JPH0665797B2 - Soda recovery method - Google Patents
Soda recovery methodInfo
- Publication number
- JPH0665797B2 JPH0665797B2 JP11333986A JP11333986A JPH0665797B2 JP H0665797 B2 JPH0665797 B2 JP H0665797B2 JP 11333986 A JP11333986 A JP 11333986A JP 11333986 A JP11333986 A JP 11333986A JP H0665797 B2 JPH0665797 B2 JP H0665797B2
- Authority
- JP
- Japan
- Prior art keywords
- iron oxide
- fluidized bed
- dust collector
- cyclone
- bed furnace
- 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 - Fee Related
Links
Landscapes
- 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、不純物を除去する方法、詳しくは集
じん機捕集物を系外にブローすることにより、NaClを系
内に蓄積させないようにしたソーダ回収方法に関するも
のである。DETAILED DESCRIPTION OF THE INVENTION [Industrial field of application] The present invention relates to a direct causticizing fluidized bed system for recovering caustic soda from pulp cooking waste liquor (also referred to as black liquor) using iron oxide as a causticizing agent to remove impurities. More specifically, the present invention relates to a soda recovery method in which NaCl is not accumulated in the system by blowing the collected matter of the dust collector to the outside of the system.
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、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, when recovering caustic soda from pulp cooking waste liquid (hereinafter referred to as pulp waste liquid) generated when wood chips are digested, the lime method has been put into practical use. However, this lime method has drawbacks in that the process is complicated, waste is generated, and measures against odor and drainage are required, and the causticizing rate is low.
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(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、アルカリ廃液からの苛性ソーダ
の生成は、おそらく廃液の燃焼によって廃液中に含まれ
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 drawbacks, as shown in Japanese Patent Publication No. 51-12724, the alkaline waste liquid containing substantially no sulfur compounds discharged from the cooking and bleaching steps of the fibrin substance is concentrated and iron oxide is concentrated. A method has been proposed in which sodium hydroxide is added and burned, and the obtained sodium ferrate (sodium ferrate) is put into water to directly recover caustic soda as an extraction aqueous solution, and the iron oxide obtained as an extraction residue is circulated and reused. ing. In this method, caustic soda is produced from the alkaline waste liquid, and the organic matter contained in the waste liquid is probably decomposed by combustion of the waste liquid, and the sodium carbonate and / or sodium oxide obtained as the product is expressed by the following formula (1). And as in formula (2), reacts with iron oxide to produce sodium ferrate,
It is considered that by treating this in water, caustic soda and iron oxide can be obtained as shown in formula (3).
Na2CO3+Fe2O3→Na2Fe2O4+CO2 (1) Na2O+Fe2O3→Na2Fe2O4 (2) Na2Fe2O4+H2O→2NaOH+Fe2O3 (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。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 → 2 NaOH + Fe 2 O 3 (3) However, when applying the above method to a fluidized bed furnace, in the direct causticizing method, iron oxide (iron ore) is generally recycled and used, and only the carryover amount of a dust collector or the like is supplied. Yes (supplement rate is at most a few percent). On the other hand, granular iron ore, which is both a causticizing agent and a fluidized bed maintainer, increases the pulverization in the furnace as the number of times of re-use increases (about 10% pulverization), and other feeders Some pulverization is also seen in the handling of iron ore, causticizing process, etc. In addition, since the fluidized bed system basically uses a granular causticizing agent, the reaction molar ratio Fe / Na cannot be set to near 1.0 (equal molar ratio as shown in reaction formulas (1) and (2)). On the other hand, there is a problem that the powdery causticizing agent jumps out of the furnace immediately and the reaction cannot be expected to proceed sufficiently.
本発明者らは上記問題点を解決するために、流動床ボイ
ラ、サイクロン、電気集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-mentioned problems, the present inventors causticize powdered sodium ferrate collected by a fluidized bed boiler, a cyclone, and an electric dust collector, and then dry the dried powdered iron oxide. We developed a technology to granulate a part or all of the product using black liquor as a binder and supply it as granules to a fluidized bed furnace again, and filed a patent application as Japanese Patent Application No. 58-167927 (Japanese Patent Application Laid-Open No. 60-59190). ing.
上記の直接苛性化法は、KP法に比較して、石灰キルンを
省略し、プロセスの簡略化、省エネルギー化を目指した
優れたプロセスがあるが、クローズド化を特徴とする点
に問題がある。The above-mentioned direct causticizing method has an excellent process in which the lime kiln is omitted, the process is simplified and the energy is saved as compared with the KP method, but there is a problem in that it is characterized by being closed.
すなわち、製紙プロセスにおいては、木材チップ、工業
用水などにより、蒸解に必要な薬液以外の不純物が入り
込む。KP法では、ドレッグ、スラッジなどとともに、不
純物は沈澱物として系外に投棄されるのに対し、直接苛
性化法では系がクローズド化されているので、系外から
侵入した不純物は、系内で次第に濃縮される傾向にあ
る。この内、NaClは鉄製ソーダ生成反応に悪影響を与え
る(反応阻害となる)、Na2CO3と低温域にて溶融する共
融混合物をつくり易いなど、直接苛性化法流動床式に悪
影響を与えることが懸念されている。That is, in the papermaking process, impurities other than the chemical liquid necessary for cooking enter due to wood chips, industrial water, and the like. In the KP method, impurities such as dregs and sludge are discarded outside the system as precipitates, whereas in the direct causticization method, the system is closed, so impurities that have entered from outside the system do not enter the system. It tends to be gradually concentrated. Of these, NaCl adversely affects the iron soda formation reaction (reacts reaction) and easily forms a eutectic mixture that melts in the low temperature range with Na 2 CO 3 , which adversely affects the direct causticizing fluidized bed system. That is a concern.
本発明は上記の諸点に鑑みなされたもので、NaClを系内
に蓄積させないで、一定の値以下にその濃度を制御し、
効率よく苛性ソーダを回収できるようにした方法の提供
を目的とするものである。The present invention has been made in view of the above points, without accumulating NaCl in the system, the concentration is controlled below a certain value,
It is intended to provide a method capable of efficiently collecting caustic soda.
本願の第1の発明のソーダ回収方法は、NaClを含むパル
プ廃液を、酸化鉄を苛性化剤および流動化媒体とする流
動床炉で燃焼せしめ、ついで生成物である鉄酸ソーダを
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
集じん機に導入して集じんする方法において、電気集じ
ん機捕集物を系外にブローすることを特徴としている。The soda recovery method of the first invention of the present application is to burn a pulp waste liquid containing NaCl in a fluidized bed furnace using iron oxide as a causticizing agent and a fluidizing medium, and then add the product sodium ferrate to water. In this method, the caustic soda and iron oxide are recovered, and the exhaust gas from the fluidized bed furnace is recovered by heat in a boiler, and then introduced into a cyclone or an electrostatic precipitator to collect dust from the electrostatic precipitator outside the system. It is characterized by doing.
すなわち、ボイラ後流以降の集じん装置としては、マル
チサイクロンなどのサイクロン、電気集じん機などが用
いられ、煙道捕集粉状鉄酸ソーダのうち、NaCl含有量の
最も高い電気集じん機捕集物を系外に投棄することによ
り、系内にNaClを蓄積させることなく、流動床方式を好
適に運転することができる。That is, as a dust collector after the boiler, a cyclone such as a multi-cyclone, an electric dust collector, etc. are used, and among the flue trapped powdery sodium ferrate, the dust collector with the highest NaCl content is used. By discarding the collected material out of the system, the fluidized bed system can be suitably operated without accumulating NaCl in the system.
また本願の第2の発明のソーダ回収方法は、NaCl含有量
の高い電気集じん機捕集物の全部、およびNaCl含有量の
高いサイクロン捕集物の一部または全部を系外にブロー
することを特徴としており、これにより系内にNaClを蓄
積させることなく、流動床方式を好適に運転することが
できる。Further, the soda recovery method of the second invention of the present application is to blow all the collected matter of the electrostatic precipitator having a high NaCl content and a part or all of the collected matter of the cyclone having a high NaCl content to the outside of the system. Therefore, the fluidized bed system can be suitably operated without accumulating NaCl in the system.
サイクロン捕集物、電気集じん機捕集物のNaClの割合
は、通常、重量比で全ソーダ分の10〜70%であり、電気
集じん機捕集物では、Naの50%以上はNaClの形で含有さ
れている。The ratio of NaCl in the cyclone collected matter and the electric dust collector collected is usually 10 to 70% by weight of the total soda, and in the electric dust collector collected, 50% or more of Na is NaCl. It is contained in the form of.
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。Hereinafter, embodiments of the present invention will be illustratively described in detail with reference to the drawings. However, the arrangement of the constituent devices described in this embodiment is not limited to them unless otherwise specified, and is merely an example of description.
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%の濃黒液とし、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700〜1
100℃、望ましくは900〜1000℃とし、Fe/Naは1.0以上
となるようにする。流動層形成材としては、純鉄、鉄鉱
石(Fe2O3、Fe3O4)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。The diluted black liquor is introduced into the thin film evaporator 1, evaporated and concentrated to 50-60% black liquor, and then introduced into the disc evaporator 2 to obtain 70-80% dark liquor. It is supplied to the fluidized bed furnace 3. On the other hand, granular iron ore storage tank 4 supplies granular iron oxide to fluidized bed furnace 3. Bed temperature of fluidized bed furnace 3 is 700-1
The temperature is 100 ° C., preferably 900 to 1000 ° C., and the Fe / Na is 1.0 or more. As the fluidized bed forming material, granular iron-based granular compounds such as pure iron, iron ore (Fe 2 O 3 , Fe 3 O 4 ) sinter, reduced pellets, and granulated iron-making dust are used. . In this example, iron ore is used as iron oxide, and the replenishment is performed with granular iron ore. 5 is a fluidized bed, 6 is an air dispersion plate, and 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、分級装置11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12および粉状酸化鉄貯槽13へ
供給する。この造粒装置としては、圧縮造粒装置とする
のが好ましい。Sodium ferrate from the fluidized bed furnace 3 is introduced into the first causticizing device 8 to extract and separate into a caustic soda aqueous solution and recovered iron oxide,
After the recovered iron oxide is dried by combustion exhaust gas in the first drying device 10, it is classified into granular iron oxide and powdered iron oxide by the classifying device 11, and the granular iron oxide is charged into the granular iron ore storage tank 4, while The powdery iron oxide is supplied to the granulating device 12 and the powdery iron oxide storage tank 13. As this granulating device, a compression granulating device is preferable.
一方、ボイラ14で捕集した粉状捕集物を第2苛性化装置
15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16で燃焼排ガス
などにより乾燥した後、造粒装置12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 powdery collected matter collected by the boiler 14 is used as the second causticizing device.
Introduced into 15 and extracted into aqueous caustic soda solution and recovered iron oxide,
The separated iron oxide is separated and dried in the second drying device 16 by combustion exhaust gas or the like, and then, in the granulating device 12, the black liquor is granulated as a binder to form granular iron oxide into the iron ore storage tank 4.
電気集じん機18の捕集物の全部、または電気集じん機18
の捕集物の全部とサイクロン17の捕集物の一部もしくは
全部とを、系外にブローして、系内にNaClが蓄積するの
を防止する。All of the collected matter of the electric dust collector 18 or the electric dust collector 18
All of the collected substances of (1) and some or all of the collected substances of cyclone 17 are blown out of the system to prevent the accumulation of NaCl in the system.
このように、NaCl含有率の最も高い電気集じん機捕集物
は、全量系外にブローして排出する。サイクロン捕集物
は全量系外にブローする場合と、一部を系外にブローす
る場合と、全量を系外にブローしない場合とがある。In this way, the total amount of the collected matter of the electrostatic precipitator having the highest NaCl content is blown out of the system and discharged. There are cases where the whole amount of the cyclone collected is blown out of the system, a case where a part thereof is blown out of the system, and a case where the whole amount is not blown out of the system.
サイクロン捕集物で系外にブローしない分は、第2苛性
化装置15または第2乾燥装置16へ供給するが、冷水抽出
装置20に導入してNaClを除去抽出後、第2苛性化装置15
または第2乾燥装置16へ供給する場合もある。The part of the cyclone collected that is not blown out of the system is supplied to the second causticizing device 15 or the second drying device 16, but is introduced into the cold water extracting device 20 to remove and extract NaCl, and then the second causticizing device 15
Alternatively, it may be supplied to the second drying device 16.
上記のように本発明の方法によれば、NaClを系内に蓄積
させないで、一定のレベル以下にその濃度をコントロー
ルし、苛性化反応を好適に進行させるとともに、酸化
鉄、鉄酸ソーダを流動化媒体とする流動層を、良好な流
動化状態を保つことが可能になるという効果を奏する。As described above, according to the method of the present invention, NaCl is not accumulated in the system, its concentration is controlled to a certain level or less, and the causticizing reaction is appropriately advanced, and iron oxide and sodium ferrate are allowed to flow. The fluidized bed used as the fluidizing medium can maintain an excellent fluidized state.
図面は本発明のソーダ回収方法を実施する装置の一例を
示すフローシートである。 1……薄膜式エバポレータ、2……ディスクエバポレー
タ、3……流動床炉、4……粒状鉄鉱石貯槽、5……流
動層、6……空気分散板、7……風箱、8……第1苛性
化装置、10……第1乾燥装置、11……分級装置、12……
造粒装置、13……粉状酸化鉄貯槽、14……ボイラ、15…
…第2苛性化装置、16……第2乾燥装置、17……サイク
ロン、18……電気集じん機、20……冷水抽出装置The drawings are flow sheets showing an example of an apparatus for carrying out the soda recovery method of the present invention. 1 ... Thin film evaporator, 2 ... Disk evaporator, 3 ... Fluidized bed furnace, 4 ... Granular iron ore storage tank, 5 ... Fluidized bed, 6 ... Air dispersion plate, 7 ... Wind box, 8 ... 1st causticizing device, 10 ... 1st drying device, 11 ... Classifying device, 12 ...
Granulator, 13 …… Powdery iron oxide storage tank, 14 …… Boiler, 15…
… Second causticizer, 16 …… Second dryer, 17 …… Cyclone, 18 …… Electrostatic precipitator, 20 …… Cold water extractor
Claims (2)
剤および流動化媒体とする流動床炉で燃焼せしめ、つい
で生成物である鉄酸ソーダ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、電気集じん機に導入して集じん
する方法において、電気集じん機捕集物を系外にブロー
することを特徴とするソーダ回収方法。1. A pulp waste liquor containing NaCl is combusted in a fluidized bed furnace using iron oxide as a causticizing agent and a fluidizing medium, and then the product sodium ferrate is put into water to remove caustic soda and iron oxide. In the method of collecting and collecting the heat of the fluidized bed furnace exhaust gas with a boiler, and introducing it to a cyclone or an electric dust collector to collect dust, a soda characterized by blowing the collected electricity dust collector to the outside of the system Recovery method.
剤および流動化媒体とする流動床炉で燃焼せしめ、つい
で生成物である鉄酸ソーダ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、電気集じん機に導入して集じん
する方法において、電気集じん機捕集物の全部、および
サイクロン捕集物の一部または全部を系外にブローする
ことを特徴とするソーダ回収方法。2. A pulp waste liquor containing NaCl is combusted in a fluidized bed furnace using iron oxide as a causticizing agent and a fluidizing medium, and then the product sodium ferrate is charged into water to remove caustic soda and iron oxide. In the method of recovering and collecting the heat of the fluidized bed furnace exhaust gas with a boiler, and then introducing it into a cyclone or an electric dust collector to collect dust, all of the collected matter of the electric dust collector and a part of the collected matter of the cyclone or A soda recovery method characterized by blowing all of it out of the system.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP11333986A JPH0665797B2 (en) | 1986-05-16 | 1986-05-16 | Soda recovery method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP11333986A JPH0665797B2 (en) | 1986-05-16 | 1986-05-16 | Soda recovery method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS62268886A JPS62268886A (en) | 1987-11-21 |
| JPH0665797B2 true JPH0665797B2 (en) | 1994-08-24 |
Family
ID=14609736
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP11333986A Expired - Fee Related JPH0665797B2 (en) | 1986-05-16 | 1986-05-16 | Soda recovery method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0665797B2 (en) |
-
1986
- 1986-05-16 JP JP11333986A patent/JPH0665797B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPS62268886A (en) | 1987-11-21 |
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