JPH05171582A - Regeneration of waste paper - Google Patents

Regeneration of waste paper

Info

Publication number
JPH05171582A
JPH05171582A JP33846591A JP33846591A JPH05171582A JP H05171582 A JPH05171582 A JP H05171582A JP 33846591 A JP33846591 A JP 33846591A JP 33846591 A JP33846591 A JP 33846591A JP H05171582 A JPH05171582 A JP H05171582A
Authority
JP
Japan
Prior art keywords
seawater
paper
aqueous solution
precipitate
water
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.)
Withdrawn
Application number
JP33846591A
Other languages
Japanese (ja)
Inventor
Jun Nasu
那須醇
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP33846591A priority Critical patent/JPH05171582A/en
Publication of JPH05171582A publication Critical patent/JPH05171582A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/64Paper recycling

Abstract

PURPOSE:To recover high-quality fibers from waste paper without degrading the fiber. CONSTITUTION:The pH of seawater is lowered with a specific acid and then increased with an alkaline agent and the formed precipitate (a) is removed. The treated seawater is concentrated and cooled and the formed precipitate is removed to obtain an aqueous solution (b) having high pH. Finely cut paper is put into the aqueous solution (b) having high pH to effect the defibration of the paper. The product is deinked by conventional method to obtain a pulp raw material. The process can be performed without using heating process and the amount of water can be reduced to suppress the environmental pollution caused by waste liquid. A high-quality fiber is produced because there is no destruction of the fiber in itself.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】この発明は新聞紙、ダンボール、
OA紙、牛乳パック等の古紙を再生する方法に関する。
BACKGROUND OF THE INVENTION This invention relates to newspaper, cardboard,
The present invention relates to a method of recycling used paper such as OA paper and milk carton.

【0002】[0002]

【従来の技術】近年OA機器から出される不要紙が増大
しており、一方パルプの原料となる木材の国内供給量の
絶対的不足から、古紙の再利用が重要性を増している。
従来より、古紙の再生はまず古紙をパルパー、蒸解が
ま、ニーダー等により解繊するとともに混入しているポ
リエステル、粘着テープその他の異物を除去し、さらに
紙繊維から水中に分散してインクをフローテーション法
或いは洗浄法等により脱墨し、パルプ原料としている。
2. Description of the Related Art In recent years, the amount of waste paper discharged from OA equipment has increased, and on the other hand, the reusability of waste paper has become more important due to the absolute shortage of domestic supply of wood, which is a raw material for pulp.
Conventionally, the used paper is recycled by first disintegrating the used paper with a pulper, a digester, a kneader, etc., and removing the mixed polyester, adhesive tape and other foreign substances, and further dispersing it from the paper fiber in water to remove the ink. It is deinked by rotation method or washing method and used as pulp material.

【0003】このような古紙再生工程においては、古紙
の解繊及び脱墨をするために水酸化ナトリウム水溶液と
界面活性剤を用いて、加熱しながら解繊と脱墨を行なっ
ている。
In such a used paper recycling process, an aqueous sodium hydroxide solution and a surfactant are used to defibrate and deink the used paper while heating and defibrating and deinking.

【0004】[0004]

【発明が解決しようとする問題点】しかし、このような
従来の方法では高濃度の水酸化ナトリウム水溶液を用い
ているため、また加熱工程を経るため、紙の繊維がいた
みやすく、再生される紙の品質は低下せざるを得なかっ
た。また、水酸化ナトリウム水溶液を洗い流すため多量
の水を必要とし、しかも再生工程において排出される廃
液は環境汚染の一因となっている。
However, since such a conventional method uses a high-concentration aqueous sodium hydroxide solution and undergoes a heating step, the fibers of the paper are easily damaged and the recycled paper is used. The quality of I was forced to decline. Further, a large amount of water is required to wash away the sodium hydroxide aqueous solution, and the waste liquid discharged in the regeneration process is one of the causes of environmental pollution.

【0005】本発明はこのような従来の古紙再生方法の
難点を解消し、高品質の再生紙を得ることができる古紙
再生方法を提供することを目的とする。また本発明は加
熱工程を不要とし、比較的少量の水で水洗を行なうこと
ができる古紙再生方法を提供することを目的とする。更
に本発明は再生工程における廃液のリサイクルが可能で
環境汚染の問題のない古紙再生方法を提供することを目
的とする。
An object of the present invention is to provide a used paper recycling method which solves the above problems of the used paper recycling method and can obtain recycled paper of high quality. Another object of the present invention is to provide a used paper recycling method that does not require a heating step and can be washed with a relatively small amount of water. Another object of the present invention is to provide a method for recycling used paper that allows recycling of waste liquid in the recycling process and does not pose a problem of environmental pollution.

【0006】[0006]

【問題点を解決するための手段】このような目的を達成
するため、本発明の古紙再生方法は海水を硫酸イオンを
含有する強酸により低pHに調整した後、強アルカリ剤
を加え高pHにし、その際生じる第1の沈殿を除いた後
の海水を更に濃縮し、冷却することにより生じる第2の
沈殿を除いた残液から得られた塩を含む、高pHの水溶
液に古紙を溶かした後、脱色し、パルプ原料を取り出す
ものであり、好適には高pHの水溶液はさらに上記海水
から得られた第1の沈殿と希石灰との混合物を含むもの
である。
In order to achieve such an object, in the method for recycling used paper of the present invention, seawater is adjusted to a low pH with a strong acid containing a sulfate ion, and then a strong alkali agent is added to increase the pH. , The seawater after removing the first precipitate formed at that time was further concentrated, and the waste paper was dissolved in a high-pH aqueous solution containing a salt obtained from the residual liquid from which the second precipitate formed by cooling was removed. After that, it is decolorized and the pulp raw material is taken out, and preferably the high pH aqueous solution further contains a mixture of the first precipitate obtained from the seawater and dilute lime.

【0007】ここで海水から得られた塩とは、特開平2
−221107号に開示された「海水の塩分離方法」に
よって得られる塩で、海水を硫酸イオンを含有する強酸
により低pHに調整した後、強アルカリ剤を加え高pH
にし、その際生じる第1の沈殿(a)を除いた後の海水
を更に濃縮し、急冷することにより生じる第2の沈殿を
除去した残液(b)から得られる。この第2の沈殿除去
後の海水は約pH14以上の高いアルカリ性を示し、そ
のまま高pHの水溶液として利用することができる。ま
た、この海水(b)から水分を除去して塩(c)を回収
し、この塩(c)を適宜水に溶解して用いてもよい。高
pHの水溶液のpHは12以上であることが好ましく、
好適には13以上、更に好適には14程度である。
[0007] Here, the salt obtained from seawater refers to JP-A-2
No. 221107, the salt obtained by the “separation method of seawater”, wherein seawater is adjusted to a low pH with a strong acid containing a sulfate ion, and then a strong alkaline agent is added to increase the pH.
The first precipitate (a) formed at that time is removed, and the seawater after the first precipitate (a) is removed is further concentrated, and the second precipitate formed by quenching is removed from the residual liquid (b). The seawater after the removal of the second precipitate exhibits a high alkalinity of about pH 14 or higher, and can be used as it is as a high pH aqueous solution. Alternatively, water may be removed from the seawater (b) to recover the salt (c), and the salt (c) may be appropriately dissolved in water before use. The pH of the high pH aqueous solution is preferably 12 or more,
It is preferably 13 or more, and more preferably about 14.

【0008】更に本発明の古紙再生方法において用いら
れる高pHの水溶液には、海水を酸及びアルカリ処理し
た際に得られる第1の沈殿(a)と希石灰との混合物を
添加してもよい。この混合物を添加することにより、脱
色効果を得ることができる。沈澱物(a)と希石灰との
混合比は適宜選択することができるが、通常3:7〜
7:3、好ましくは4:6〜6:4の範囲である。また
沈殿(a)と希石灰との混合物は、上記の残液である海
水(b)を希釈したものに溶解させるか、或いは海水
(b)から得た塩(c)と共に水に溶解させることがで
きる。
Further, a mixture of the first precipitate (a) obtained when seawater is treated with an acid and alkali and dilute lime may be added to the high pH aqueous solution used in the used paper recycling method of the present invention. .. A decolorizing effect can be obtained by adding this mixture. The mixing ratio of the precipitate (a) and the dilute lime can be appropriately selected, but is usually 3: 7 to.
It is in the range of 7: 3, preferably 4: 6 to 6: 4. In addition, the mixture of the precipitate (a) and dilute lime is dissolved in the diluted residual seawater (b), or dissolved in water together with the salt (c) obtained from the seawater (b). You can

【0009】以下、海水から塩(c)を分離する方法を
簡単に説明する。海水を低pHにするために用いられる
硫酸イオンを含有する強酸としては、数%の希硫酸を用
いることができるが、活性化した燐酸カルシウムを溶解
せしめた水溶液に3〜5%の濃硫酸を加えて沈澱物を除
去した水溶液(以下P−S酸と略す)を用いることがで
きる。希硫酸あるいはP−S酸を海水に対し数%加え、
2〜3時間放置することにより海水をpH2以下の低p
Hに調整することができる。この時、沈澱物は殆ど生じ
ないが若干の沈澱物はもとの海水中の懸濁物質と共に濾
過等の手段により除去する。
The method for separating salt (c) from seawater will be briefly described below. As the strong acid containing a sulfate ion used to bring the seawater to a low pH, dilute sulfuric acid of several% can be used, but 3 to 5% concentrated sulfuric acid is added to an aqueous solution in which activated calcium phosphate is dissolved. In addition, an aqueous solution from which precipitates have been removed (hereinafter abbreviated as P-S acid) can be used. Add a few% of dilute sulfuric acid or P-S acid to seawater,
Leave the seawater at a pH of 2 or lower by leaving it for 2 to 3 hours.
It can be adjusted to H. At this time, almost no precipitate is generated, but some precipitate is removed together with the suspended matter in the original seawater by means such as filtration.

【0010】強アルカリ剤は、高pH下で溶解度の低下
するカルシウム、マグネシウム等のアルカリ土類金属
類、その他金属の硫酸塩等の塩類を沈澱せしめる。この
ような強アルカリ剤としては、水酸化ナトリウム、水酸
化カリウム、酸化カルシウム、あるいはそれらの混合物
などが用いられる。強アルカリ剤の量は高pH、即ちp
H12以上、好ましくはpH13以上にするために、例
えば水酸化ナトリウム(固体)の場合海水に対し3%、
酸化カルシウムの水溶液に水酸化ナトリウムを加えた水
溶液の場合約5%加え、10時間以上放置する。これら
例示された量のアルカリを添加することによって海水は
pH13以上の塩基性を呈し、第1の沈澱物(a)が生
成する。
The strong alkaline agent precipitates alkaline earth metals such as calcium and magnesium whose solubility decreases at high pH and salts such as sulfates of other metals. As such a strong alkaline agent, sodium hydroxide, potassium hydroxide, calcium oxide, or a mixture thereof is used. The amount of strong alkaline agent is high pH, that is, p
H12 or more, preferably pH 13 or more, for example, in the case of sodium hydroxide (solid) 3% to seawater,
In the case of an aqueous solution of sodium hydroxide added to an aqueous solution of calcium oxide, about 5% is added, and the mixture is left for 10 hours or more. By adding the amounts of these exemplified alkalis, the seawater exhibits a basicity of pH 13 or higher, and the first precipitate (a) is formed.

【0011】この沈澱物(a)は希石灰とともに混合し
て、本発明の高pHの水溶液に添加することができる。
添加量は水に対して数%〜50%程度である。沈澱物
(a)と希石灰の混合物(d)を添加することにより、
本発明の高pHの水溶液は脱色作用を呈することができ
る。沈澱物(a)と希石灰との混合比は適宜選択するこ
とができるが、通常3:7〜7:3、好ましくは4:6
〜6:4の範囲である。
The precipitate (a) can be mixed with dilute lime and added to the high pH aqueous solution of the present invention.
The addition amount is about several% to 50% with respect to water. By adding the mixture of precipitate (a) and dilute lime (d),
The high pH aqueous solution of the present invention can exhibit a decolorizing action. The mixing ratio of the precipitate (a) and the dilute lime can be appropriately selected, but is usually 3: 7 to 7: 3, preferably 4: 6.
It is in the range of to 6: 4.

【0012】沈澱物(a)を除去後の残余の海水を更に
容量が10%〜15%くらいになるまで濃縮し、冷却す
る。冷却することにより第2の沈殿が生じる。この沈殿
を除去した後の残液(b)は、pH13以上のアルカリ
性で、本発明の高pHの水溶液としてそのまま用いるこ
とができる。更にこの処理後の海水(b)を必要に応じ
て水で希釈した後、これに上述の沈澱物(a)と希石灰
の混合物(d)を添加してもよい。またこの処理後の海
水(b)から水を除去した塩(c)と沈澱物(a)と希
石灰の混合物(d)を水に溶解させてたものを本発明の
高pHの水溶液とすることも可能である。
The residual seawater after removing the precipitate (a) is further concentrated to a volume of about 10% to 15% and cooled. A second precipitate forms upon cooling. The residual liquid (b) after removing this precipitate is alkaline having a pH of 13 or more and can be used as it is as the high pH aqueous solution of the present invention. Further, the seawater (b) after this treatment may be diluted with water if necessary, and then the mixture (d) of the above-mentioned precipitate (a) and dilute lime may be added thereto. Further, a salt (c) obtained by removing water from the seawater (b) after this treatment, a mixture of the precipitate (a) and dilute lime (d) dissolved in water is used as the high pH aqueous solution of the present invention. It is also possible.

【0013】本発明の高pHの水溶液は上記いずれの場
合にもpH13以上を示し、加熱することなく紙を繊維
に分解するとともに、紙繊維内に浸透して紙からインク
を離脱させて水中に分散させることができる。更に本発
明の高pHの水溶液は、特に海水の酸−アルカリ処理後
の沈殿(a)と希石灰との混合物(d)を添加した場合
には漂白剤等を使用しなくても漂白作用を示す。さらに
漂白作用を高めるためには解繊後、上述のP−S酸を添
加することができる。本発明の高pHの水溶液により解
繊するためには、重量にして数倍の高pH水溶液に古紙
を浸し、0.5〜2時間程度撹拌する。これにより、紙
は殆ど繊維状に分解するとともに、紙繊維中のインクが
水中に分散する。なお、必要に応じ、界面活性剤を適宜
添加してもよい。
The high pH aqueous solution of the present invention shows a pH of 13 or more in any of the above cases, decomposes the paper into fibers without heating, and penetrates into the paper fibers to release the ink from the paper to be submerged in water. It can be dispersed. Furthermore, the high pH aqueous solution of the present invention has a bleaching action without using a bleaching agent, especially when the mixture (d) of the salt (a) after acid-alkali treatment of seawater and dilute lime is added. Show. To further enhance the bleaching action, the above-mentioned P-S acid can be added after defibration. In order to defibrate with the high pH aqueous solution of the present invention, the used paper is immersed in a high pH aqueous solution several times in weight and stirred for about 0.5 to 2 hours. As a result, the paper is decomposed into almost fibrous form, and the ink in the paper fibers is dispersed in water. If necessary, a surfactant may be added appropriately.

【0014】その後はフローテーション法或いは洗浄法
等により脱墨する。好適には、フローテーション法によ
りインクを気泡に付着させて浮上分離した後、水で洗浄
する。本発明の古紙生成方法により得られるパルプ原料
は、通常の用途には漂白の必要がないものであるが、更
に用途によっては過酸化水素、サイドロサルファイト等
の漂白剤で漂白してもよい。
After that, deinking is performed by a flotation method or a cleaning method. Preferably, the ink is adhered to the bubbles by the flotation method to float and separate, and then washed with water. The pulp raw material obtained by the method for producing used paper of the present invention does not need to be bleached for ordinary use, but may be bleached with a bleaching agent such as hydrogen peroxide or side loss sulfite depending on the use.

【0015】なお、解繊に使用された水溶液はリサイク
ルして適宜新しい水溶液を加えて数回使うことができ
る。また、最終的に廃液となってものは、海水を酸ーア
ルカリ処理して生じた沈澱物(a)と希石灰の混合物
(d)を添加することにより、排水基準に適合するきれ
いな排水となり、河川に還元することができる。
The aqueous solution used for defibration can be recycled and a new aqueous solution can be appropriately added and used several times. In addition, what becomes the final waste liquid becomes clean drainage that meets drainage standards by adding a mixture (d) of precipitate (a) and dilute lime produced by treating seawater with acid-alkali, Can be reduced to

【0016】[0016]

【実施例】【Example】

実施例1 海水500lに対し、P−S酸10lを加え、3時間放置
した後、不純物を瀘過により除去した。これにより海水
はpH1.6となった。次いで、低pH化した海水500lに
NaOHを3%加え10時間放置した。この時、生成し
た沈澱物(a)を除去後の海水を更に加熱して容量が1
0%になるまで水分を除去して濃縮し、冷却して沈殿を
生じせしめた。この沈殿を除去して得られた残液(b)
はpH14以上であった。
Example 1 10 liters of P-S acid was added to 500 liters of seawater, left for 3 hours, and then impurities were removed by filtration. This brought the pH of seawater to 1.6. Next, 3% of NaOH was added to 500 liters of seawater having a lowered pH, and the mixture was left for 10 hours. At this time, the seawater after removing the formed precipitate (a) was further heated to a volume of 1
The water was removed to 0% and the mixture was concentrated and cooled to cause precipitation. Residual liquid (b) obtained by removing this precipitate
Was above pH 14.

【0017】この残った海水(b)7lに細かく裁断し
た古新聞紙を500g入れ、約30分撹拌して繊維に分
解した。この繊維の水分を除去した後、P−S酸を加
え、混合撹拌することにより漂白した後、遠心分離器で
水分を除去し、310gのパルプ材料を得た。このパル
プ材料は、繊維が長く高品質紙に適用できるものであっ
た。 実施例2 実施例1で得られた処理後の海水(b)から水分を除去
して、塩(c)を得た。一方、海水処理時に生じた沈殿
(a)と希石灰を重量比4:6で混合撹拌し混合物
(d)を得た。塩(c)及び混合物(d)をそれぞれ水
道水に対し20重量%及び10重量%溶解させた。この
上澄水のpHは13.6であった。
Into the remaining 7 l of seawater (b), 500 g of finely cut old newspaper was put and stirred for about 30 minutes to decompose it into fibers. After removing the water content of this fiber, P-S acid was added and bleached by mixing and stirring, and then the water content was removed by a centrifugal separator to obtain 310 g of pulp material. This pulp material has long fibers and can be applied to high-quality paper. Example 2 Water was removed from the treated seawater (b) obtained in Example 1 to obtain salt (c). On the other hand, the precipitate (a) generated during seawater treatment and dilute lime were mixed and stirred at a weight ratio of 4: 6 to obtain a mixture (d). The salt (c) and the mixture (d) were dissolved in tap water at 20% by weight and 10% by weight, respectively. The pH of this supernatant water was 13.6.

【0018】この上澄水に実施例1と同様に古新聞紙を
入れ、約30分撹拌して繊維に分解した。得られたパル
プ材料は、脱色されて白く、繊維が長く高品質紙に適用
できるものであった。 実施例3 実施例1で得られた酸−アルカリ処理後の海水(b)を
約4倍の水で希釈し、これに沈殿(a)と希石灰の混合
比4:6の混合物(d)を10重量%溶解させた。この
上澄水のpHは13.6であった。
Old supernatant paper was put into this supernatant water in the same manner as in Example 1 and stirred for about 30 minutes to decompose it into fibers. The resulting pulp material was decolorized and white, had long fibers and was applicable to high quality papers. Example 3 The seawater (b) after the acid-alkali treatment obtained in Example 1 was diluted with about 4 times the amount of water, and the mixture (d) in which the mixing ratio of the precipitate (a) and dilute lime was 4: 6. Was dissolved by 10% by weight. The pH of this supernatant water was 13.6.

【0019】この上澄水に実施例1と同様に古新聞紙を
入れ、約30分撹拌して繊維に分解した。得られたパル
プ材料は、繊維が長く高品質紙に適用できるものであっ
た。
In the same manner as in Example 1, old newspaper was placed in this supernatant water and stirred for about 30 minutes to decompose it into fibers. The resulting pulp material had long fibers and was applicable to high quality paper.

【0020】[0020]

【発明の効果】以上の説明から明らかなように、本発明
によれば海水から分離した塩を利用した高pHの水溶液
により紙を分解するようにしたので、水酸化ナトリウム
を用いた場合のように紙の繊維が破壊されることなく高
品質のパルプ材料を得ることができる。また本発明によ
れば加熱工程を不要とするので、比較的簡単な装置で簡
易に再生パルプ原料を製造することができる。更に本発
明によれば、漂白剤等を用いることなく殆ど着色のない
高品質のパルプ原料が得られ、また廃液による環境汚染
の問題がない。
As is apparent from the above description, according to the present invention, the paper is decomposed by the high pH aqueous solution using the salt separated from the seawater, and therefore, the paper is not decomposed as in the case of using sodium hydroxide. High quality pulp material can be obtained without breaking the fibers of the paper. Further, according to the present invention, since the heating step is unnecessary, the regenerated pulp raw material can be easily manufactured with a relatively simple apparatus. Further, according to the present invention, a high-quality pulp raw material with almost no coloring can be obtained without using a bleaching agent, etc., and there is no problem of environmental pollution due to waste liquid.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】海水を硫酸イオンを含有する強酸により低
pHに調整した後、強アルカリ剤を加え高pHにし、そ
の際生じる第1の沈殿を除いた後の海水を更に濃縮し、
冷却することにより生じる第2の沈殿を除いた残液から
得られた塩を含む、高pHの水溶液に古紙を溶かした
後、脱墨し、パルプ原料を取り出すことを特徴とする古
紙再生方法。
1. The seawater is adjusted to a low pH with a strong acid containing a sulfate ion, and then a strong alkaline agent is added to bring it to a high pH, and the seawater after removing the first precipitate generated at that time is further concentrated,
A method for recycling used paper, which comprises dissolving the used paper in an aqueous solution having a high pH and containing a salt obtained from the residual liquid obtained by removing the second precipitate generated by cooling, deinking, and taking out a pulp raw material.
【請求項2】前記高pHの水溶液はさらに前記第1の沈
殿と希石灰との混合物を含むことを特徴とする請求項1
記載の古紙再生方法。
2. The high pH aqueous solution further comprises a mixture of the first precipitate and dilute lime.
How to recycle the described waste paper.
JP33846591A 1991-12-20 1991-12-20 Regeneration of waste paper Withdrawn JPH05171582A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP33846591A JPH05171582A (en) 1991-12-20 1991-12-20 Regeneration of waste paper

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP33846591A JPH05171582A (en) 1991-12-20 1991-12-20 Regeneration of waste paper

Publications (1)

Publication Number Publication Date
JPH05171582A true JPH05171582A (en) 1993-07-09

Family

ID=18318423

Family Applications (1)

Application Number Title Priority Date Filing Date
JP33846591A Withdrawn JPH05171582A (en) 1991-12-20 1991-12-20 Regeneration of waste paper

Country Status (1)

Country Link
JP (1) JPH05171582A (en)

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