルカリバルブ廃液は回収ボイラ
4で燃焼するにとで生成したスメルトは、スメルト溶解
槽5で水に溶解して炭酸ソーダ水溶液をつくる。このF
酸ソーダは次に苛+′を化種6で、供給される0a(O
T()+ (又はCnOとH2O)と接触させて次式の
ように蒸解薬品である苛性ソーダに苛性化される。
The chemicals with a pulp of mm are supplied to a digester and a causticizing tank 6, followed by a broken tank 2, an evaporator 5, a recovery boiler 4. ,, smelt dissolving tank 5, causticizing tank λ, white liquor tag 8) 'Lt'l'? Steam product circulation system PL
cycle. Calcium carbonate produced in the causticizing tank 6 is converted into an oxidizing power by a low-temperature kiln 7 and used for circulation in the causticizing tank 6, and the chemicals are recycled in the recovery boiler 4. Most of the dust is scattered from the flue, but most of it is collected by the electrostatic precipitator 9, returned to the black liquor 1, and sent to the recovery boiler 4 to be burned. In the conventional method, the 1 alkali valve waste liquid is combusted in a recovery boiler 4, and the smelt produced is dissolved in water in a smelt dissolving tank 5 to produce a sodium carbonate aqueous solution. This F
Acid soda is then converted into sodium chloride with species 6 and 0a (O
It is brought into contact with T()+ (or CnO and H2O) and causticized into caustic soda, which is a cooking chemical, as shown in the following formula.

Na2003 +0a(OH)2−+ 2NaOH+ 
CFLCO3一方、苛性化槽6で生成したCa c03
は、ロータリキルン7で焼成してCaOとし、水で消和
させてCa(OR)2を生成させて苛性化槽6に循環使
用する。
Na2003 +0a(OH)2-+ 2NaOH+
CFLCO3 Meanwhile, Ca c03 produced in causticizing tank 6
is calcined in a rotary kiln 7 to form CaO, slaked with water to generate Ca(OR)2, and recycled to the causticizing tank 6.

′ □上記□゛従末法の欠点は、苛性化槽6で生成した
caao3スラリをキルン焼成するときの燃料使用:蓮
が大きいことである。
' □ The disadvantage of the above □゛ secondary method is that the amount of fuel used when firing the CAAO3 slurry produced in the causticizing tank 6 in a kiln is large.

本発明は苛性化槽6で生成するc B a o、スラリ
□ −の焼成における省エネルギと回収薬品の苛性イし
プロセスの合理化を図りうるバルブ廃液ソーダ回収ボイ
ラび装置を提供することを目的とするもので、従来、用
いていたロータリキルンを廃し、パルプ廃液ソーダ回収
ボイラと炭酸カルシウム焼成用流動層焼成装置を組合せ
使用し、パルプ廃液の1部を流動層焼成装置に供給する
と共に、燃焼排ガスをソーダ回収ボイラの下流部に導く
ことを要旨とするものであり、これによシ従来のロータ
リキルン型炭酸カルシウム焼成装置を使用した場合に比
べ熱量を節減できるものである。
An object of the present invention is to provide a valve waste liquid soda recovery boiler device that can save energy in the firing of the cBao and slurry produced in the causticizing tank 6 and streamline the process of causticizing the recovered chemicals. The rotary kiln used in the past was abolished, and a pulp waste liquid soda recovery boiler and a fluidized bed calciner for calcining calcium carbonate were used in combination.A part of the pulp waste liquid was supplied to the fluidized bed calciner, and a part of the pulp waste liquid was supplied to the fluidized bed calciner. The main purpose of this method is to introduce the carbonate to the downstream part of the soda recovery boiler, thereby reducing the amount of heat compared to the case where a conventional rotary kiln type calcium carbonate calcining device is used.

本発明の第1の発明は、パルプ廃液ソーダ回収において
、バルブ廃液ソーダ回収ボイラ下部のソーダ溶解槽また
拡装置の苛性化装置からの炭11P/カルシウムを同ン
ー、ダ回1又ボイラ、に、併設された炭酸カルシウム焼
成用流、動郡焼ルシ7装、装置に供給して、酸化カルシ
ウムを炉1威させ、焼、盛酸化カルシウムを前記ソーダ
溶、解mまたは苛性、化装置へ導くと共に、ソーダ回収
ボイラと炭、酸、ソフルシウノ・焼成用n動IF4焼成
装置との、双方にバ1/L7ノ廃液を供給、燃焼し、流
動:層、焼成装置か、ら、の排ガスをソーダ回収ボイラ
排、ガ、スと、:合流、させ、る、ことef:特徴とす
るバルブ廃液ソーダ回収方繞に関するものであり、第2
の発明titバルブ廃液を噴霧燃焼するソーダ回収ボイ
ラにおいて5.ヨ記ソーダ回収ボイラに併設された炭酸
、カルシウ:ム焼成用r・t、 1lb1層焼成装力と
、同?IE動層焼成装置−2配、設された回収ボイラ下
部のソーダ溶解fpItたは別置の苛性化槽と連結した
炭酸力、ルシウム9供給「1と、上記流動層焼成装置・
・\配、、股された助燃用燃料供給口及びパルプ廃液供
給、口と、上記流動層焼成装置の出口廃ガスを上記、ン
、−ダ回収ボイラの下流部に導く手段を備えたことを特
徴とするパルプ廃液ソー5回」疼装置に関するものでろ
る。
The first aspect of the present invention is that, in pulp waste soda recovery, charcoal 11P/calcium from the soda dissolving tank at the bottom of the valve waste soda recovery boiler or from the causticizing device of the expansion device is transferred to the same boiler, The calcium carbonate calcining flow, the 7-unit calcining unit, and the 7-unit calcining equipment were supplied to the furnace, and the calcined and plated calcium oxide was introduced to the soda dissolving, dissolving, or causticizing equipment. The waste liquid of B1/L7 is supplied to both the soda recovery boiler and the n-motion IF4 calciner for charcoal, acid, and calcination, and burned, and the exhaust gas from the fluidized bed and calciner is recovered with soda. Boiler exhaust, gas, suto: merging, letting, ru, ef: Concerning the characteristic valve waste liquid soda recovery method, the second
5. In a soda recovery boiler that sprays and burns tit valve waste liquid. Is it the same as the 1lb 1 layer firing equipment installed in the soda recovery boiler? IE fluidized bed calciner - 2 units, carbonation power connected to soda melting fpIt at the bottom of the installed recovery boiler or a separate causticizing tank, lucium 9 supply "1", and the above fluidized bed calciner/
・A fuel supply port for auxiliary combustion, a pulp waste liquid supply port, and a means for guiding the outlet waste gas of the fluidized bed firing apparatus to the downstream part of the recovery boiler are provided. Characteristics of pulp waste liquid saw 5 times" It is related to the pain device.

本発明においては回収ボイラに次いで従来、の如くスメ
ルト溶解、タンク、苛性化槽が設置され、この苛性化槽
で生成さ、れたC!aO03,を流動層焼成置に導い・
てもよいが、後述の具体例に示すように・回収ボイラに
次ぐスメルト溶解槽と流動層焼成装置を直結し、δメル
ト溶解槽において、流動層燃焼装置からのOaOとN 
32003  水溶液を反応さ、せてOa CQ3を生
成し、とのo z a o3を流動層燃焼□装置に送る
方が苛性化槽を省略できるので好ま・、しい。
In the present invention, a smelt melting tank, a causticizing tank, and a causticizing tank are installed next to the recovery boiler as in the conventional method, and the C! aO03, is introduced into the fluidized bed calcination equipment.
However, as shown in the specific example below, the smelt melting tank next to the recovery boiler and the fluidized bed sintering device are directly connected, and in the δ melt melting tank, OaO and N from the fluidized bed sintering device are directly connected.
It is preferable to react the 32003 aqueous solution to produce Oa CQ3 and send the Oa CQ3 to the fluidized bed combustion apparatus because the causticizing tank can be omitted.

本発明の方法および装置はエネルギ多消費型産業である
紙パルプ工場のパルプ蒸解薬品回収ボイラに適□用して
有効である。
The method and apparatus of the present invention are effective when applied to pulp cooking chemical recovery boilers in pulp and paper mills, which are energy-intensive industries.

以下、第2図を参照・して本発明を説明する。    
The present invention will be explained below with reference to FIG.
.

図において、10は回収ボイラ本体で、通常のソ、−、
ダ回収ボイラの構成である。11は煙道に連がるボ、イ
ラバンク部、12はパルプ廃液パ−す、15及び14け
それぞれ1次、2次空気、供給口である。16は上記回
収ボイラ10の下部に配設されたソーダ溶解槽、17は
同ソーダ溶解槽16の上部に開口するごとく配設された
用水供給口、18は上記ソーダ溶解槽16に開口するご
とく配設された白液取出し管、19は同白液取出し!1
Bが接続された白液タンク、20は同白液りンク19に
接続された白液供給管、21は上記ソーダ溶解槽16の
下底に接続された炭酸カルシウムスラリ取出し管である
In the figure, 10 is the main body of the recovery boiler, which is a normal so, -,
This is the configuration of a waste recovery boiler. Reference numeral 11 designates a hole connected to the flue, an ira bank section, 12 a pulp waste liquid purse, and 15 and 14 primary and secondary air supply ports, respectively. 16 is a soda dissolving tank disposed at the bottom of the recovery boiler 10, 17 is a water supply port disposed to open at the top of the soda dissolving tank 16, and 18 is a water supply port disposed to open to the soda dissolving tank 16. The installed white liquid extraction pipe, 19, is the same white liquid extraction pipe! 1
B is a white liquor tank connected to it, 20 is a white liquor supply pipe connected to the same white liquor link 19, and 21 is a calcium carbonate slurry take-out pipe connected to the bottom of the soda dissolving tank 16.

22け上記回収ボイラ本体10に併設された炭酸カルシ
ウムスラリ焼成用の流動層焼成装置、23は同流動層焼
成装置22内の流動層22A下部の空気分散板、24は
上記流動層焼成装置22上部の排ガス取出し管、25は
同排ガス取Ill L管24に接続した固体粒千年じん
用ライクロン、26は同サイクロン25の上部と回収ボ
・イラの下流部を結ぶ連接管である。
22 is a fluidized bed firing device for firing calcium carbonate slurry attached to the recovery boiler main body 10, 23 is an air distribution plate at the lower part of the fluidized bed 22A in the same fluidized bed firing device 22, and 24 is the upper part of the fluidized bed firing device 22. 25 is a cyclone for solid particle 1,000-year dust connected to the exhaust gas extraction Ill L pipe 24, and 26 is a connecting pipe connecting the upper part of the cyclone 25 and the downstream part of the recovery boiler.

27は同サイクロン25の下部と」1記ソーダ溶解槽1
6を結ぶ移送管、28は上記流動層焼成装置22内の流
動層22Aで焼成された粒子の取出し管、29は同取出
管28に配設された流量調節用のロータリバルブ、30
は同ロータリバルブ29と上記ソーダ溶解槽16を結ぶ
連接管である。
27 is the lower part of the cyclone 25 and the soda dissolving tank 1
6, 28 is a take-out pipe for the particles fired in the fluidized bed 22A in the fluidized bed firing apparatus 22, 29 is a rotary valve for adjusting the flow rate disposed in the take-out pipe 28, 30
is a connecting pipe connecting the rotary valve 29 and the soda dissolving tank 16.

31は上記流動層焼成装置22内の流動層22Aに開口
するごとく配設されたパルプ廃液供給口、′52は同じ
く炭酸カルシウム供給口、33は同じく起動及び助燃用
燃料供給口である。34は上記流動層焼成装置22の空
気分散板23の下部に開口するごとく配設された流動層
22Aを流動させ、かつバルブ廃液及び鱈料を燃焼させ
る加熱空気供給口である。
Reference numeral 31 designates a pulp waste liquid supply port which is arranged to open into the fluidized bed 22A in the fluidized bed firing apparatus 22, reference numeral '52 designates a calcium carbonate supply port, and reference numeral 33 designates a fuel supply port for starting and auxiliary combustion. Reference numeral 34 denotes a heated air supply port for fluidizing the fluidized bed 22A, which is disposed so as to open at the bottom of the air distribution plate 23 of the fluidized bed firing apparatus 22, and for burning the valve waste liquid and cod meat.

このような構成において、本発明の作用について説明す
る。、 回収ボイラ10のパルプ廃液燃焼部である炉底部には、
高濃度に濃縮されたアルカリパルプ廃液がバーナ12か
ら微粒状で噴霧され、炉底部に供給される1次及び2次
空気供給W16゜14から供給される加熱空気で高温燃
焼されスメルト(主としてN汽20(13)li生成す
る1、このスメルトを炉底からソーダ溶解槽16に流下
、溶解させる。
In such a configuration, the operation of the present invention will be explained. , At the bottom of the furnace which is the pulp waste liquid combustion part of the recovery boiler 10,
Highly concentrated alkaline pulp waste liquid is sprayed in the form of fine particles from the burner 12, and combusted at high temperature with heated air supplied from the primary and secondary air supply W16°14 supplied to the bottom of the furnace to form smelt (mainly N steam). 20 (13) li produced 1, this smelt flows down from the bottom of the furnace into the soda melting tank 16 and is melted.

一方、流動層却1「成装置22にパルプ簾液供給口31
から供給されたパルプ廃液は、加熱空気供給口34から
供給される加熱空気で燃焼させて流71717層22A
を1000 Tl:前後の高温に保つ。
On the other hand, the pulp retentate supply port 31 is connected to the fluidized bed cooling device 22.
The pulp waste liquid supplied from
is maintained at a high temperature of around 1000 Tl.

この温度では炭酸カルシウムは下記のように酸化カルシ
ラノ・に焼成される。
At this temperature, calcium carbonate is calcined to calcyano oxide as described below.

OFl、003 →C!ao +co2生成された酸化
力ルシウノ・は取出し7管28、ロータリパルプ29、
連接管30を経て、ソーダ溶解4・4.fl 16に導
かれ、前述のスメルト成分N a2003と反応して下
記反応を生じる。
OFl, 003 →C! ao + co2 generated oxidizing power is taken out 7 pipes 28, rotary pulp 29,
Through the connecting pipe 30, soda melting 4.4. fl 16 and reacts with the aforementioned smelt component Na2003 to produce the following reaction.

N132003 +OnO+ N20−+ 2NaOH
+CaO03このようにして蒸解薬品であるN FI 
OHを作る。
N132003 +OnO+ N20-+ 2NaOH
+CaO03 Thus the cooking chemical N FI
Make OH.

ソーダM解槽16で生成したNaOHは白液取出口18
から白液タンク19へ導かれ、白液供給管20からは降
第1図に示すようなバルブ薬品循環系統PLへ送らiす
る。
NaOH generated in the soda M decomposition tank 16 is removed from the white liquor outlet 18.
From there, it is led to a white liquid tank 19, and from a white liquid supply pipe 20, it is sent to a valve chemical circulation system PL as shown in FIG.

またソーダ溶解槽16で生成したCa C03(’:l
’、 %炭酸カルシウムスラリ取出口21から取出され
、予備脱水の後に炭酸カルシウム焼成装置となる流動層
焼成装置22に戻される。
In addition, Ca C03 (':l) generated in the soda dissolving tank 16
', % The calcium carbonate slurry is taken out from the outlet 21, and after preliminary dehydration is returned to the fluidized bed sintering apparatus 22 which becomes the calcium carbonate sintering apparatus.

一方流動層焼成装置22で発生17た高温熱ガスは、排
ガス取出し管24から排出され倚粒子捕集用サイクロン
25で固体粒子を分離捕集したのち連接管26を通して
回収ボイラの下流部に導かれる。ザイクロン25で捕集
した固体粒子は連接管27を通ってソーダ溶解槽16又
は従来の苛性化装置に導かれる。
On the other hand, the high-temperature gas generated 17 in the fluidized bed firing device 22 is discharged from the exhaust gas take-off pipe 24, solid particles are separated and collected by the particle-collecting cyclone 25, and then guided to the downstream part of the recovery boiler through the connecting pipe 26. . The solid particles collected by Zyclone 25 are conducted through connecting pipe 27 to soda dissolution tank 16 or conventional causticizing equipment.

本発明により次のよう々効果が奏せられる。The present invention provides the following effects.

(ト) 炭酸カルシラノ・焼成用ロータリキルンをガス
と固体の接触がよく熱伝達のよい流動層焼成装置に値換
えるので燃料油it?、 、N) (=節減できる。
(g) Is it possible to replace the rotary kiln for carbonic acid calcining with a fluidized bed calcining device that has good contact between gas and solid and has good heat transfer? , , N) (= Savings can be made.

(イ)流動層焼成装置の燃料の一部にバルブ廃液分用い
るので燃料消費量を節減できる。
(a) Since valve waste liquid is used as part of the fuel for the fluidized bed firing device, fuel consumption can be reduced.

(つ) ソーダ溶解槽または苛性化装置から排出される
炭酸カルシウムスラリ中の炭酸カルシウノ・粒子は微粒
で・あるので、流動層勢威装置では微、粒の飛び出しが
予<、そのためガス速度を遅くする必要があり装置直径
を大きくしなければならないが、本発明でけ適晴のパル
プ。
(1) Calcium carbonate particles in the calcium carbonate slurry discharged from the soda dissolving tank or causticizing device are fine particles, so in the fluidized bed device, the particles are likely to fly out, which slows down the gas velocity. Although it is necessary to increase the diameter of the device, the present invention can produce suitable pulp.

廃液を加えるので、流動層内で廃箪、中のソニ・ダ分が
結合剤となって造粒が生り、微粒の飛び方が少なく、ガ
ス流速を上げられるので装置は小さくてよい。パルプ廃
液1多すぎるり流動層全体が粒子同志が固着して・動か
なくなるので、添加用は適宜、調節する必要があ夕、具
体的には供給炭酸力ルシウノ・重量1V?c対、!、6
0%濃度のパル7′廃液約0.5位が上限と考えられる
Since waste liquid is added, granulation occurs in the fluidized bed with the waste liquid and the soni/da content acting as a binder, which reduces the scattering of fine particles and increases the gas flow rate, so the equipment can be small. If there is too much pulp waste liquid, the particles will stick to each other and stop moving in the entire fluidized bed, so it is necessary to adjust the amount of addition appropriately.Specifically, the supply carbonic power is 1V by weight. c vs.! ,6
The upper limit is considered to be about 0.5 for Pal 7' waste liquid with a concentration of 0%.

に) ?M、動層の燃料としてパルプ廃液中加えるとt
’l’ガス中にNバ、co3の微粒子が飛ぶのてその1
1大気に放出できないが、回工1ポイン煙道に1へすこ
とで熱回収と排ガス脱しんが同時顛行なわれる。排ガス
に同伴するカルシウム1、回収ボイラに何ら影響をもた
ない。
)? M, when added to the pulp waste liquid as fuel for the moving bed, t
Part 1: Fine particles of N and CO3 fly in the 'l' gas.
1 Although it cannot be released into the atmosphere, heat recovery and exhaust gas desorption can be performed simultaneously by placing it in a 1-point circuit flue. Calcium 1 accompanying the exhaust gas has no effect on the recovery boiler.

0)流!lll1層に添加したパルプ廃液中のNn 分
は、Na2003として大部分は酸化カルシラノ・粒子
に付着して回収される。Na200sl’J:カルシラ
ノ^と共にソーダ溶解槽、に戻されるので回収ボイラか
らの14 a2003  と同様にソーダ溶解槽に回収
される。、。
0) Flow! The Nn content in the pulp waste liquid added to the lll1 layer is mostly recovered as Na2003, adhering to the oxidized calcyano particles. Na200sl'J: Since it is returned to the soda dissolving tank together with Calcillano^, it is recovered to the soda dissolving tank in the same way as 14 a2003 from the recovery boiler. ,.

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

第1図は、従来やアルカリパルプfJv造工程を示すフ
ロー・ヒートで金ル、第2図は本発明の方法および装置
を示す概略図である。 復代理人  内 [l   明  。 復代理人  萩 原 亮 − 第1図 第2図 i20′
FIG. 1 is a flow heat method showing a conventional alkali pulp fJv manufacturing process, and FIG. 2 is a schematic diagram showing the method and apparatus of the present invention. Within the sub-agent [l Akira. Sub-Agent Ryo Hagiwara - Figure 1 Figure 2 i20'

Claims (2)

【特許請求の範囲】[Claims] (1)  パルプ廃液ソーダ回収におい−て、ノクルプ
廃液ソー□ダ回収ボイラ下部のソーダ溶解槽または別置
の苛性化装置からの炭酸カルシ:カムを同ソーダ回収ボ
イラに併設された炭酸功ルンウム焼□成用流動層焼□成
装置に供給・し・で酸化カ□ルシウムを焼成させ、焼成
酸化カル・シウム、を□前記ソーダ溶解槽または苛性化
装置へ導くと共に、ソーダ回収ボイラと炭酸□カル・1
ッグム焼成用流動層焼成装置との双方にパルプ□部、・
液を供給、燃焼し、流動層焼成装置□からの排ガスをソ
ーダ回収ボイラ排ガスと合流させ・ることf:特徴とす
るパルプ廃液ソーダ回収方法。
(1) In pulp waste soda recovery, the carbonate calcined cam from the soda dissolving tank at the bottom of the Nokulpu waste liquid soda recovery boiler or the separate causticizing equipment is transferred to the carbonate gong runum kiln attached to the same soda recovery boiler. The calcined calcium oxide is fed to the fluidized bed sintering device for sintering, and the calcined calcium oxide is guided to the soda dissolving tank or causticizing device, and the calcined calcium oxide is fed to the soda recovery boiler and the carbonate sintering device. 1
Pulp □ part, ・
The liquid is supplied and combusted, and the exhaust gas from the fluidized bed calciner □ is combined with the soda recovery boiler exhaust gas. f: Characteristic pulp waste liquid soda recovery method.
(2)  パルプ廃液を噴霧燃焼するソーダ回収ボイラ
において、上記ソーダ回収ボイラ・に・併設された炭酸
カルシウム焼成用流動・層焼成装置と、同流動層焼成装
置へ配・設された回収ボイラ下部のソーダ溶解槽また□
は別置の苛性化槽と連結した炭酸勤ルシウムの供給口と
、上記流動層□焼成装置へ配設された助燃用燃料供給口
及びバ□ルプ廃液供給口と、上記流動層焼成装置の□出
口廃:ガスを上記ソーダ回収ボイラの下流□部に導ぐ手
段を備えたことを特徴とするパルプ廃液プーダ回収装置
(2) In a soda recovery boiler that spray-combusts pulp waste liquid, a fluidized bed calcination device for calcium carbonate calcination attached to the above-mentioned soda recovery boiler, and a lower part of the recovery boiler arranged and installed in the same fluidized bed calcination device. Soda dissolving tank □
are a lucium carbonate supply port connected to a separate causticizing tank, an auxiliary combustion fuel supply port and a bulb waste liquid supply port provided to the fluidized bed calcination device, and a □ of the fluidized bed calcination device. Outlet waste: A pulp waste liquid puda recovery device characterized by comprising means for guiding gas to a downstream section of the soda recovery boiler.
JP16216682A 1982-09-20 1982-09-20 Method and apparatus for recovering soda from waste liquid of pulp Pending JPS5954621A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16216682A JPS5954621A (en) 1982-09-20 1982-09-20 Method and apparatus for recovering soda from waste liquid of pulp

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16216682A JPS5954621A (en) 1982-09-20 1982-09-20 Method and apparatus for recovering soda from waste liquid of pulp

Publications (1)

Publication Number Publication Date
JPS5954621A true JPS5954621A (en) 1984-03-29

Family

ID=15749274

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16216682A Pending JPS5954621A (en) 1982-09-20 1982-09-20 Method and apparatus for recovering soda from waste liquid of pulp

Country Status (1)

Country Link
JP (1) JPS5954621A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03291407A (en) * 1990-04-10 1991-12-20 Mitsubishi Heavy Ind Ltd Desulfurizer
CN110354784A (en) * 2019-07-19 2019-10-22 李家浩 A kind of sodium hydroxide process units

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03291407A (en) * 1990-04-10 1991-12-20 Mitsubishi Heavy Ind Ltd Desulfurizer
CN110354784A (en) * 2019-07-19 2019-10-22 李家浩 A kind of sodium hydroxide process units

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