JPS6055638B2 - Pulp bleaching method with ozone - Google Patents

Pulp bleaching method with ozone

Info

Publication number
JPS6055638B2
JPS6055638B2 JP12399176A JP12399176A JPS6055638B2 JP S6055638 B2 JPS6055638 B2 JP S6055638B2 JP 12399176 A JP12399176 A JP 12399176A JP 12399176 A JP12399176 A JP 12399176A JP S6055638 B2 JPS6055638 B2 JP S6055638B2
Authority
JP
Japan
Prior art keywords
methanol
bleaching
ozone
cooking
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
Application number
JP12399176A
Other languages
Japanese (ja)
Other versions
JPS5349107A (en
Inventor
洋 上嶋
哲 野島
卓三 橋本
静夫 本多
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.)
Hitachi Zosen Corp
National Institute of Advanced Industrial Science and Technology AIST
Original Assignee
Agency of Industrial Science and Technology
Hitachi Zosen Corp
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 Agency of Industrial Science and Technology, Hitachi Zosen Corp filed Critical Agency of Industrial Science and Technology
Priority to JP12399176A priority Critical patent/JPS6055638B2/en
Publication of JPS5349107A publication Critical patent/JPS5349107A/en
Publication of JPS6055638B2 publication Critical patent/JPS6055638B2/en
Expired legal-status Critical Current

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Description

【発明の詳細な説明】 この発明は、パルプの製造におけるパルプの漂白法に関
し、特に漂白剤としてオゾンを用いる方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for bleaching pulp in pulp production, and in particular to a method using ozone as a bleaching agent.

従来、パルプの漂白は、塩素、次亜塩素酸塩、二酸化塩
素などの塩素系漂白剤を用いて行なわれていた。
Conventionally, pulp has been bleached using chlorine bleaches such as chlorine, hypochlorite, and chlorine dioxide.

しかし、この方法では、腐食性の強い物質である塩素化
リグニン類、遊離塩素などが廃水中に多量に含まれ、か
つ該廃水は固形分濃度が低いうえに水量が著しく多いも
のであるために、該廃水の取扱いが極めて困難であつた
。したがつて、該廃水の汚染問題が生じない程度の高い
精度で、該廃水を処理する方法は、技術的かつ経済的に
未だ確立されていない。
However, with this method, the wastewater contains a large amount of highly corrosive substances such as chlorinated lignin and free chlorine, and the wastewater has a low solid content concentration and an extremely large amount of water. However, it was extremely difficult to handle the wastewater. Therefore, a method for treating the wastewater with a high degree of precision that does not cause the problem of contamination of the wastewater has not yet been established technically and economically.

また塩素系漂白剤を含む廃水を精選、洗浄、蒸解工程に
戻して再使用し、蒸解黒液ととともに蒸解薬品の回収工
程に通して、上記漂白剤を食塩の形態に変えて白液から
分離回収する方法も知られているが、この場合には、精
選、洗浄、蒸解、回収工程の装置の材質が、上記廃水の
腐食性に抗し得るように優れた耐食性を有するものでな
ければならないので、設備費が嵩むうらみがある。そし
て不純物として含まれるカルシウム、マグネシウムから
スケールが生じて、しばしば装置の運転に支障をきたす
欠点もある。他方、オゾンは強力な漂白剤として公知の
物質であるが、パルプの漂白の際には、セルロース鎖を
破壊して重合度を低め、パルプの粘度を低下させる欠点
があつたので、一般に用いられていなかつた。
In addition, the wastewater containing chlorine bleach is recycled by returning it to the cleaning, washing, and cooking processes, and passes it through the cooking chemical recovery process along with the cooking black liquor, converting the bleach into salt form and separating it from the white liquor. Recovery methods are also known, but in this case, the materials used for the equipment used in the screening, washing, cooking, and recovery steps must have excellent corrosion resistance to withstand the corrosive nature of the wastewater. Therefore, there is a concern that equipment costs will increase. Another disadvantage is that scale is formed from calcium and magnesium contained as impurities, often interfering with the operation of the equipment. On the other hand, ozone is a substance known as a powerful bleaching agent, but it is not commonly used when bleaching pulp because it has the disadvantage of destroying cellulose chains, lowering the degree of polymerization, and lowering the viscosity of pulp. I wasn't there.

この発明は、以上のような実情に鑑みてなされたもので
あつて、上記の諸欠点を克服して優れた漂白効果を発揮
し、かつセルロース鎖の破壊によるバルブの粘度低下の
おそれのないバルブ漂白法を提供することを目的とする
ものである。
The present invention has been made in view of the above-mentioned circumstances, and provides a valve that overcomes the above-mentioned drawbacks, exhibits an excellent bleaching effect, and is free from the risk of a decrease in the viscosity of the valve due to destruction of cellulose chains. The purpose is to provide a bleaching method.

該発明者らは、この目的を達成すべく鋭意研究を重ねた
結果、漂白剤としてオゾンを用いるバルブの漂白法にお
いて、セルロース鎖の破壊を抑制するためには回収メタ
ノールの共存下で行うことが効果的であるという知見を
得、該知見に基づいてこの発明を完成するに至つ、た。
As a result of extensive research to achieve this objective, the inventors discovered that in a valve bleaching method that uses ozone as a bleaching agent, it is necessary to carry out the process in the coexistence of recovered methanol in order to suppress the destruction of cellulose chains. We have obtained the knowledge that it is effective, and have completed this invention based on this knowledge.

すなわち、この発明は、晒バルブの製造に際して、漂白
剤としてオゾンを用い、セルロースの破壊を抑制するた
めに蒸解工程で副生した回収メタノールの共存下で未晒
バルブを漂白し、漂白工程から出たメタノール含有排水
を、用水の代りに蒸解、洗浄、精選のうちの少なくとも
1工程に導いて、未晒パル液から分離された汚染物質、
悪臭物質、蒸解・洗浄黒液などをメタノール含有排水に
溶解せしめ、これら溶解物質とメタノールを含む排水か
ら粗メタノールを回収し、回収メタノールを漂白工程に
循環して再使用することからなるオゾンによるバルブ漂
白法を要旨とするものである。以下、この発明を図面に
示す実施例に従つて具体的に説明する。
That is, this invention uses ozone as a bleaching agent when manufacturing bleached bulbs, bleaches unbleached bulbs in the coexistence of recovered methanol, which is a by-product of the cooking process, in order to suppress the destruction of cellulose, and removes the bleached bulbs from the bleaching process. Contaminants separated from the unbleached pulp liquid by introducing the methanol-containing wastewater into at least one of cooking, washing, and screening processes instead of water for use,
An ozone-based valve that dissolves malodorous substances, cooking/washing black liquor, etc. into methanol-containing wastewater, recovers crude methanol from the wastewater containing these dissolved substances and methanol, and circulates the recovered methanol to the bleaching process for reuse. The gist is the bleaching method. Hereinafter, this invention will be specifically explained according to embodiments shown in the drawings.

蒸解工程1において木材チップをNaOHとNa2sを
含む蒸解液で蒸解すると、メタノールが副生する。
In cooking step 1, when wood chips are cooked in a cooking liquor containing NaOH and Na2s, methanol is produced as a by-product.

メタノールを含むリリーフガスまたはブローガスの凝縮
液を、管2によつてメタノール回収工程3に導き、蒸留
によつてメタノールを回収する。得られた回収メタノー
ルを管4によつて漂白工程5に導く。この工程5におい
て、オゾン発生器21からオゾンを供給することにより
、前記蒸解工程1から洗浄工程6および精選工程7を経
て来た未晒バルブを漂白する。漂白工程5を出たメタノ
ール含有排水を管8によつて精選工程7、さらに洗浄工
程6に導き、また管9によつて直接洗.浄工程6にも導
いて、未晒バルブ液と向流接触せしめる。こうして、未
晒バルブ液から分離された有機質および無機質の汚染物
質、H2S,CH3SH,(CH3)2S2のような硫
化物からなる悪臭物質、蒸解・洗浄黒液などを、メタノ
ール含有排水に溶解せしめる。ついで、この溶解物質と
メタノールを含んだ排水の一部を、管10によつて蒸解
工程1に導き、蒸解済みのバルブを稀釈し、再び洗浄工
程6に戻す。他方残部を管11によつてメタノール分離
工程12に導き、メタノールその他の物質を蒸発させ、
さらに凝縮させて、管13によつてメタノール回収工程
3に導く。この工程3において、ストリツピング処理お
よび蒸留によつて汚染物質、悪臭物質を除去し、メタノ
ールを回収する。回収メタノールを、前述のように、管
4によつて漂白工程5に導く。他方、メタノール分離工
程12に残された濃黒液を、管14によつて蒸解薬品回
収工程15に導き、ボイラによつて回収さ”れた緑液を
、管16によつて苛性化工程17に導く。ここで苛性化
された薬品を、管18によつて蒸解工程1に循環して使
用する。漂白工程5から出た漂白バルブを再精選工程1
9に導き、さらにバルブ・マシン20でクラフト●バル
ブを得る。なお、メタノールの循環系においてメタノー
ルの量を調整するために、回収メタノールの一部を、管
22によつて蒸解薬品回収工程15に導き、ボイラの燃
料として使用する場合もある。この発明によるバルブ漂
白法は、メタノールを副生する蒸解工程を含むバルブの
製造法てあれば、実施例のものに限定されることなく行
なわれる。
The methanol-containing relief gas or blow gas condensate is led via pipe 2 to a methanol recovery step 3, where methanol is recovered by distillation. The recovered methanol obtained is led to a bleaching step 5 via a pipe 4. In step 5, ozone is supplied from the ozone generator 21 to bleach the unbleached bulbs that have passed through the cooking step 1, the washing step 6, and the selection step 7. The methanol-containing wastewater discharged from the bleaching step 5 is led through a pipe 8 to a screening step 7 and further to a washing step 6, and is also directly washed through a pipe 9. It is also led to a cleaning step 6 to bring it into countercurrent contact with the unbleached valve fluid. In this way, organic and inorganic pollutants separated from the unbleached valve liquid, malodorous substances consisting of sulfides such as H2S, CH3SH, (CH3)2S2, cooking/washing black liquor, etc. are dissolved in the methanol-containing wastewater. A portion of the waste water containing the dissolved substances and methanol is then led to the cooking step 1 through the pipe 10, dilutes the cooked bulb, and returned to the washing step 6 again. On the other hand, the remainder is led to a methanol separation step 12 through a pipe 11 to evaporate methanol and other substances,
It is further condensed and led to a methanol recovery step 3 via a pipe 13. In this step 3, contaminants and malodorous substances are removed by stripping treatment and distillation, and methanol is recovered. The recovered methanol is led to the bleaching step 5 by pipe 4, as described above. On the other hand, the concentrated black liquor left in the methanol separation step 12 is led to a cooking chemical recovery step 15 through a pipe 14, and the green liquor recovered by the boiler is led through a pipe 16 to a causticizing step 17. The causticized chemicals are then circulated through pipe 18 to the cooking stage 1 for use.The bleaching bulb from the bleaching stage 5 is transferred to the re-selection stage 1.
Lead to 9 and then use Valve Machine 20 to obtain a Craft●Valve. In order to adjust the amount of methanol in the methanol circulation system, a part of the recovered methanol may be led to the cooking chemical recovery step 15 through the pipe 22 and used as fuel for the boiler. The bulb bleaching method according to the present invention is not limited to the embodiments, but may be carried out as long as it includes a cooking process that produces methanol as a by-product.

蒸解工程の例としては、硫酸塩法、亜硫酸塩法、アルカ
リ法、酸素−アルカリ法などが挙げられる。また、この
発明によるバルブ漂白法は、漂白剤としてオゾンととも
に過酸化物、酸素のような非塩素系漂白剤を併用しても
よい。
Examples of the cooking process include a sulfate method, a sulfite method, an alkali method, an oxygen-alkali method, and the like. Further, in the bulb bleaching method according to the present invention, a non-chlorine bleaching agent such as peroxide or oxygen may be used in combination with ozone as a bleaching agent.

回収メタノールは、漂白工程に必要な量が確保されたな
らば、残部を燃料として使用してもよく、また装置の作
動開始用に貯蔵しておいてもよい。
The remainder of the recovered methanol may be used as fuel once the amount necessary for the bleaching process is obtained, or it may be stored for use in starting up the device.

この発明は、以上のとおり構成されているので、冒頭に
述べたような塩素系漂白剤による問題が生じるおそれは
全くない。
Since the present invention is constructed as described above, there is no possibility that the problem caused by chlorine bleach as described at the beginning will occur.

そして、セルロース鎖の破壊を生じることなく、晒バル
ブを効果的に漂白することができる。また、蒸解工程に
おいて副生したメタノールを用いるので、メタノールを
系外から導入する必要がなく、さらに漂白工程から出た
メタノール含有排水を蒸解、洗浄、精選のうちの少なく
とも1工程に導入するので、洗浄等のために系外から供
給する水量を著しく減少させることができる。さらに、
溶解物質とメタノールを含む排水から粗メタノールを回
収し、回収メタノールを漂白工程に循環して再使用する
のて、メタノールを有効に利用できて、生産コストを著
しく低下させることができる。参考例 実験1 白色度28.8%、粘?5.6センチ●ポイズ、カッパ
ー価24.1である未晒NUKP(ダグラスフアー65
%、その他35%)を、予めPH=3の希硫酸水溶液に
1時間浸漬して水洗し、乾燥して試料バルブを調製する
In addition, the bleached bulb can be effectively bleached without destroying the cellulose chains. In addition, since methanol by-produced in the cooking process is used, there is no need to introduce methanol from outside the system, and since the methanol-containing wastewater from the bleaching process is introduced into at least one of the cooking, washing, and screening processes, The amount of water supplied from outside the system for cleaning etc. can be significantly reduced. moreover,
By recovering crude methanol from waste water containing dissolved substances and methanol, and recycling the recovered methanol to the bleaching process for reuse, methanol can be used effectively and production costs can be significantly reduced. Reference Example Experiment 1 Whiteness 28.8%, viscosity? 5.6cm●Poise, unbleached NUKP (Douglas Fur 65) with a kappa value of 24.1
%, other 35%) in advance for 1 hour in a dilute sulfuric acid aqueous solution with a pH of 3, washed with water, and dried to prepare a sample bulb.

この試料バルブを絶乾重量で5yとなるような量だけ取
り、市販のメタノール100m1中に浸漬する。試料を
メタノール液中から取出し試料中の含水量が45%にな
るように水分を調整する。試料の重量の増加量を測定し
てメタノールの含浸量を求める。メタノールを含浸した
バルブをフラスコに入れて、フラスコ内に1容量%のオ
ゾンを含む酸素を通流し、フラスコから出るガスを0.
5Mヨウ化カリウム溶液を入れた捕集ピンに導いてオゾ
ンを吸収させる。漂白済みのバルブを蒸留水350m1
と混合し、ろ過水洗する。実験2 実験1と同じ試料バルブを用い、メタノールを全く用い
ないで、その他の操作を実験1と同様に行なう。
Take an amount of this sample bulb to give an absolute dry weight of 5y and immerse it in 100ml of commercially available methanol. A sample is taken out of the methanol solution and the water content is adjusted so that the water content in the sample is 45%. The amount of methanol impregnated is determined by measuring the amount of increase in the weight of the sample. A valve impregnated with methanol is placed in the flask, oxygen containing 1% by volume of ozone is passed through the flask, and the gas leaving the flask is 0.0% by volume.
The ozone is absorbed by a collection pin containing 5M potassium iodide solution. Pour the bleached valve into 350ml of distilled water.
Mix with water, filter and wash. Experiment 2 Other operations are performed as in Experiment 1, using the same sample valve as in Experiment 1 and without using any methanol.

実験3 実験1と同じ試料バルブを用い、汚染物質実施例のメタ
ノール回収工程から出た回収メタノールを用いて、その
他の操作を実験1と同様に行なつ。
Experiment 3 Other operations were performed in the same manner as in Experiment 1, using the same sample valve as in Experiment 1 and using recovered methanol from the methanol recovery process of the contaminant example.

以下に各実験の結果を示す。The results of each experiment are shown below.

白色度はハンダー比色光度計で測定し、粘度は銅エチレ
ンジアミンピペット法により測定する。
Whiteness is measured with a Hander colorimeter, and viscosity is measured with a copper ethylenediamine pipette method.

オゾン供給量はフラスコ内にオゾン含有酸素を通流する
直前のオゾン濃度と通気速度と漂白時間から算出する。
オゾン消費量はオゾン供給量から0.5Mヨウ化カリウ
ム水溶液に吸収されたオゾン量を差引いて算出する。)
これら実験によつて、回収メタノールは、市販のメタノ
ールと同様に、セルロースの破壊を抑制する作用を有し
ていることがわかる。
The amount of ozone supplied is calculated from the ozone concentration immediately before passing ozone-containing oxygen into the flask, the aeration rate, and the bleaching time.
The amount of ozone consumed is calculated by subtracting the amount of ozone absorbed into the 0.5M potassium iodide aqueous solution from the amount of ozone supplied. )
These experiments show that recovered methanol has the same effect as commercially available methanol in suppressing the destruction of cellulose.

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

図面はこの発明の1実施例を示す工程図である。 1・・・蒸解工程、3・・・メタノール回収工程、5・
・・漂白工程、6・・・洗浄工程、7・・・精選工程、
12・・・メタノール分離工程、15・・・蒸解薬品回
収工程、17・・・苛性化工程、19・・・再精選工程
、20・・・バルブ●マシン、21・・・オゾン発生器
The drawings are process diagrams showing one embodiment of the present invention. 1... Cooking process, 3... Methanol recovery process, 5...
... Bleaching process, 6... Washing process, 7... Selection process,
12... Methanol separation process, 15... Cooking chemical recovery process, 17... Causticizing process, 19... Re-selection process, 20... Valve machine, 21... Ozone generator.

Claims (1)

【特許請求の範囲】[Claims] 1 晒パルプの製造に際して、漂白剤としてオゾンを用
い、セルロースの破壊を抑制するために蒸解工程で副生
した回収メタノールの共存下で未晒パルプを漂白し、漂
白工程から出たメタノール含有排水を、用水の代りに蒸
解、洗浄、精選のうちの少なくとも1工程に導いて、未
晒パルプ液から分離された汚染物質、悪臭物質、蒸解・
洗浄黒液などをメタノール含有排水に溶解せしめ、これ
ら溶解物質をメタノールを含む排水から粗メタノールを
回収し、回収メタノールを漂白工程に循環して再使用す
ることからなるオゾンによるパルプ漂白法。
1. When producing bleached pulp, ozone is used as a bleaching agent, and in order to suppress the destruction of cellulose, unbleached pulp is bleached in the coexistence of recovered methanol, which is a by-product of the cooking process, and methanol-containing wastewater from the bleaching process is treated. , the contaminants, malodorous substances, cooking and
A pulp bleaching method using ozone that consists of dissolving cleaning black liquor etc. in methanol-containing wastewater, recovering crude methanol from these dissolved substances from the methanol-containing wastewater, and recycling the recovered methanol to the bleaching process for reuse.
JP12399176A 1976-10-16 1976-10-16 Pulp bleaching method with ozone Expired JPS6055638B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP12399176A JPS6055638B2 (en) 1976-10-16 1976-10-16 Pulp bleaching method with ozone

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12399176A JPS6055638B2 (en) 1976-10-16 1976-10-16 Pulp bleaching method with ozone

Publications (2)

Publication Number Publication Date
JPS5349107A JPS5349107A (en) 1978-05-04
JPS6055638B2 true JPS6055638B2 (en) 1985-12-05

Family

ID=14874325

Family Applications (1)

Application Number Title Priority Date Filing Date
JP12399176A Expired JPS6055638B2 (en) 1976-10-16 1976-10-16 Pulp bleaching method with ozone

Country Status (1)

Country Link
JP (1) JPS6055638B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0552010A (en) * 1991-08-26 1993-03-02 Houken Watabe Motor driven staircase capable of developing and storing

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4229252A (en) * 1979-01-11 1980-10-21 Weyerhaeuser Company Additives for ozone bleaching
US5354423A (en) * 1993-03-01 1994-10-11 University Of New Brunswick Ozone dioxane bleaching of chemical pulps
EP0723611A1 (en) * 1993-10-15 1996-07-31 Macmillan Bloedel Limited Organic solvent recovery

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
SE365008B (en) * 1971-11-19 1974-03-11 Mo Och Domsjoe Ab
JPS51116207A (en) * 1975-04-07 1976-10-13 Kogyo Gijutsuin Improved process for bleaching pulp with ozone

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0552010A (en) * 1991-08-26 1993-03-02 Houken Watabe Motor driven staircase capable of developing and storing

Also Published As

Publication number Publication date
JPS5349107A (en) 1978-05-04

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