JPS59146930A - Method for recovering soda from waste liquor from pulp manufacturing stage - Google Patents

Method for recovering soda from waste liquor from pulp manufacturing stage

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Publication number
JPS59146930A
JPS59146930A JP2150583A JP2150583A JPS59146930A JP S59146930 A JPS59146930 A JP S59146930A JP 2150583 A JP2150583 A JP 2150583A JP 2150583 A JP2150583 A JP 2150583A JP S59146930 A JPS59146930 A JP S59146930A
Authority
JP
Japan
Prior art keywords
iron oxide
soda
recovery boiler
caco3
waste liquor
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
JP2150583A
Other languages
Japanese (ja)
Inventor
Kikuo Tokunaga
喜久男 徳永
Senichi Tsubakizaki
椿崎 仙市
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 JP2150583A priority Critical patent/JPS59146930A/en
Publication of JPS59146930A publication Critical patent/JPS59146930A/en
Pending legal-status Critical Current

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  • Paper (AREA)

Abstract

PURPOSE:To reduce the cost of fuel by feeding powder consisting of CaCO3 and iron oxide to the waste liquor burning section of a recovery boiler, forming calcium ferrate by calcination, introducing it into a soda dissolving vessel to recover soda, CaCO3 and iron oxide, bringing the CaCO3 and iron oxide into contact with flue gas, and reutilizing dried compounds. CONSTITUTION:Waste liquor from a pulp manufacturing stage is blown into a recovery boiler 10 as a mist from burners 12, heated air is fed from air feeding pipes 13, 14, and the waste liquor is burned to produce smelted matter. At the same time, powder contg. CaCO3 and iron oxide as principal components is fed to the waste liquor burning section of the boiler 10 from feeding inlets 15, and calcium ferrate is formed by calcination. The smelted matter and the calcium ferrate are introduced into a soda dissolving vessel 16 under the boiler to recover sodium, calcium and iron components, and a slurry contg. CaCO3 and iron oxide formed by caustification in the vessel 16 is introduced into a drying means 24 placed in a flue through a transferring pipe 25. The slurry is dried, and the resulting powder is fed to the feeding inlets 15 through a transferring pipe 26 and reutilized.

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の改善。[Detailed description of the invention] The present invention is an improvement of a pulp waste soda recovery method.

特に回収薬品の苛性化プロセスの合理化対策に関する。In particular, it concerns measures to streamline the causticization process for recovered chemicals.

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
法について説明する。
FIG. 1 is a schematic diagram showing an alkali pulp manufacturing process. Hereinafter, a conventional method for producing alkaline pulp will be explained with reference to FIG.

第1図において、1はバルブ蒸解缶、2はパルプ材のブ
ロータンク、Pはパルプ、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2と呼
ぶ)、5はスメルト溶ブ仔タンク、6は苛性化槽、7は
ロータリキルン、8は白液夕/り、9は喝気集趙機であ
る。
In Figure 1, 1 is a valve digester, 2 is a blow tank for pulp material, P is pulp, 3 is an evaporator for concentrating waste liquid, 4 is a chemical recovery boiler (hereinafter referred to as recovery boiler 2), and 5 is a smelt. 6 is a causticizing tank, 7 is a rotary kiln, 8 is a white liquor tank, and 9 is a steam collector.

パルプ蒸解用の薬品は、蒸解缶1又は苛性化槽6に供給
され以下ブロータンク2、エバポレータ3、回収ボイラ
41スメルト浴屏タンク5゜苛性化槽6、白液タンク8
の順にパルプ蒸解薬品循環系RP Lを俯虚する。苛性
化槽6で生成した炭酸カルシウムは、ロークリキルン7
で焼成して酸イピカルシウムとし苛性化槽6に循環利用
される。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で回収されて黒液ラインに戻され上記回収ボイラ
4に送られ燃焼される。従来の方法において、アルカリ
パルプ廃液は回収ボイラ4で燃焼する。ここで生成した
スメルトは、スメルト溶解槽5で水に溶解して炭酸ソー
ダ水溶液なつ(る。この炭酸ソーダは次に苛性化槽6で
、供給されるcacoH)2(又はCaO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。
Chemicals for pulp cooking are supplied to the digester 1 or the causticizing tank 6, which includes a blow tank 2, an evaporator 3, a recovery boiler 41, a smelt bath tank 5, a causticizing tank 6, and a white liquor tank 8.
In this order, the pulp cooking chemical circulation system RP L is evacuated. The calcium carbonate produced in the causticizing tank 6 is transferred to the lorry kiln 7.
It is calcined to produce ipicalcium acid and recycled to the causticizing tank 6. In addition, some of the chemicals scatter as dust from the flue in the recovery boiler 4, but most of it is recovered by the electrostatic precipitator 9, returned to the black liquor line, sent to the recovery boiler 4, and burned. In the conventional method, the alkaline pulp waste liquid is combusted in a recovery boiler 4. The smelt produced here is dissolved in water in a smelt dissolving tank 5 to form an aqueous solution of sodium carbonate.This soda is then brought into contact with the supplied cacoH)2 (or CaO and H2O) in a causticizing tank 6. Then, it is causticized with caustic soda, which is a cooking chemical, as shown in the following formula.

Na2CO3+0a(OH)2−+ 2NaOH+0a
C03一方、苛性化槽6で生成したO a 003は、
ロータリキルン7で焼成してOaOとし、水で消和させ
てCa (OH)2を生成させて苛性化槽6に循環使用
する。
Na2CO3+0a(OH)2-+ 2NaOH+0a
On the other hand, O a 003 generated in the causticizing tank 6 is
It is calcined in a rotary kiln 7 to form OaO, slaked with water to generate Ca (OH)2, and recycled to the causticizing tank 6.

上記従来法の欠点は、苛性化槽6で生成したOa O0
3スラリをキルン焼成するときの燃料使用量が大きいこ
とである。
The disadvantage of the above conventional method is that Oa O0 generated in the causticizing tank 6
3. The amount of fuel used when firing the slurry in a kiln is large.

本発明は苛性化槽6で生成するC a CO3スラリー
の焼成における省エネルギと回収薬品の苛性化プロセス
の合理化を図りうるパルプ廃液ソーダ回収方法を提供す
ることを目的とするものであるが、同じ目的のために本
発明者等は先に回収ボイラのパルプ廃液燃焼部に(ag
o3を主として含む粉末を供給して回収ボイラ炉内にて
GaOを得、同炉内で燃成されたCaOを回収ボイラ下
部のソーダ溶解槽へ導き、同ソーダ溶解槽内の苛性化反
応で生成するCaCO3スラリをボイラ煙道の排ガスと
接触させて乾燥し5回収ボイラ炉内に投入するようKし
て、これにより従来使用していた苛性化装置内のCa 
CO3スラリの乾燥、焼成用ロータリキルンを排除する
際のCaC; Osスラリの乾燥を、ボイラ排熱により
有効に行うことができるという方法を提案しているが(
%願紹57−149232号)、本発明はこれを更に改
良したもので上記方法におけるC aG Osを主とし
て含む粉末に代えて炭酸カルシウムと酸化鉄を主として
含む粉末を回収ボイラのパルプ廃液燃焼部に供給するこ
とにより、焼成および苛性化率を高めた点に特徴を有す
るものである。
The purpose of the present invention is to provide a pulp waste soda recovery method that can save energy in firing the C a CO3 slurry produced in the causticizing tank 6 and streamline the causticizing process of recovered chemicals. For this purpose, the inventors first installed (ag) in the pulp waste liquid combustion section of the recovery boiler.
GaO is obtained in the recovery boiler furnace by supplying powder mainly containing o3, and the CaO burned in the furnace is led to the soda dissolution tank at the bottom of the recovery boiler, where it is generated by a causticizing reaction in the soda dissolution tank. The CaCO3 slurry is brought into contact with the exhaust gas of the boiler flue, dried, and then fed into the recovery boiler furnace.
When drying CO3 slurry and eliminating the need for a rotary kiln for firing, a method has been proposed in which drying of CaC;Os slurry can be effectively carried out using boiler exhaust heat (
% Application No. 57-149232), the present invention is a further improvement on this, and instead of the powder mainly containing CaG Os in the above method, a powder mainly containing calcium carbonate and iron oxide is used in the pulp waste liquid combustion section of the recovery boiler. It is characterized in that the firing and causticizing rates are increased by supplying it.

本発明は、ソーダ回収ボイラでパルプ廃液を噴霧燃焼す
る際に、回収ボイラのパルプ廃液燃焼部に炭酸カルシウ
ム及び酸化鉄を主として含む粉末を供給して回収ボイラ
炉内にて鉄酸カルシウムに焼成し、同炉内で焼成された
鉄酸カルシウムを回収ボイラ下部のン)ダ、カルシウム
、及び鉄分を回収するソーダ溶解槽へ導き、同ソーダ溶
解槽内の苛性化反応で生成する炭酸カルシウム及び酸化
鉄スラリを回収ボイラの後部煙道排ガス中に接触させて
乾燥した炭酸カルシウム及び酸化鉄粉末を回収ボイラ炉
内に供給することを特徴とするものである。
In the present invention, when pulp waste liquid is spray-combusted in a soda recovery boiler, powder mainly containing calcium carbonate and iron oxide is supplied to the pulp waste liquid combustion section of the recovery boiler, and the powder is calcined into calcium ferrate in the recovery boiler furnace. Calcium ferrate calcined in the same furnace is led to a soda dissolution tank located at the bottom of the recovery boiler that recovers iron, calcium, and calcium, and calcium carbonate and iron oxide produced by the causticization reaction in the soda dissolution tank. The method is characterized in that the slurry is brought into contact with the flue gas at the rear of the recovery boiler to supply the dried calcium carbonate and iron oxide powder into the recovery boiler furnace.

本発明の方法は、エネルギ多消費型産業である紙バルグ
エ楊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 of the present invention is effective when applied to the pulp cooking chemical recovery boiler of paper bargueyang, which is an energy-intensive industry.

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あり、下部は漏斗
状に傾斜しておりスメルトが流下しやすいように形成さ
れている。11は煙道に連がるボイラバンク部、12は
パルプ廃液バーナ、13及び14はそれぞれ1次及び2
次空気供給口、15は炭酸カルシウム及び酸化鉄を主と
して含む粉末の供給口である。炭酸カルシウムとしては
例えば石灰石が、酸化鉄としてはFeO。
In the figure, 10 is a recovery boiler main body, the lower part of which is sloped in the shape of a funnel so that the smelt can easily flow down. 11 is a boiler bank connected to the flue, 12 is a pulp waste liquid burner, and 13 and 14 are primary and secondary, respectively.
The secondary air supply port 15 is a supply port for powder mainly containing calcium carbonate and iron oxide. For example, limestone is an example of calcium carbonate, and FeO is an example of iron oxide.

Fe2O3,Fe3O4が用いられる。炭酸カルシウム
、酸化鉄はスメルトに対しほぼ自艦でよい。なお、上記
粉末はパルプ廃液供給系統に添加してもよい。16は上
記回収ボイラ1oの下部に配設されたソーダ溶解槽、1
7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
ること(配設された白液取出し管、19は同白液取出し
管18が接読された白液タンク、2oは同白液タンク1
9に接続された白液供給管、21は上記ソーダ溶′ps
槽16の下底に接続された炭酸カルシウムスラリ及び酸
化鉄スラリ取出し管である。22はボイラバンク後部煙
道に配設されたダスト捕集装置でマルチクロン又は高温
電気業じん機等が使用できる。23は上記ダスト捕集装
置22に一側が接続され、他側がソーダ溶解槽16に開
口する捕集ダスト移送管、24は後部煙道に配設された
炭酸カルシウム及び酸化鉄スラリの乾燥手段でボイラ排
ガスに接触乾燥させるようにしたものである。この場合
、炭酸カルシウム及び酸化鉄を含むスラリは場合によっ
ては予備脱水後、脱水ケーキを乾燥するようにしてもよ
い。24Aは上記炭酸カルシウム及び酸化鉄の乾燥手段
24の上部に配設されたスラリ供給手段で5例えばスプ
レィノズル、ベルトコンベア等が使用できる。25は上
記炭酸カルシウム及び酸化鉄のスラリ取出管21に一側
が接続され、他側が上記スラリ供給手段24Aに接続さ
れたスラリ移送管、26は上記炭酸カルシウム及び酸化
鉄スラリの乾燥手段24の下部に一側が接続され他側が
炭酸カルシウム及び酸化鉄を主として含む粉末の供給口
15に接続された、乾燥された炭酸カルシウム及び酸化
鉄粉末の移送管である。
Fe2O3 and Fe3O4 are used. Calcium carbonate and iron oxide can be used on your own ship for most of the time against smelt. Note that the above powder may be added to the pulp waste liquid supply system. 16 is a soda dissolving tank disposed at the bottom of the recovery boiler 1o;
7 is a water supply port arranged to open at the upper part of the soda dissolving tank 16, 18 is a white liquor take-out pipe that opens into the above-mentioned soda dissolving tank 16, and 19 is a white liquor take-out pipe 18. is the white liquor tank that was read directly, 2o is the same white liquor tank 1
9 is connected to the white liquor supply pipe, 21 is the above soda solution 'ps
This is a calcium carbonate slurry and iron oxide slurry take-out pipe connected to the bottom of the tank 16. 22 is a dust collection device installed in the flue at the rear of the boiler bank, and a Multichron or high-temperature electric industrial dust machine can be used. 23 is a collected dust transfer pipe connected to the dust collecting device 22 on one side and opened to the soda dissolving tank 16 on the other side; 24 is a drying means for calcium carbonate and iron oxide slurry disposed in the rear flue; It is designed to dry by contact with exhaust gas. In this case, the slurry containing calcium carbonate and iron oxide may optionally be pre-dehydrated, and then the dehydrated cake may be dried. Reference numeral 24A denotes slurry supply means disposed above the drying means 24 for calcium carbonate and iron oxide, and for example, a spray nozzle, a belt conveyor, etc. can be used. 25 is a slurry transfer pipe connected on one side to the calcium carbonate and iron oxide slurry take-out pipe 21 and the other side is connected to the slurry supply means 24A, and 26 is a lower part of the calcium carbonate and iron oxide slurry drying means 24. It is a transfer pipe for dried calcium carbonate and iron oxide powder, connected on one side and connected on the other side to a supply port 15 for powder mainly containing calcium carbonate and iron oxide.

このような構成において1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i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
空気供給管13.14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Na2Go3ンを生成する。
In this configuration, the operation of the present invention will be explained. At the bottom of the furnace, which is the pulp waste liquid combustion section of the recovery boiler 10, highly concentrated alkaline pulp waste liquid is stored in the burner 12.
The heated air supplied from the primary and secondary air supply pipes 13 and 14 is sprayed in the form of fine particles and supplied to the bottom of the furnace, and is combusted at high temperature to produce smelt (mainly Na2Go3).

この際、図のように炉底部を漏斗状に傾斜させておきス
メルトの流れを良好にする。
At this time, the bottom of the furnace is tilted like a funnel as shown in the figure to improve the flow of the smelt.

さらに、炉底部に炭酸カルシウム及び酸化鉄を主として
含む粉末、例えば石灰石Ca G Os粉末及び第二酸
化鉄粉末を供給口15から炉内に噴霧する。炉内で焼成
(CaCO3+Fe2O3→CtL○・Fe2O3+0
02 )されたCaO・Fe2O3の大部分な炉壁を流
下するスメル)K乗せて下部のソーダ溶解槽16に流下
させる。ソーダ溶解槽16内では、用水供給管17から
あらかじめ供給しである水にスメルト(Na2Go3.
 aao−Fe2o5)が溶解して下記反応を生ずる。
Further, powder containing mainly calcium carbonate and iron oxide, such as limestone Ca G Os powder and ferric oxide powder, is sprayed into the furnace from the supply port 15 at the bottom of the furnace. Calcined in a furnace (CaCO3+Fe2O3→CtL○・Fe2O3+0
Most of the CaO.Fe2O3 produced in 02) is carried by the smell) K flowing down the furnace wall and is caused to flow down into the soda dissolving tank 16 at the bottom. In the soda dissolving tank 16, smelt (Na2Go3.
aao-Fe2o5) is dissolved and the following reaction occurs.

Na Co +CaO・Fa O−+ 2NaOH+C
aCO3+Fe2032 3       23 このようにして蒸解薬品であるNaOHを作る。
NaCo+CaO・FaO−+ 2NaOH+C
aCO3+Fe2032 3 23 In this way, NaOH, which is a cooking chemical, is made.

一方、ソーダ溶解槽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
ら以降第1図に示すようなパルプ蒸解薬品循環系統PL
へ送られる。
On the other hand, NaOH generated in the soda dissolving tank 16 is led from a white liquor outlet 18 to a white liquor tank 19, and from a white liquor supply pipe 20 to a pulp cooking chemical circulation system PL as shown in FIG.
sent to.

又、ソーダ溶解槽16で生成したC a CiO3及び
Fe2O3は炭酸カルシウム及び酸化鉄スラリ取出口2
1から取出され、このスラリーは前記のように後部煙道
の乾燥手段24に送り、乾燥物は回収ボイラに供給口1
5から供給する。
In addition, C a CiO3 and Fe2O3 generated in the soda dissolving tank 16 are transferred to the calcium carbonate and iron oxide slurry outlet 2.
1, this slurry is sent to the drying means 24 in the rear flue as described above, and the dried material is fed to the recovery boiler at the feed port 1.
Supply from 5.

本発明において次のような効果が萎される。In the present invention, the following effects are achieved.

(至)本発明方法は、パルプ廃液な噴霧燃焼するソーダ
回収ポインにおいて、回収ボイラのパルプ廃液燃焼部に
炭酸カルシウム及び酸化鉄を主として含む粉末を供給し
て回収ボイラ炉内にて鉄酸カルシウムを焼成させるよう
にし炉内で高温を与えて苛性化するようにしたので、従
来の方法に比べ燃料使用量が大きかったロータリキルン
による加熱が必要でな(、従って燃料費を太幅Kidで
きる利点がある。
(To) The method of the present invention is to supply powder mainly containing calcium carbonate and iron oxide to the pulp waste liquid combustion section of the recovery boiler at a soda recovery point where pulp waste liquid is spray-combusted, and to convert calcium ferrate in the recovery boiler furnace. Since the method is calcined and causticized by applying high temperature in the furnace, there is no need for heating in a rotary kiln, which requires a large amount of fuel compared to the conventional method (therefore, there is an advantage that the fuel cost can be greatly reduced). be.

(イ) ロータリキルンを廃止するので、炭酸カルシウ
ム及び酸化鉄スラリの乾燥が必要であるが、ソーダ溶解
槽で生成する炭酸カルシウム及び酸化鉄スラリな予備脱
水後、煙道排ガスに直接接触させてスラリを乾燥させる
ため。
(b) Since the rotary kiln will be abolished, it will be necessary to dry the calcium carbonate and iron oxide slurry, but after preliminary dehydration of the calcium carbonate and iron oxide slurry produced in the soda dissolving tank, the slurry will be dried by bringing it into direct contact with the flue gas. for drying.

乾燥に要する熱を排ガスから得ることができ熱効率が改
善される。
The heat required for drying can be obtained from the exhaust gas, improving thermal efficiency.

り) 第3図はr、Barin 、 O,Knacke
 ’ Thermo −chemical prope
rties of inorganic 5ubsta
nce”(1973)の熱力学データを用いて計算した
本発明方法および比較反応の各温度におけるlog’K
p(反応の平向定数の対数)をプロットしたものであり
、 logK])か大きい程反応が進み易いことを示し
ている。図において、曲線AはCaaos 十Fe2e
3→CaO−Fe2O3+co21曲線BはCaC0→
CaO+Go2曲線C曲線NaCo+Fe2O3→Na
20−Fe2O3+002そして3 曲線りはNa2CO3→Na2O+CO2の反応につい
て、logKpの温度変化を求めたものである。
ri) Figure 3 shows r, Barin, O, Knacke.
'Thermo-chemical prope
rties of inorganic 5ubsta
log'K at each temperature of the method of the present invention and the comparative reaction calculated using the thermodynamic data of
This is a plot of p (logarithm of the horizontal constant of the reaction), and indicates that the larger the value (logK]), the easier the reaction is to proceed. In the figure, curve A is Caaos +Fe2e
3→CaO-Fe2O3+co21 curve B is CaC0→
CaO+Go2 curve C curve NaCo+Fe2O3→Na
20-Fe2O3+002 and 3 The curve shows the temperature change in logKp for the reaction of Na2CO3→Na2O+CO2.

本発明方法である曲線Aは、Ca 法(曲線B)、及び
Fe  法(曲線C)に比べて、 logiCI)が高
い位置にありこれは反応性の面で他より優位であること
を示している。換言すれば、これは曲線Aにおいて、 
CaO’ Fe3205が他の反応の生成物、例えば、
CaO,Na20−Fe2O3と比べてより多く生成す
ることを示しており、ソーダ溶M槽において、他の方法
(Ca法、Fe法)より、高い苛性化率が得られること
を意味し、本発明方法が有用であることを示す。
Curve A, which is the method of the present invention, shows that logiCI) is at a higher position than the Ca method (curve B) and the Fe method (curve C), indicating that it is superior to the others in terms of reactivity. There is. In other words, this means that in curve A,
CaO' Fe3205 is a product of other reactions, e.g.
This shows that CaO, Na20-Fe2O3 is produced in a larger amount than other methods (Ca method, Fe method), which means that a higher causticization rate can be obtained in the soda solution M bath than other methods (Ca method, Fe method). Demonstrate that the method is useful.

に)乾燥した炭酸カルシウム及び酸化鉄を炉内に供給す
るので、炉内で乾燥させる場合に比べ、炉内温度の低下
がな(、CaO−Fe2O3の焼成がより容易となる。
2) Since dried calcium carbonate and iron oxide are supplied into the furnace, the temperature inside the furnace does not decrease compared to the case where they are dried in the furnace (the calcination of CaO-Fe2O3 becomes easier).

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

第1図は、従来のアルカリバルブ製造工程を示すフロー
シルトであり、第2図は本発明の方法が適用できる装置
を示す概略図である。第6図は本発明方法および比較反
応のlog、Kpの温度依存性を示すグラフである。 復代理人 内 1)  明 復代理人 萩 原 亮 − 第1図 第2閃
FIG. 1 is a flow silt showing a conventional alkali valve manufacturing process, and FIG. 2 is a schematic diagram showing an apparatus to which the method of the present invention can be applied. FIG. 6 is a graph showing the temperature dependence of log and Kp of the method of the present invention and comparative reactions. Sub-agents 1) Meikoku Agent Ryo Hagiwara - Figure 1, 2nd flash

Claims (1)

【特許請求の範囲】[Claims] (1) ソーダ回収ボイラでパルプ廃液を噴霧燃焼する
際に、回収ボイラのパルプ廃液燃焼部に炭酸カルシウム
及び酸化鉄を主として含む粉末を供給して回収ボイラ炉
内にて鉄酸カルシウムに焼成し、同炉内で焼成された鉄
酸カルシウムを回収ボイラ下部のソーダ痔解槽へ導きソ
ーダ、カルシウム及び鉄分を回収すると共に、同ソーダ
溶解槽内の苛性化反応で生成する炭酸カルシウムスラリ
及び酸化鉄スラリを回収ボイラの後部煙道排ガスに接触
させて乾燥したのち、乾燥した炭酸カルシウム及び酸化
鉄粉末を回収ボイラ炉内に供給することを特徴とするパ
ルプ廃液ソーダ回収方法。
(1) When the pulp waste liquid is spray-combusted in the soda recovery boiler, a powder mainly containing calcium carbonate and iron oxide is supplied to the pulp waste liquid combustion section of the recovery boiler, and the powder is calcined into calcium ferrate in the recovery boiler furnace. The calcium ferrate calcined in the same furnace is led to the soda dissolution tank at the bottom of the recovery boiler to recover soda, calcium and iron, and the calcium carbonate slurry and iron oxide slurry produced by the causticization reaction in the same soda dissolution tank. A pulp waste liquid soda recovery method characterized in that the pulp waste soda is dried by being brought into contact with the rear flue gas of a recovery boiler, and then the dried calcium carbonate and iron oxide powders are supplied into a recovery boiler furnace.
JP2150583A 1983-02-14 1983-02-14 Method for recovering soda from waste liquor from pulp manufacturing stage Pending JPS59146930A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2150583A JPS59146930A (en) 1983-02-14 1983-02-14 Method for recovering soda from waste liquor from pulp manufacturing stage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2150583A JPS59146930A (en) 1983-02-14 1983-02-14 Method for recovering soda from waste liquor from pulp manufacturing stage

Publications (1)

Publication Number Publication Date
JPS59146930A true JPS59146930A (en) 1984-08-23

Family

ID=12056822

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2150583A Pending JPS59146930A (en) 1983-02-14 1983-02-14 Method for recovering soda from waste liquor from pulp manufacturing stage

Country Status (1)

Country Link
JP (1) JPS59146930A (en)

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