JPH0411673B2 - - Google Patents
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- Publication number
- JPH0411673B2 JPH0411673B2 JP58167927A JP16792783A JPH0411673B2 JP H0411673 B2 JPH0411673 B2 JP H0411673B2 JP 58167927 A JP58167927 A JP 58167927A JP 16792783 A JP16792783 A JP 16792783A JP H0411673 B2 JPH0411673 B2 JP H0411673B2
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- JP
- Japan
- Prior art keywords
- iron oxide
- fluidized bed
- bed furnace
- dust
- recovered
- 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
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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とともに、苛性
化剤の補給量を少なくすることができる方法に関
するものである。[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a method for efficiently recovering caustic soda from pulp cooking waste liquor (also referred to as black liquor) and reducing the amount of causticizing agent supplied. It is something.
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、パルプ排液という)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 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的
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 discharged from the process of cooking and bleaching cellulose materials, which is substantially free of sulfur compounds, is concentrated and then burnt with the addition of iron oxide to produce sodium ferrate. A method has been proposed in which caustic soda is recovered directly 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 probably caused by the combustion of the waste liquid, which decomposes the organic matter contained in the waste liquid, and the resulting products are soda carbonate and/or soda oxide, which are It is thought that by reacting with iron oxide to produce sodium ferrate as shown in equations ) and (2), and treating this in water, caustic soda and iron oxide can be obtained as shown in equation (3). .
Na2CO3+Fe2O3→Na2Fe2O4+CO2 ……(1)
Na2O+Fe2O3→Na2Fe2O4 ……(2)
Na2Fe2O4+H2O→2NaON+Fe2O3 ……(3)
一方、特開昭58−132191号公報には、酸化鉄と
黒液とを混合槽で混合した後燃焼炉に供給する工
程と、燃焼により生じた鉄酸ナトリウムを含む粉
状物を溶解槽に供給する工程と、酸化鉄を分離し
苛性ソーダを回収する工程と、分離した酸化鉄を
前記混合槽に供給する工程とからなるパルプ製造
工程において直接可性化方法が記載されている。 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→ 2NaON+Fe 2 O 3 ...(3) On the other hand, JP-A-58-132191 describes a process of mixing iron oxide and black liquor in a mixing tank and then supplying the mixture to a combustion furnace, and a process of mixing iron oxide and black liquor in a mixing tank and then supplying the sodium ferrate produced by combustion. A direct solubilization method in the pulp manufacturing process, which comprises a step of supplying a powder containing powder to a dissolution tank, a step of separating iron oxide and recovering caustic soda, and a step of supplying the separated iron oxide to the mixing tank. is listed.
また、特開昭58−132192号公報には、黒液と酸
化鉄粉とを混合槽で予め混合した後、流動層炉で
燃焼し、燃焼排ガス中の粉状鉄酸ナトリウムを集
塵装置で捕集し、ついで、苛性ソーダと酸化鉄に
加水分解して、回収した酸化鉄と黒液とを前記混
合槽で混合する流動層炉を用いた直接苛性化方法
が記載されている。 Furthermore, in Japanese Patent Application Laid-Open No. 58-132192, black liquor and iron oxide powder are mixed in advance in a mixing tank, then burned in a fluidized bed furnace, and the powdered sodium ferrate in the combustion exhaust gas is collected in a dust collector. A direct causticizing method using a fluidized bed furnace is described in which iron oxide is collected, then hydrolyzed into caustic soda and iron oxide, and the recovered iron oxide and black liquor are mixed in the mixing tank.
しかし上記の特公昭51−12724号公報記載の方
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、集じん機などのキヤリーオーバー
分のみ補給する(補給率は高々数%のオーダーで
ある)。一方、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)、その他フイ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
からすず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つた。
However, when applying the method described in the above-mentioned Japanese Patent Publication No. 51-12724 to a fluidized bed furnace, the general principle is that iron oxide (iron ore) is regenerated and recycled in the direct causticizing method, and a dust collector or other (The replenishment rate is on the order of a few percent at most). On the other hand, as the number of times granular iron ore is recycled and used increases, the amount of pulverization in the furnace increases (approximately 10% is pulverized), and there is also some pulverization during handling of iron ore in the feeder, causticization process, etc. can be seen. In addition, 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 equations (1) and (2), equimolar On the other hand, there were problems with powdered causticizing agents, such as tin being thrown out of the furnace, making it impossible to expect the reaction to proceed sufficiently.
また、上記の特開昭58−132191号公報、特開昭
58−132192号公報には、本発明の特徴である「流
動床炉からの鉄酸ソーダおよびボイラ、サイクロ
ン、電気集じん機からのダストを加水分解装置に
導入して苛性ソーダと回収酸化鉄とに分離した
後、粒状酸化鉄を流動床炉へ供給し、粉状酸化鉄
を黒液と混合し、ついでこの混合物を流動床炉に
投入する」という技術的思想は、何も記載されて
いない。 In addition, the above-mentioned Japanese Patent Application Laid-Open No. 58-132191,
Publication No. 58-132192 describes the feature of the present invention as follows: ``Ferrous acid soda from a fluidized bed furnace and dust from a boiler, cyclone, and electrostatic precipitator are introduced into a hydrolysis device to convert them into caustic soda and recovered iron oxide. There is no mention of the technical concept of "after separation, the granular iron oxide is fed to a fluidized bed furnace, the powdered iron oxide is mixed with black liquor, and then this mixture is fed into the fluidized bed furnace."
本発明は上記の諸点に鑑みなされたもので、回
収した粒状酸化鉄を流動床炉へそのまま循環し、
ボイラ、サイクロン、電気集じん機から回収した
粉状酸化鉄を黒鉄と予混合して循環使用すること
により、反応表面積が大きくなつて黒液と酸化鉄
との反応率が向上するとともに、酸化鉄の補給量
を少なくすることができ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 involves circulating recovered granular iron oxide directly to a fluidized bed furnace.
By premixing powdered iron oxide recovered from boilers, cyclones, and electrostatic precipitators with black iron and circulating it, the reaction surface area increases and the reaction rate between black liquor and iron oxide improves. The purpose of this invention is to provide a method that can reduce the amount of replenishment.
上記の目的を達成するために、本願の第1の発
明のパルプ廃液から苛性ソーダを回収する方法
は、第1図に示すように、パルプ廃液を濃縮した
後、酸化鉄を苛性化剤として加えて流動床炉3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し、流動床炉排ガス
をボイラ5で熱回収し、サイクロン6、電気集じ
ん機7などの集じん装置に通して集じんする方法
において、
流動床炉3に粒状の新酸化鉄を供給し、流動床
炉3からの鉄酸ソーダおよびボイラ5、サイクロ
ン6、電気集じん機7からのダストを加水分解装
置8に導入して苛性ソーダと回収酸化鉄とに分離
した後、この回収酸化鉄を粉状酸化鉄と粒状酸化
鉄とに分級し、粒状酸化鉄を流動床炉3へ供給
し、粉状酸化鉄と濃縮パルプ廃液とを混合し、つ
いでこの混合物を流動床炉3に投入することを特
徴としている。
In order to achieve the above object, the method for recovering caustic soda from pulp waste liquid according to the first invention of the present application involves, as shown in FIG. 1, adding iron oxide as a causticizing agent after concentrating the pulp waste liquid. The product is combusted in a fluidized bed furnace 3, and then the product is poured into water to recover caustic soda and a causticizing agent.The fluidized bed furnace exhaust gas is heat recovered in a boiler 5, and then collected in a cyclone 6, an electrostatic precipitator 7, etc. In the method of collecting dust through a device, granular new iron oxide is supplied to the fluidized bed furnace 3, and ferric acid soda from the fluidized bed furnace 3 and dust from the boiler 5, cyclone 6, and electrostatic precipitator 7 are added with water. After being introduced into the decomposition device 8 and separated into caustic soda and recovered iron oxide, the recovered iron oxide is classified into powdered iron oxide and granular iron oxide, and the granular iron oxide is supplied to the fluidized bed furnace 3 to be separated into powdered iron oxide. The method is characterized in that iron oxide and concentrated pulp waste liquid are mixed, and then this mixture is charged into a fluidized bed furnace 3.
また、本願の第2の発明の方法は、第2図に示
すように、流動床炉3に粒状の新酸化鉄を供給
し、流動床炉3からの粒状鉄酸ソーダを第1加水
分解装置8aに導入して苛性ソーダと回収粒状酸
化鉄とに分離し、この回収粒状酸化鉄を流動床炉
3へ供給し、ボイラ5、サイクロン6、電気集じ
ん機7からのダストを第2加水分解装置8bに導
入して苛性ソーダと回収粉状酸化鉄とに分離し、
この回収粉状酸化鉄と濃縮パルプ廃液とを混合
し、ついでこの混合物を流動床炉3に投入するこ
とを特徴としている。 Moreover, as shown in FIG. 2, the method of the second invention of the present application supplies granular new iron oxide to the fluidized bed furnace 3, and converts the granular sodium ferrate from the fluidized bed furnace 3 into the first hydrolysis device. 8a to separate caustic soda and recovered granular iron oxide, and the recovered granular iron oxide is supplied to the fluidized bed furnace 3, and the dust from the boiler 5, cyclone 6, and electrostatic precipitator 7 is transferred to the second hydrolysis device. 8b to separate into caustic soda and recovered powdered iron oxide,
The method is characterized in that the recovered powdered iron oxide and the concentrated pulp waste liquid are mixed, and then this mixture is charged into the fluidized bed furnace 3.
また、本願の第3の発明の方法は、第3図に示
すように、流動床炉3に粒状の新酸化鉄を供給
し、ボイラ排ガスを第1サイクロン6aで集じん
した後、排ガスの少なくとも一部を乾燥器12に
導入して濃縮パルプ廃液と粉状酸化鉄との混合物
を予熱乾燥し、この乾燥物を流動床炉3に投入す
るとともに、乾燥器12の排ガスを第2サイクロ
ン6b、電気集じん機7に通して集じんし、流動
床炉3からの鉄酸ソーダ、ボイラ5、第1サイク
ロン6aからのダストを加水分解装置8に導入し
て苛性ソーダと回収酸化鉄とに分離し、この回収
酸化鉄を粒状酸化鉄と粉状酸化鉄とに分級した
後、粒状酸化鉄を流動床炉3へ供給し、粉状酸化
鉄および第2サイクロン6b、電気集じん機7か
らのダストの濃縮パルプ廃液とを混合し、ついで
この混合物を前記乾燥器12へ供給することを特
徴としている。 Further, as shown in FIG. 3, the method of the third invention of the present application is to supply granular new iron oxide to the fluidized bed furnace 3, collect dust from the boiler exhaust gas in the first cyclone 6a, and then collect at least one part of the exhaust gas. A portion of the mixture of concentrated pulp waste liquid and powdered iron oxide is introduced into the dryer 12 to be preheated and dried, and this dried product is introduced into the fluidized bed furnace 3, and the exhaust gas from the dryer 12 is transferred to the second cyclone 6b, The dust is collected through an electrostatic precipitator 7, and the ferric acid soda from the fluidized bed furnace 3, the boiler 5, and the dust from the first cyclone 6a are introduced into a hydrolysis device 8 and separated into caustic soda and recovered iron oxide. After classifying the recovered iron oxide into granular iron oxide and powdered iron oxide, the granular iron oxide is supplied to the fluidized bed furnace 3, and the powdered iron oxide and the dust from the second cyclone 6b and the electrostatic precipitator 7 are collected. The method is characterized in that it is mixed with a concentrated pulp waste liquid, and then this mixture is supplied to the dryer 12.
さらに、本願の第4の発明の方法は、第4図に
示すように、流動床炉3に粒状の新酸化鉄を供給
し、ボイラ排ガスを第1サイクロン6aで集じん
した後、排ガスの少なくとも一部を乾燥器12に
導入して濃縮パルプ廃液と粉状酸化鉄との混合物
を予熱乾燥し、この乾燥物を流動床炉3に投入す
るとともに、乾燥器12の排ガスを第2サイクロ
ン6b、電気集じん機7に通して集じんし、流動
床炉3からの鉄酸ソーダを第1加水分解装置8a
に導入して苛性ソーダと回収粒状酸化鉄とに分離
し、この回収粒状酸化鉄を流動床炉3へ供給し、
ボイラ5、第1サイクロン6aからのダストを第
2加水分解装置8bに導入して苛性ソーダと回収
粉状酸化鉄とに分離し、この回収粉状酸化鉄およ
び第2サイクロン6b、電気集じん機7からのダ
ストと濃縮パルプ廃液とを混合し、ついでこの混
合物を前記乾燥器12へ供給することを特徴とし
ている。 Furthermore, as shown in FIG. 4, in the method of the fourth invention of the present application, granular new iron oxide is supplied to the fluidized bed furnace 3, and after the boiler exhaust gas is collected in the first cyclone 6a, at least A portion of the mixture of concentrated pulp waste liquid and powdered iron oxide is introduced into the dryer 12 to be preheated and dried, and this dried product is introduced into the fluidized bed furnace 3, and the exhaust gas from the dryer 12 is transferred to the second cyclone 6b, Dust is collected through an electrostatic precipitator 7, and sodium ferrate from the fluidized bed furnace 3 is passed through the first hydrolysis device 8a.
to separate into caustic soda and recovered granular iron oxide, and supply the recovered granular iron oxide to a fluidized bed furnace 3,
The dust from the boiler 5 and the first cyclone 6a is introduced into the second hydrolysis device 8b and separated into caustic soda and recovered powdered iron oxide, and the recovered powdered iron oxide, the second cyclone 6b, and the electrostatic precipitator 7 It is characterized in that the dust from the dryer and the concentrated pulp waste liquid are mixed, and then this mixture is supplied to the dryer 12.
以下、本発明の実施例を図面に基づいて詳細に
説明する。第1図は本発明の方法を実施する装置
の一例を示している。希黒液を真空蒸発器、回転
デイスク型蒸発器などの蒸発器1に導入し、蒸
発、濃縮して60〜80%の濃黒液とした後、こと濃
黒液を混合槽2へ送る。一方、流動床炉3に粒状
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900〜1000℃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、
還元ペレツト、製鉄ダストを造粒したものなどの
粒状の鉄系化合物、SiO2、AI2O3、Cr2O3、
MgO、CaOなど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。補給粒状鉄鉱石は、流
動層形成材と同じ(0.2〜3.0mm)、または流動層
形成材より粗い粒度(最大5.0mm)のものを用い
る。4は流動層形成材供給槽である。流動床炉3
からの鉄酸ソーダおよびボイラ5、サイクロン
6、電気集じん機7からのダストを一緒に加水分
解装置8に導入して苛性ソーダと回収酸化鉄とに
抽出、分離し、この回収酸化鉄を乾燥分級装置1
0で燃焼排ガスと接触させて粉状酸化鉄と粒状酸
化鉄とに乾燥分級した後、粒状酸化鉄と供給槽4
を介して流動床炉3へ供給し、粉状酸化鉄と濃縮
パルプ廃液(濃黒液)とを混合槽2で混合し、つ
いでこの混合物を乾燥装置11で燃焼排ガスと接
触させて乾燥した後、流動床炉3に投入する。
Embodiments of the present invention will be described in detail below with reference to the drawings. FIG. 1 shows an example of an apparatus for carrying out the method of the invention. The dilute black liquor is introduced into an evaporator 1 such as a vacuum evaporator or a rotary disk type evaporator, and is evaporated and concentrated to obtain a 60 to 80% concentrated black liquor.Then, the concentrated black liquor is sent to a mixing tank 2. Meanwhile, granular iron oxide is supplied to the fluidized bed furnace 3. The bed temperature of fluidized bed furnace 3 is 700~
1100℃, preferably 900~1000℃, Fe/Na
should be greater than or equal to 1.0. Examples of fluidized bed forming materials include pure iron, iron ore (Fe 2 O 3 , Fe 3 O 4 ), sintered ore,
Granular iron-based compounds such as reduced pellets and granulated steel dust, SiO 2 , AI 2 O 3 , Cr 2 O 3 ,
Particulate compounds such as MgO and CaO are used.
In this example, iron ore is used as iron oxide,
Replenishment is done with granular iron ore. The supplementary granular iron ore used has the same particle size as the fluidized bed forming material (0.2 to 3.0 mm) or coarser than the fluidized bed forming material (maximum 5.0 mm). 4 is a fluidized bed forming material supply tank. Fluidized bed furnace 3
The ferric acid soda from the boiler 5, the cyclone 6, and the dust from the electrostatic precipitator 7 are introduced together into the hydrolysis device 8, where they are extracted and separated into caustic soda and recovered iron oxide, and the recovered iron oxide is dried and classified. Device 1
After dry classification into powdered iron oxide and granular iron oxide by contacting with combustion exhaust gas at 0, granular iron oxide and supply tank 4
The powdered iron oxide and the concentrated pulp waste liquid (concentrated black liquor) are mixed in the mixing tank 2, and then this mixture is brought into contact with combustion exhaust gas in the drying device 11 to dry it. , and put it into the fluidized bed furnace 3.
なお酸化鉄の供給は、粒状、粉状とも黒液と予
混合して行う場合もある。また酸化鉄と黒液との
混合は、単に不定形状に混合するか、または造粒
してもよい。この場合、造粒剤は黒液が使用で
き、新たなバインダーはとくに不要である。すな
わち、混合槽2内で混合することにより、黒液量
が多い場合は粉状酸化鉄が凝集して不定形状の集
合物となり、黒液量が少ない場合は黒液がバイン
ダーとなつて造粒物が生じる。この場合は混合槽
2は造粒槽の機能を兼ねることになる。第1図で
は黒液は全量酸化鉄と混合する場合を示している
が、黒液を単独供給分と予混合分とに分別して供
給することも可能である。 Note that iron oxide may be supplied in either granular or powdered form by premixing it with black liquor. Further, the iron oxide and black liquor may be simply mixed into an irregular shape or may be granulated. In this case, black liquor can be used as the granulating agent, and no new binder is particularly required. That is, by mixing in the mixing tank 2, when the amount of black liquor is large, the powdered iron oxide aggregates and becomes an irregularly shaped aggregate, and when the amount of black liquor is small, the black liquor becomes a binder and is granulated. Things arise. In this case, the mixing tank 2 also functions as a granulation tank. Although FIG. 1 shows a case in which the entire amount of black liquor is mixed with iron oxide, it is also possible to separate and supply the black liquor into an individual supply and a premixed supply.
第2図は加水分解装置を2基設ける場合を示し
ている。すなわち、流動床炉3からの粒状鉄酸ソ
ーダを第1加水分解装置8aに導入して苛性ソー
ダと回収粒状酸化鉄とに抽出、分離し、この回収
粒状酸化鉄を乾燥装置10aで燃焼排ガスと接触
させて乾燥した後、流動層形成材供給槽4を介し
て流動床炉3へ供給し、ボイラ5、サイクロン
6、電気集じん機7からのダストを第2加水分解
装置8bに導入して苛性ソーダと回収粉状酸化鉄
とに抽出、分離し、この回収粉状酸化鉄を乾燥装
置10bで燃焼排ガスと接触させて乾燥した後、
混合槽2へ送つて濃縮パルプ廃液(濃黒液)と混
合し、ついでこの混合物を乾燥した後、流動床炉
3へ投入するようにしたものである。ここで粒状
酸化鉄の粒度は前述のように、0.2〜5mm程度の
ものとし、粉状酸化鉄の粒度は炉内でキヤリーオ
ーバーされる程度の粒度である0.2mm以下のもの
とする。他の構成は第1図の場合と同様である。 FIG. 2 shows a case where two hydrolysis devices are provided. That is, granular sodium ferrate from the fluidized bed furnace 3 is introduced into the first hydrolysis device 8a, extracted and separated into caustic soda and recovered granular iron oxide, and the recovered granular iron oxide is brought into contact with combustion exhaust gas in the drying device 10a. After drying, the fluidized bed forming material is supplied to the fluidized bed furnace 3 via the fluidized bed forming material supply tank 4, and the dust from the boiler 5, cyclone 6, and electrostatic precipitator 7 is introduced into the second hydrolysis device 8b, and caustic soda is After extracting and separating the recovered powdered iron oxide from
It is sent to a mixing tank 2 and mixed with concentrated pulp waste liquid (concentrated black liquor), and then this mixture is dried and then charged into a fluidized bed furnace 3. As mentioned above, the particle size of the granular iron oxide is about 0.2 to 5 mm, and the particle size of the powdered iron oxide is 0.2 mm or less, which is a particle size that can be carried over in the furnace. The other configurations are the same as in the case of FIG.
第3図はフラツシユドライヤなどの乾燥器(以
下、フラツシユドライヤという)、1基の加水分
解装置を設ける場合を示している。すなわち、ボ
イラ5からの排ガスを第1サイクロン6aで集じ
んした後、排ガスの一部又は全部をフラツシユド
ライヤ12に導入してスラリーポンプ13により
送られてきた濃黒液と粉状酸化鉄との混合物を噴
霧乾燥造粒し、この造粒物を流動床炉3に投入す
るとともに、フラツシユドライヤ12の排ガスを
第2サイクロン6b、電気集じん機7に通して集
じんし、流動床炉3からの鉄酸ソーダ、ボイラ
5、第1サイクロン6aからのダストを加水分解
装置8に導入して苛性ソーダと回収酸化鉄とに抽
出、分離し、この回収酸化鉄を乾燥分級装置14
で燃焼排ガスと接触させて乾燥するとともに、粒
状酸化鉄と粉状酸化鉄とに分級した後、粒状酸化
鉄を流動層形成材供給槽4を介して流動床炉3へ
供給し、紛状酸化鉄および第2サイクロン6b、
電気集じん機7からのダストと濃黒液とを混合槽
2で混合し、ついでこの混合物をフラツシユドラ
イヤ12へ供給するようにしたものである。第3
図における蒸発器1aは真空蒸発器からなり、希
黒液を60〜65%の濃黒液に蒸発、濃縮する。他の
構成は第1図の場合と同様である。 FIG. 3 shows a case where a dryer such as a flash dryer (hereinafter referred to as a flash dryer) and one hydrolysis device are provided. That is, after the exhaust gas from the boiler 5 is collected by the first cyclone 6a, part or all of the exhaust gas is introduced into the flash dryer 12, where it is mixed with the concentrated black liquor and powdered iron oxide sent by the slurry pump 13. The mixture is spray-dried and granulated, and this granulated material is charged into the fluidized bed furnace 3, and the exhaust gas from the flash dryer 12 is passed through the second cyclone 6b and the electrostatic precipitator 7 to collect dust. The ferric acid soda from 3, the boiler 5, and the dust from the first cyclone 6a are introduced into the hydrolysis device 8, where they are extracted and separated into caustic soda and recovered iron oxide, and the recovered iron oxide is passed through the dry classification device 14.
After drying it by contacting it with combustion exhaust gas and classifying it into granular iron oxide and powdered iron oxide, the granular iron oxide is supplied to the fluidized bed furnace 3 via the fluidized bed forming material supply tank 4, and the powdered iron oxide is iron and second cyclone 6b,
Dust from an electrostatic precipitator 7 and concentrated black liquor are mixed in a mixing tank 2, and then this mixture is supplied to a flash dryer 12. Third
The evaporator 1a in the figure is a vacuum evaporator, which evaporates and concentrates the dilute black liquor to a 60-65% concentrated black liquor. The other configurations are the same as in the case of FIG.
第4図はフラツシユドライヤなどの乾燥器、2
基の加水分解装置を設ける場合を示している。す
なわち、流動床炉3からの鉄酸ソーダを第1加水
分解装置8aに導入して苛性ソーダと回収粉状酸
化鉄とに抽出、分離し、この回収粒状酸化鉄を乾
燥装置10aで燃焼排ガスと接触させて乾燥した
後、供給槽4を介して流動床炉3へ供給し、ボイ
ラ5、第1サイクロン6aからのダストを第2加
水分解装置8bに導入して苛性ソーダと回収粉状
酸化鉄とに抽出、分離し、この回収粉状酸化鉄を
乾燥装置10bで燃焼排ガスと接触させて乾燥し
た後、この回収粉状酸化鉄および第2サイクロン
6b、電気集じん機7からのダストと黒液とを混
合槽2で混合し、ついでこの混合物をフラツシユ
ドライヤ12へ供給するものである。他の構成は
第3図の場合と同様である。 Figure 4 shows a dryer such as a flash dryer, 2
This figure shows the case where a hydrolysis device is provided. That is, the ferric acid soda from the fluidized bed furnace 3 is introduced into the first hydrolysis device 8a, where it is extracted and separated into caustic soda and recovered powdered iron oxide, and the recovered granular iron oxide is brought into contact with combustion exhaust gas in the drying device 10a. After drying, the dust is supplied to the fluidized bed furnace 3 via the supply tank 4, and the dust from the boiler 5 and the first cyclone 6a is introduced into the second hydrolysis device 8b, where it is converted into caustic soda and recovered powdered iron oxide. After extraction and separation, the recovered powdered iron oxide is dried by contacting with combustion exhaust gas in the drying device 10b, and then the recovered powdered iron oxide, the dust from the second cyclone 6b, the electrostatic precipitator 7, and the black liquor are combined. are mixed in a mixing tank 2, and then this mixture is supplied to a flash dryer 12. The other configurations are the same as in the case of FIG.
本発明は上記のように構成されているので、つ
ぎのような効果を奏する。
Since the present invention is configured as described above, it has the following effects.
(1) 酸化鉄(鉄鉱石)の苛性化剤として用い、回
収した粒状酸化鉄をそのまま流動床炉へ循環
し、ボイラ、サイクロン、電気集じん機から回
収した粉状酸化鉄を黒液と予混合して循環使用
するものであるから、反応表面積が大きくなつ
て黒液と酸化鉄との反応率が向上するととも
に、酸化鉄の補給量が少なくなり、経済性が高
くなる。(1) Used as a causticizing agent for iron oxide (iron ore), the recovered granular iron oxide is circulated as it is to the fluidized bed furnace, and the powdered iron oxide recovered from the boiler, cyclone, and electrostatic precipitator is mixed with black liquor. Since it is mixed and used in circulation, the reaction surface area is increased and the reaction rate between black liquor and iron oxide is improved, and the amount of iron oxide to be replenished is reduced, making it more economical.
(2) 流動床からキヤリーオーバーするNa分は、
操作条件にもよるが3〜4割になる。このNa
分をほぼ100%回収することができる。なお、
Na分をほぼ100%流動床のオーバーフローとし
て粒状物で回収しようとすれば、流動床におけ
る鉄鉱石の滞留時間を短くし、粉化を少なくす
ることが必要であり、鉄鉱石循環量の増大につ
ながり、ランニングコストが増加する。(2) The Na content carried over from the fluidized bed is
It depends on the operating conditions, but it is 30-40%. This Na
Almost 100% of the amount can be recovered. In addition,
In order to recover nearly 100% of the Na content as granular material as overflow from the fluidized bed, it is necessary to shorten the residence time of iron ore in the fluidized bed and reduce pulverization. connection, increasing running costs.
図面は本発明のパルプ廃液から苛性ソーダを回
収する方法を実施する装置を示すもので、第1図
は加水分解装置を1基設ける場合のフローシー
ト、第2図は加水分解装置を2基設ける場合のフ
ローシート、第3図はフラツシユドライヤ、1基
の加水分解装置を設ける場合のフローシート、第
4図はフラツシユドライヤ、2基の加水分解装置
を設ける場合のフローシートである。
1,1a……蒸発器、2……混合槽、3……流
動床炉、4……流動層形成材供給槽、5……ボイ
ラ、6,6a,6b……サイクロン、7……電気
集じん機、8,8a,8b……加水分解装置、1
0……乾燥分級装置、10a,10b,11……
乾燥装置、12……乾燥器(フラツシユドライ
ヤ)、13……スラリーポンプ、14……乾燥分
級装置。
The drawings show an apparatus for carrying out the method of recovering caustic soda from pulp waste liquid according to the present invention. Figure 1 is a flow sheet when one hydrolysis apparatus is installed, and Figure 2 is a flow sheet when two hydrolysis apparatuses are installed. 3 is a flow sheet when a flash dryer and one hydrolysis device are installed, and FIG. 4 is a flow sheet when a flash dryer and two hydrolysis devices are installed. 1, 1a... Evaporator, 2... Mixing tank, 3... Fluidized bed furnace, 4... Fluidized bed forming material supply tank, 5... Boiler, 6, 6a, 6b... Cyclone, 7... Electric collector Dust machine, 8, 8a, 8b...Hydrolysis device, 1
0... Dry classification device, 10a, 10b, 11...
Drying device, 12... Dryer (flash dryer), 13... Slurry pump, 14... Drying classification device.
Claims (1)
として加えて流動床炉3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
を回収し、流動床炉排ガスをボイラ5で熱回収
し、サイクロン6、電気集じん機7などの集じん
装置に通して集じんする方法において、 流動床炉3に粒状の新酸化鉄を供給し、流動床
炉3からの鉄酸ソーダおよびボイラ5、サイクロ
ン6、電気集じん機7からのダストを加水分解装
置8に導入して苛性ソーダと回収酸化鉄とに分離
した後、この回収酸化鉄を粉状酸化鉄と粒状酸化
鉄とに分級し、粒状酸化鉄を流動床炉3へ供給
し、粉状酸化鉄と濃縮パルプ廃液とを混合し、つ
いでこの混合物を流動床炉3に投入することを特
徴とするパルプ廃液から苛性ソーダを回収する方
法。 2 パルプ廃液を濃縮した後、酸化鉄を苛性化剤
として加えて流動床炉3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
を回収し、流動床炉排ガスをボイラ5で熱回収
し、サイクロン6、電気集じん機7などの集じん
装置に通して集じんする方法において、 流動床炉3に粒状の新酸化鉄を供給し、流動床
炉3からの粒状鉄酸ソーダを第1加水分解装置8
aに導入して苛性ソーダと回収粒状酸化鉄とに分
離し、この回収粒状酸化鉄を流動床炉3へ供給
し、ボイラ5、サイクロン6、電気集じん機7か
らのダストを第2加水分解装置8bに導入して苛
性ソーダと回収粉状酸化鉄とに分離し、この回収
粉状酸化鉄と濃縮パルプ廃液とを混合し、ついで
この混合物を流動床炉3に投入することを特徴と
するパルプ廃液から苛性ソーダを回収する方法。 3 パルプ廃液を濃縮した後、酸化鉄を苛性化剤
として加えて流動床炉3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
を回収し、流動床炉排ガスをボイラ5で熱回収
し、サイクロン6a,6b、電気集じん機7など
の集じん装置に通して集じんする方法において、 流動床炉3に粒状の新酸化鉄を供給し、ボイラ
排ガスを第1サイクロン6aで集じんした後、排
ガスの少なくとも一部を乾燥器12に導入して濃
縮パルプ廃液と粉状酸化鉄との混合物を予熱乾燥
し、この乾燥物を流動床炉3に投入するととも
に、乾燥器12の排ガスを第2サイクロン6b、
電気集じん機7に通して集じんし、流動床炉3か
らの鉄酸ソーダ、ボイラ5、第1サイクロン6a
からのダストを加水分解装置8に導入して苛性ソ
ーダと回収酸化鉄とに分離し、この回収酸化鉄を
粒状酸化鉄と粉状酸化鉄とに分級した後、粒状酸
化鉄を流動床炉3へ供給し、粉状酸化鉄および第
2サイクロン6b、電気集じん機7からのダスト
と濃縮パルプ廃液とを混合し、ついでこの混合物
を前記乾燥器12へ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。 4 パルプ廃液を濃縮した後、酸化鉄を苛性化剤
として加えて流動床炉3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
を回収し、流動床炉排ガスをボイラ5で熱回収
し、サイクロン6a,6b、電気集じん機7など
の集じん装置に通して集じんする方法において、 流動床炉3に粒状の新酸化鉄を供給し、ボイラ
排ガスを第1サイクロン6aで集じんした後、排
ガスの少なくとも一部を乾燥器12に導入して濃
縮パルプ廃液と粉状酸化鉄との混合物を予熱乾燥
し、この乾燥物を流動床炉3に投入するととも
に、乾燥器12の排ガスを第2サイクロン6b、
電気集じん機7に通して集じんし、流動床炉3か
らの鉄酸ソーダを第1加水分解装置8aに導入し
て苛性ソーダと回収粒状酸化鉄とに分離し、この
回収粒状酸化鉄を流動床炉3へ供給し、ボイラ
5、第1サイクロン6aからのダストを第2加水
分解装置8bに導入して苛性ソーダと回収粉状酸
化鉄とに分離し、この回収粉状酸化鉄および第2
サイクロン6b、電気集じん機7からのダストと
濃縮パルプ廃液とを混合し、ついでこの混合物を
前記乾燥器12へ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, iron oxide is added as a causticizing agent and burned in a fluidized bed furnace 3, and the product is then poured into water to recover caustic soda and the causticizing agent. In a method in which heat is recovered from bed furnace exhaust gas in a boiler 5 and dust is collected through a dust collector such as a cyclone 6 or an electrostatic precipitator 7, granular new iron oxide is supplied to a fluidized bed furnace 3. Ferric acid soda from 3 and dust from boiler 5, cyclone 6, and electrostatic precipitator 7 are introduced into hydrolysis device 8 and separated into caustic soda and recovered iron oxide, and then the recovered iron oxide is converted into powdered iron oxide. and granular iron oxide, the granular iron oxide is supplied to a fluidized bed furnace 3, the powdered iron oxide and concentrated pulp waste liquid are mixed, and this mixture is then charged into the fluidized bed furnace 3. A method for recovering caustic soda from pulp waste liquid. 2 After concentrating the pulp waste liquid, add iron oxide as a causticizing agent and combust it in a fluidized bed furnace 3. Then, the product is poured into water to recover caustic soda and the causticizing agent, and the fluidized bed furnace exhaust gas is sent to a boiler 5. In this method, granular new iron oxide is supplied to the fluidized bed furnace 3, and the granular iron oxide from the fluidized bed furnace 3 is Soda is transferred to the first hydrolysis device 8
a, the recovered granular iron oxide is separated into caustic soda and recovered granular iron oxide, and the recovered granular iron oxide is supplied to the fluidized bed furnace 3, and the dust from the boiler 5, cyclone 6, and electrostatic precipitator 7 is transferred to the second hydrolysis device. 8b to separate caustic soda and recovered powdered iron oxide, the recovered powdered iron oxide and concentrated pulp waste liquid are mixed, and then this mixture is introduced into a fluidized bed furnace 3. How to recover caustic soda from. 3 After concentrating the pulp waste liquid, add iron oxide as a causticizing agent and combust it in a fluidized bed furnace 3. Then, the product is poured into water to recover caustic soda and the causticizing agent, and the fluidized bed furnace exhaust gas is sent to a boiler 5. In this method, granular new iron oxide is supplied to the fluidized bed furnace 3, and the boiler exhaust gas is passed through the first cyclone 6a to recover heat and collect dust through a dust collector such as cyclones 6a and 6b and an electrostatic precipitator 7. After collecting dust in the fluidized bed furnace 3, at least a part of the exhaust gas is introduced into the dryer 12 to preheat and dry the mixture of concentrated pulp waste liquid and powdered iron oxide, and this dried product is fed into the fluidized bed furnace 3, and 12 exhaust gas to the second cyclone 6b,
The dust is collected through an electrostatic precipitator 7, and the ferric acid soda from the fluidized bed furnace 3, the boiler 5, and the first cyclone 6a are collected.
The dust is introduced into a hydrolysis device 8 to be separated into caustic soda and recovered iron oxide, and the recovered iron oxide is classified into granular iron oxide and powdered iron oxide, and then the granular iron oxide is transferred to a fluidized bed furnace 3. caustic soda from the pulp waste liquid, which is characterized in that the powdered iron oxide and the dust from the second cyclone 6b and the electrostatic precipitator 7 are mixed with the concentrated pulp waste liquid, and then this mixture is fed to the dryer 12. How to recover. 4 After concentrating the pulp waste liquid, add iron oxide as a causticizing agent and combust it in a fluidized bed furnace 3. Then, the product is poured into water to recover caustic soda and the causticizing agent, and the fluidized bed furnace exhaust gas is sent to a boiler 5. In this method, granular new iron oxide is supplied to the fluidized bed furnace 3, and the boiler exhaust gas is passed through the first cyclone 6a to recover heat and collect dust through a dust collector such as cyclones 6a and 6b and an electrostatic precipitator 7. After collecting dust in the fluidized bed furnace 3, at least a part of the exhaust gas is introduced into the dryer 12 to preheat and dry the mixture of concentrated pulp waste liquid and powdered iron oxide, and this dried product is fed into the fluidized bed furnace 3, and 12 exhaust gas to the second cyclone 6b,
Dust is collected through the electrostatic precipitator 7, and the ferric acid soda from the fluidized bed furnace 3 is introduced into the first hydrolysis device 8a to separate it into caustic soda and recovered granular iron oxide. The dust from the boiler 5 and the first cyclone 6a is introduced into the second hydrolysis device 8b and separated into caustic soda and recovered powdered iron oxide.
A method for recovering caustic soda from pulp waste liquid, characterized in that the dust from the cyclone 6b and the electrostatic precipitator 7 and the concentrated pulp waste liquid are mixed, and then this mixture is supplied to the dryer 12.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP16792783A JPS6059190A (en) | 1983-09-12 | 1983-09-12 | Recovery of caustic soda from pulp waste liquid |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP16792783A JPS6059190A (en) | 1983-09-12 | 1983-09-12 | Recovery of caustic soda from pulp waste liquid |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6059190A JPS6059190A (en) | 1985-04-05 |
| JPH0411673B2 true JPH0411673B2 (en) | 1992-03-02 |
Family
ID=15858634
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP16792783A Granted JPS6059190A (en) | 1983-09-12 | 1983-09-12 | Recovery of caustic soda from pulp waste liquid |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6059190A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4998580A (en) * | 1985-10-02 | 1991-03-12 | Modine Manufacturing Company | Condenser with small hydraulic diameter flow path |
| JPS62268882A (en) * | 1986-05-16 | 1987-11-21 | 川崎重工業株式会社 | Treatment of iron acid soda |
Family Cites Families (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS58132192A (en) * | 1982-01-27 | 1983-08-06 | バブコツク日立株式会社 | Direct caustification using fluidized layer furnace |
| JPS58132191A (en) * | 1982-01-27 | 1983-08-06 | バブコツク日立株式会社 | Direct caustification method and apparatus in pulping process |
| US4441959A (en) * | 1982-07-21 | 1984-04-10 | International Paper Company | Recovery of heat and chemical values from spent pulping liquors |
| JPS59162129A (en) * | 1983-02-28 | 1984-09-13 | Kawasaki Heavy Ind Ltd | Recovery of sodium hydroxide from pulp waste |
| JPS59162128A (en) * | 1983-02-28 | 1984-09-13 | Kawasaki Heavy Ind Ltd | Recovery of sodium hydroxide from pulp waste |
-
1983
- 1983-09-12 JP JP16792783A patent/JPS6059190A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6059190A (en) | 1985-04-05 |
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