JPS62268882A - Treatment of iron acid soda - Google Patents

Treatment of iron acid soda

Info

Publication number
JPS62268882A
JPS62268882A JP11333586A JP11333586A JPS62268882A JP S62268882 A JPS62268882 A JP S62268882A JP 11333586 A JP11333586 A JP 11333586A JP 11333586 A JP11333586 A JP 11333586A JP S62268882 A JPS62268882 A JP S62268882A
Authority
JP
Japan
Prior art keywords
iron oxide
fluidized bed
causticizing
cyclone
boiler
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
JP11333586A
Other languages
Japanese (ja)
Inventor
伊東 速水
永井 千秋
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 JP11333586A priority Critical patent/JPS62268882A/en
Publication of JPS62268882A publication Critical patent/JPS62268882A/en
Pending legal-status Critical Current

Links

Landscapes

  • 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、パルプ蒸解廃液(黒液ともいう)から酸化鉄
を苛性化剤として苛性ソーダを回収する直接苛性化法流
動床方式において、集しん装置捕集鉄酸ソーダを効率よ
く循環処理する方法に関するものである。
[Detailed Description of the Invention] [Field of Industrial Application] The present invention is a direct causticizing fluidized bed system in which caustic soda is recovered from pulp cooking waste liquor (also called black liquor) using iron oxide as a causticizing agent. The present invention relates to a method for efficiently circulating and treating sodium ferrate collected by a device.

〔従来の技術〕[Conventional technology]

従来、木材チップを蒸解したときに発生するパルプ蒸解
廃液(以下、バルブ廃液という)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。
BACKGROUND ART Conventionally, the lime method has been put into practical use when recovering caustic soda from pulp cooking waste liquid (hereinafter referred to as valve waste liquid) 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51−1272
4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(鉄酸ナトリウム)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、アルカリ廃ン夜からの苛
性ソーダの生成は、おそらく廃液の燃焼によって廃液中
に含まれていた存機吻は分解し、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+11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って(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
As shown in Publication No. 4, the alkaline waste liquid 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, resulting in sodium ferrate ( A method has been proposed in which caustic soda is directly recovered as an extracted aqueous solution by pouring sodium ferrate) into water, and the iron oxide obtained as an extraction residue is recycled and reused. In this method, the generation of caustic soda from the alkaline wastewater is probably caused by the combustion of the wastewater, which decomposes the remaining organic matter contained in the wastewater, and the resulting products are soda carbonate and/or soda oxide, which are It is thought that sodium ferrate is produced by reacting with iron oxide as shown in equations +11 and (2), and by treating this in water, caustic soda and iron oxide are obtained as shown in equation (3).

NazCOi +F6!03 = NatFezOn 
+COt   [1)Na!0+Fe2O,l−4Na
tFet04(2)NalFetOa + HzO= 
2NaOH+ Petos    [3)しかし上記の
方法を流動床炉に適用するにあたり、直接苛性化法では
、酸化鉄(鉄鉱石)は再生循環使用するのが大原則であ
り、集じん機などのキャリーオーバー分のみ補給する(
補給率は高々数%のオーダーである)、一方、苛性化反
応剤であると同時に流動層維持剤である粒状鉄鉱石は再
生使用回数の増加に従い、炉内での粉化が増大すること
(約10%前後は粉化)、その他フィーダーでの鉄鉱石
のハンドリング、苛性化工程などでも若干粉化が見られ
る。また流動床方式では基本的に粒状の苛性化剤を使用
するため、反応モル比Fe/Naを1.0近くに設定す
ることができず(反応式(1)、(2)に示すように等
モル反応)、一方、粉状の苛性化剤では炉内からすぐ飛
び出してしまい反応の進行が十分期待できないなどの問
題があった。
NazCOi +F6!03 = NatFezOn
+COt [1) Na! 0+Fe2O, l-4Na
tFet04(2)NalFetOa + HzO=
2NaOH+ Petos [3] However, when applying the above method to a fluidized bed furnace, in the direct causticizing method, the basic principle is to recycle and reuse iron oxide (iron ore), and to remove carryover from dust collectors, etc. Replenish only (
The replenishment rate is on the order of a few percent at most), while granular iron ore, which is a causticizing reactant as well as a fluidized bed maintenance agent, becomes more powdered in the furnace as the number of recycled uses increases ( Approximately 10% of the iron ore is pulverized), and some pulverization is also seen during iron ore handling in the feeder, causticizing process, etc. Furthermore, since the fluidized bed method basically uses a granular causticizing agent, it is not possible to set the reaction molar ratio Fe/Na close to 1.0 (as shown in reaction formulas (1) and (2), On the other hand, powdered causticizing agents have the problem that they immediately jump out of the furnace, making it impossible to expect the reaction to proceed sufficiently.

本発明者らは上記の問題点を解決するために、流動床ボ
イラ、サイクロン、電気業じん機で捕集された粉状鉄酸
ソーダを苛性化した後、乾燥し、乾燥した粉状酸化鉄の
一部あるいは全部を黒液をバインダーとして造粒し、再
び粒状物として流動床炉に供給する技術を開発し、特願
昭58−’167927号(特開昭60−59190号
)として特許出願している。
In order to solve the above problems, the present inventors causticized powdered sodium ferrate collected in a fluidized bed boiler, cyclone, and electric industrial dust machine, and then dried the powdered iron oxide powder. Developed a technology to granulate part or all of it using black liquor as a binder and feed it again as granules to a fluidized bed furnace, and filed a patent application as Japanese Patent Application No. 58-'167927 (Japanese Unexamined Patent Publication No. 60-59190). are doing.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

しかしながら、上記従来の方式はつぎのような問題点を
有している。
However, the above conventional method has the following problems.

+11  サイクロン補集物および電気業じん機補集物
は粒径が細かく、粉体として吸湿し易く、かつ安息角が
大であるなどハンドリング物性が悪く、ホッパー、配管
内での架橋、閉塞が起こり易い。
+11 Cyclone collected material and industrial dust machine collected material have small particle sizes, easily absorb moisture as powder, and have poor handling properties such as a large angle of repose, leading to bridging and clogging in hoppers and piping. easy.

(2)  サイクロン補集物および電気業じんi捕集物
は微粉であるため、苛性化工程における苛性ソーダ抽出
、乾燥工程における脱水が効率的に実施し難い、すなわ
ち、残留ナトリウムおよび残留水分が多くなり、流動床
炉への供給量が多くなる。
(2) Since the cyclone collection material and the electrical industry dust collection material are fine powders, it is difficult to efficiently perform caustic soda extraction in the causticizing process and dehydration in the drying process, which means that residual sodium and residual moisture are large. , the amount supplied to the fluidized bed furnace increases.

(3)  サイクロン捕集物および電気業じん機捕集物
の苛性化率が低い。
(3) The causticization rate of the cyclone collected material and the industrial dust machine collected material is low.

本発明は上記の諸点に鑑みなされたもので、サイクロン
捕集物および/または電気業じん機捕集物を、苛性化す
ることなくそのまま造粒工程に供給することにより、ハ
ンドリングを容易とし、かつ苛性化工程、乾燥工程を効
率的に行うことができ、しかも苛性化率の向上を図るこ
とができる方法の提供を目的とするものである。
The present invention was made in view of the above points, and it facilitates handling by supplying the cyclone-collected material and/or the industrial dust machine-collected material to the granulation process as it is without causticizing it. The object of the present invention is to provide a method that can efficiently perform a causticizing step and a drying step and can improve the causticizing rate.

c問題点を解決するための手段および作用〕本発明の鉄
酸ソーダの処理方法は、バルブ廃液を濃縮した後、酸化
鉄を苛性化剤および流動層維持剤として加えて流動床炉
で燃焼せしめ、ついで生成物を水中に投入して苛性ソー
ダお本び酸化鉄を回収し、流動床炉排ガスをボイラで熱
回収した後、サイクロン、電気業じん機などの集じん装
置に導入して集しんする方法において、ボイラ後流以降
の集じん装置捕集物を、苛性化することなくそのまま、
造粒工程に供給することを特徴としている。
Means and operation for solving the problems c] The method for treating sodium ferrate of the present invention involves concentrating the valve waste liquid, adding iron oxide as a causticizing agent and a fluidized bed maintenance agent, and burning it in a fluidized bed furnace. Then, the product is poured into water to recover caustic soda and iron oxide, and after the fluidized bed furnace exhaust gas is heat recovered in a boiler, it is introduced into a dust collection device such as a cyclone or electric dust machine to collect it. In this method, the collected material from the dust collector downstream of the boiler is directly treated without being causticized.
It is characterized by being supplied to the granulation process.

ボイラ後流以降の集しん装置としては、マルチサイクロ
ンなどのサイクロン、電気業じん機などが用いられ、サ
イクロン捕集物および電気業しん機補集物、または電気
業じん機浦集物を造粒工1jに供給する。また造粒は、
圧縮造粒とするのが好ましい。
A cyclone such as a multi-cyclone, an electric industrial dust machine, etc. are used as a dust collection device after the boiler, and the cyclone collected material, electric industrial dust machine collection material, or electric industrial dust machine ura collection material is granulated. Supply to Engineering 1j. In addition, granulation is
Compression granulation is preferred.

〔実施例〕〔Example〕

以下、本発明の実施例を図面に基づいて例示的に詳細に
説明する。ただしこの実施例に記載されている構成機器
の配置などは、とくに特定的な記載がない限りは、それ
らのみに限定するものではなく、単なる説明例にすぎな
い。
Embodiments of the present invention will be described in detail below by way of example based on the drawings. However, unless there is a specific description, the arrangement of the component devices described in this embodiment is not limited thereto, and is merely an illustrative example.

希黒液を薄膜式エバポレータ1に導入し、蒸発、濃縮し
て50〜60%の黒液とした後、ディスクエバポレータ
2に導入して70〜80%の2474液とし、この濃黒
液を流動床炉3に供給する。一方、流動床炉3に粒状鉄
鉱石貯槽4から粒状酸化鉄を供給する。流動床炉3の層
温度は700〜1100℃、望ましくは900〜100
0℃とし、Fe/Naは1.0以上となるようにする。
The dilute black liquor is introduced into the thin film evaporator 1, evaporated and concentrated to make a 50-60% black liquor, and then introduced into the disk evaporator 2 to make a 70-80% 2474 liquid, and this concentrated black liquor is fluidized. It is supplied to the floor furnace 3. On the other hand, granular iron oxide is supplied to the fluidized bed furnace 3 from the granular iron ore storage tank 4 . The bed temperature of the fluidized bed furnace 3 is 700 to 1100°C, preferably 900 to 100°C.
The temperature is set to 0°C, and Fe/Na is set to be 1.0 or more.

a動層形成材としては、純鉄、鉄鉱石(FeJi、Fe
1Oa ) 、焼結鉱、還元ペレット、製鉄ダストを造
粒したものなどの粒状の鉄系の粒状の化合物が用いられ
る。本例においては、酸化鉄として鉄鉱石を使用し、補
給は粒状鉄鉱石で行う。5は流動層、6は空気分散板、
7は風箱である。
a. Pure iron, iron ore (FeJi, Fe
1Oa), sintered ore, reduced pellets, granulated iron-based dust, and other granular iron-based granular compounds are used. In this example, iron ore is used as the iron oxide, and granular iron ore is used for replenishment. 5 is a fluidized bed, 6 is an air distribution plate,
7 is a wind box.

流動床炉3からの鉄酸ソーダを第1苛性化装置8に導入
して苛性ソーダ水溶液と回収酸化鉄とに抽出、分離し、
この回収酸化鉄を第1乾燥装置10で燃焼排ガスなどに
より乾燥した後、鉄鉱石貯槽4へ投入する。
The ferric acid soda from the fluidized bed furnace 3 is introduced into the first causticizing device 8 and extracted and separated into a caustic soda aqueous solution and recovered iron oxide,
After drying the recovered iron oxide using combustion exhaust gas or the like in a first drying device 10, it is charged into an iron ore storage tank 4.

一方、ボイラ11で捕集した粉状捕集物を第2苛性化装
置12へ導入して苛性ソーダ水溶液と回収酸化鉄とに抽
出、分離し、この回収酸化鉄を第2乾燥装置13で燃焼
排ガスなどにより乾燥した後、造粒装置16で黒液をバ
インダーとして造粒して粒状酸化鉄とし鉄鉱石貯槽4へ
投入する。
On the other hand, the powdered material collected in the boiler 11 is introduced into the second causticizing device 12 where it is extracted and separated into a caustic soda aqueous solution and recovered iron oxide. After drying, the iron ore is granulated in a granulator 16 using black liquor as a binder to form granular iron oxide, which is then charged into the iron ore storage tank 4.

サイクロン14および電気集じんa15で捕集した微粉
状の捕集物を苛性化することなく、直接、造粒装置16
へ送り、ここで黒液をバインダーとして造粒し、粒状酸
化鉄として鉄鉱石貯槽4へ投入して再使用に供する。
The fine powder collected by the cyclone 14 and the electrostatic precipitator A15 is directly processed into the granulation device 16 without causticizing it.
Here, the iron ore is granulated using black liquor as a binder, and then put into an iron ore storage tank 4 as granular iron oxide for reuse.

なお最も微細な電気集じん機捕集物のみを苛性化するこ
となく、そのまま造粒装置16へ送って造粒する場合も
ある。この場合は、サイクロン捕集物は第2苛性化装置
12へ供給する。
Note that there are cases where only the finest electrostatic precipitator-collected material is sent as it is to the granulator 16 for granulation without being causticized. In this case, the cyclone catch is supplied to the second causticizing device 12.

第2図は本発明の方法を実施する装置の他の例を示して
いる0本例は、第1乾燥装置10で得た乾燥酸化鉄を分
級装置17で粒状酸化鉄と粉状酸化鉄とに分級し、粒状
酸化鉄を粒状鉄鉱石貯槽4に投入し、一方、粉状酸化鉄
を造粒装置16に供給して造粒するように構成したもの
である。なおサイクロン捕集物、電気集じん機捕集物を
乾燥後の再生酸化鉄と混合する場合は、捕集物の顕熱を
再生酸化鉄の再吸湿防止に利用することができる(再生
酸化鉄は貯蔵期間にもよるが、貯蔵中に再吸湿し易い傾
向にある)。他の構成、作用は第1図の場合と同様であ
る。
FIG. 2 shows another example of an apparatus for carrying out the method of the present invention. In this example, dry iron oxide obtained in the first drying apparatus 10 is separated into granular iron oxide and powdered iron oxide in a classifier 17. The granular iron oxide is charged into a granular iron ore storage tank 4, and the powdered iron oxide is supplied to a granulator 16 for granulation. In addition, when mixing the cyclone collected material or the electrostatic precipitator collected material with the recycled iron oxide after drying, the sensible heat of the collected material can be used to prevent the regenerated iron oxide from reabsorbing moisture (regenerated iron oxide Although it depends on the storage period, it tends to re-absorb moisture during storage). Other configurations and operations are the same as those in FIG. 1.

〔発明の効果〕〔Effect of the invention〕

本発明は上記のように構成されているので、っぎのよう
な効果を有している。
Since the present invention is configured as described above, it has the following effects.

(1)苛性化率の悪いサイクロン捕集物および/または
電気集しん機捕集吻を、苛性化することなくそのまま造
粒した後、燃焼させてリサイクルするので、苛性化率の
上昇が期待でき、回収苛性ソーダの品質向上を図ること
ができる。
(1) Since the cyclone collection material and/or the electrostatic precipitator collection material, which has a poor causticization rate, is granulated without being causticized and then burned and recycled, an increase in the causticization rate can be expected. , it is possible to improve the quality of recovered caustic soda.

(2)苛性化工程、乾燥工程の効率的運用、操業が可能
となる(タラリファイアなどの設備を簡略化することが
できる)。
(2) Efficient operation and operation of the causticizing process and drying process becomes possible (equipment such as a talarifier can be simplified).

(3)生成した粉状鉄酸ソーダのハンドリングが容易と
なる。
(3) Handling of the generated powdered sodium ferrate becomes easier.

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

第1図は本発明の鉄酸ソーダの処理方法を実施する装置
の一例を示すフローシート、第2図は本発明の方法を実
施する装置の他の例を示すフローシートである。
FIG. 1 is a flow sheet showing an example of an apparatus for implementing the method of treating sodium ferrate of the present invention, and FIG. 2 is a flow sheet showing another example of an apparatus for implementing the method of the present invention.

Claims (1)

【特許請求の範囲】[Claims] 1 バルブ廃液を濃縮した後、酸化鉄を苛性化剤および
流動層維持剤として加えて流動床炉で燃焼せしめ、つい
で生成物を水中に投入して苛性ソーダおよび酸化鉄を回
収し、流動床炉排ガスをボイラで熱回収した後、サイク
ロン、電気集じん機などの集じん装置に導入して集じん
する方法において、ボイラ後流以降の集じん装置捕集物
を、苛性化することなくそのまま、造粒工程に供給する
ことを特徴とする鉄酸ソーダの処理方法。
1 After concentrating the valve waste liquid, add iron oxide as a causticizing agent and fluidized bed maintenance agent and combust it in a fluidized bed furnace.Then, the product is poured into water to recover caustic soda and iron oxide, and the fluidized bed furnace exhaust gas is In a method in which heat is recovered in a boiler and then introduced into a dust collector such as a cyclone or an electrostatic precipitator to collect dust, the collected material from the dust collector downstream of the boiler is directly produced without being causticized. A method for treating sodium ferrate characterized by supplying it to a granulation process.
JP11333586A 1986-05-16 1986-05-16 Treatment of iron acid soda Pending JPS62268882A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11333586A JPS62268882A (en) 1986-05-16 1986-05-16 Treatment of iron acid soda

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11333586A JPS62268882A (en) 1986-05-16 1986-05-16 Treatment of iron acid soda

Publications (1)

Publication Number Publication Date
JPS62268882A true JPS62268882A (en) 1987-11-21

Family

ID=14609633

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11333586A Pending JPS62268882A (en) 1986-05-16 1986-05-16 Treatment of iron acid soda

Country Status (1)

Country Link
JP (1) JPS62268882A (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS55111886A (en) * 1979-02-22 1980-08-28 Babcock Hitachi Kk Apparatus for removing chloride within dust collected from combustion gas
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

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS55111886A (en) * 1979-02-22 1980-08-28 Babcock Hitachi Kk Apparatus for removing chloride within dust collected from combustion gas
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

Similar Documents

Publication Publication Date Title
CA1135942A (en) Method of burning sulfur-containing fuels in a fluidized bed boiler
JPS60232233A (en) Method for oxidation of flue gas desulfurization absorbent
US3758668A (en) So2 absorption system with regeneration of absorbent
JPS62276095A (en) Recovery of caustic soda from alkali pulp waste liquid
JPS62268882A (en) Treatment of iron acid soda
US2334621A (en) Method of treating sulphite waste liquors
JPS62268885A (en) Treatment of iron acid soda
JPS62268888A (en) Supply of iron oxide granule
US3414468A (en) Process of regenerating pulping liquor from cellulose digestion waste liquor
JPS63120188A (en) Fluidized bed type soda recovery method
WO1983003407A1 (en) Alkali regeneration process
JPH0411673B2 (en)
JPS62268883A (en) Soda recovery method
JPS62268886A (en) Soda recovery method
JPS62268884A (en) Soda recovery method
JPH08505081A (en) Process for pelletizing alkali metal ferrate particles
JPS58132192A (en) Direct caustification using fluidized layer furnace
JPH0348127B2 (en)
JPH0662296B2 (en) Reclaimed metal oxide treatment method
JPH0368152B2 (en)
JPS60181392A (en) Direct causticizing method using fluidized bed
JPS62224641A (en) Treatment of dust and sludge
JPH0112804B2 (en)
JPH0145512B2 (en)
WO2001047809A1 (en) Process for treating sodium aluminosilicate