JPH06316888A - Method for improving bonding characteristics of defibrillated waste paper by ozone - Google Patents

Method for improving bonding characteristics of defibrillated waste paper by ozone

Info

Publication number
JPH06316888A
JPH06316888A JP13118193A JP13118193A JPH06316888A JP H06316888 A JPH06316888 A JP H06316888A JP 13118193 A JP13118193 A JP 13118193A JP 13118193 A JP13118193 A JP 13118193A JP H06316888 A JPH06316888 A JP H06316888A
Authority
JP
Japan
Prior art keywords
ozone
lignin
waste paper
fibers
amount
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.)
Granted
Application number
JP13118193A
Other languages
Japanese (ja)
Other versions
JP3212759B2 (en
Inventor
Kazuo Kurihara
和夫 栗原
Takakiyo Wada
高清 和田
Shiyoutarou Takada
渉太郎 高田
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.)
Nishimatsu Construction Co Ltd
Original Assignee
Nishimatsu Construction Co Ltd
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 Nishimatsu Construction Co Ltd filed Critical Nishimatsu Construction Co Ltd
Priority to JP13118193A priority Critical patent/JP3212759B2/en
Publication of JPH06316888A publication Critical patent/JPH06316888A/en
Application granted granted Critical
Publication of JP3212759B2 publication Critical patent/JP3212759B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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 improve the bonding characteristics of waste paper by ozone oxidation of its surface. CONSTITUTION:Lignin-contg. waste paper is put to dry defibrillation and brought into contact with vapor phase ozone at levels of 1-5wt.% of the lignin in said waste paper, thus accomplishing ozone oxidation of the surface of the lignin coexistent with the defibrillated fibers.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、オゾンによる解繊古紙
のボンディング特性改善方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for improving the bonding characteristics of defibrated waste paper by ozone.

【0002】[0002]

【従来の技術】地球環境を守る機運が非常に高まった今
日、貴重な森林資源から作られたセルロース繊維は、パ
ルプ・紙として使用された後、廃棄されて古紙となって
も、さらに回収して可能な限り有効に再利用されなけれ
ばならないのは無論である。
2. Description of the Related Art Today, when the momentum for protecting the global environment has greatly increased, cellulose fibers made from valuable forest resources are used as pulp and paper, and are then recovered even if they are discarded as waste paper. Of course, it must be reused as effectively as possible.

【0003】従来、古紙は回収集荷された後、遠隔地の
紙パルプ工場に運ばれ、パルパーと称する装置で、水を
加えて回転翼で撹拌して繊維を水中に解離し、化学的手
段で脱墨し、浮遊法で繊維を分離し、この繊維はほとん
ど全量を再生紙の原料として利用している。
[0003] Conventionally, waste paper is once collected and transported to a pulp and paper mill in a remote place, and in a device called pulper, water is added and stirred by a rotary blade to dissociate fibers into water, and chemical means is used. Deinking and separating the fibers by the flotation method, almost all of the fibers are used as raw materials for recycled paper.

【0004】[0004]

【発明が解決しようとする課題】しかし、上記従来の古
紙リサイクル法は、繊維を解離する工程で、セルロース
が短くなり、またヘミセルロースやフィブリル構造(繊
維の枝状構造)が消失し、再生後の紙力が低下するとい
う根本的課題を有していた。
However, in the above-mentioned conventional waste paper recycling method, cellulose is shortened and hemicellulose and fibril structure (branch structure of fiber) disappear in the step of dissociating the fiber, and after the regeneration, It had a fundamental problem that paper strength was reduced.

【0005】また、上記従来の古紙リサイクル法は、解
繊のために多量の水を使用することから、水資源の浪
費、排水汚染の課題を合わせ持っている。
Further, since the above-mentioned conventional waste paper recycling method uses a large amount of water for defibration, it has problems of wasting water resources and polluting waste water.

【0006】さらにまた、上記従来の古紙リサイクル法
は、通常古紙が最も多く発生する大都市より遠隔地(主
として、多量の水資源を得られる理由による。)に処理
工場があって、しかも、現実的にはその処理工場が紙パ
ルプ工場に限定されていることから、回収費用・処理費
用等の経費が嵩んで回収リサイクル率はなかなか向上し
得ないという課題を有していた。
Furthermore, the above-mentioned conventional waste paper recycling method has a treatment factory in a remote place (mainly because a large amount of water resources can be obtained) from a large city where waste paper is usually most produced, and in reality, Since the processing factory is limited to a pulp and paper factory, there is a problem that the recovery and recycling rate cannot be improved easily due to the high costs such as recovery costs and processing costs.

【0007】そこで本発明は、上記課題を解決すべくな
されたもので、古紙から回収した繊維は天然木材より生
成した繊維に比べて、絡み合いずらく、接着性が悪い、
すなわちボンディング特性が悪いことに鑑み、これら物
理的性能低下を極力抑えることで、再生紙の原料として
のみでなく、多目的(例えば建築資材等)に利用可能と
し、その結果、回収リサイクル率を向上することで天然
資源の有効活用に貢献できるオゾンによる解繊古紙のボ
ンディング特性改善方法を提供することを目的としたも
のである。
Therefore, the present invention has been made to solve the above problems. Fibers recovered from waste paper are less likely to be entangled with each other and have poorer adhesiveness than fibers produced from natural wood.
In other words, in view of poor bonding characteristics, by suppressing these physical performance deterioration as much as possible, it can be used not only as a raw material for recycled paper but also for multiple purposes (for example, building materials), and as a result, the recovery and recycling rate is improved. Therefore, it is an object of the present invention to provide a method for improving the bonding property of defibrated waste paper by ozone, which can contribute to effective use of natural resources.

【0008】さらに、本発明の他の目的とするところ
は、古紙の主な発生地である都市近郊でも、容易に処理
できるオゾンによる解繊古紙のボンディング特性改善方
法を提供することを目的としたものである。
Still another object of the present invention is to provide a method for improving the bonding property of defibrated waste paper by ozone, which can be easily treated even in the suburbs where the waste paper is mainly generated. It is a thing.

【0009】[0009]

【課題を解決するための手段】上記の目的に沿い、先述
特許請求の範囲を要旨とする本発明の構成は前述課題を
解決するために、リグニンを含有する古紙を乾式解繊
し、重量比で含有リグニン量の1%以上5%を越えざる
範囲で気相のオゾンと接触させ、解繊繊維と共存するリ
グニンの表面をオゾンにより酸化することを特徴とした
技術的手段を講じたものである。
In order to solve the above-mentioned problems, the waste paper containing lignin is dry defibrated, and the weight ratio is set to the above-mentioned object. The technical means is characterized in that the surface of lignin coexisting with the defibrated fiber is oxidized by ozone by contacting with ozone in the gas phase within the range of 1% or more and 5% or more of the contained lignin. is there.

【0010】[0010]

【作用】次に本発明法の作用を説明するが、理解を深め
るため、先にパルプ(本願では、パルプ繊維という。)
の構造を説明しておく。パルプ繊維は木材をリファイナ
ーですり潰し繊維を解離させた機械パルプ繊維と、木材
を蒸解して化学的方法でリグニンを取り除いた化学パル
プ繊維とに大別される。そして、機械パルプ繊維は脱リ
グニン処理をしていないため、「図3」に示すごとく、
セルロース100の外側をヘミセルロース101で覆
い、その外側をリグニン102が覆ってなる。なお、
「図3」は概略図であって、実際にはセルロース100
またはヘミセルロース101が露出している部分があっ
たり、セルロース100は繊維状のものが複数本束とな
り、各繊維状セルロース100やヘミセルロース101
をリグニン102が相互に連結して、該リグニン102
はセルロース100やヘミセルロース101の奥にも入
り込んでいるものである。また、多数本のセルロース1
00やヘミセルロース101の束は表面において複雑に
枝別れしているのが通常である。
Next, the operation of the method of the present invention will be described. For the sake of better understanding, pulp (hereinafter referred to as pulp fiber) is first described.
The structure of is explained. Pulp fibers are roughly classified into mechanical pulp fibers obtained by crushing wood with a refiner to dissociate fibers, and chemical pulp fibers obtained by cooking wood to remove lignin by a chemical method. Since the mechanical pulp fiber is not subjected to delignification treatment, as shown in "Fig. 3",
The outside of cellulose 100 is covered with hemicellulose 101, and the outside is covered with lignin 102. In addition,
"Fig. 3" is a schematic diagram, and actually, cellulose 100
Alternatively, there is a portion where the hemicellulose 101 is exposed, or a plurality of fibrous cellulose 100 is bundled, and each fibrous cellulose 100 or hemicellulose 101
Lignin 102 is linked to each other to form the lignin 102
Is also deep inside the cellulose 100 and the hemicellulose 101. Also, a large number of cellulose 1
A bundle of 00 or hemicellulose 101 is usually branched on the surface in a complicated manner.

【0011】なお、化学パルプ繊維は、図示はしていな
いが、「図3」のリグニン102が極端に少なくなって
いるが、化学パルプ繊維といえどもリグニン102が皆
無ではなく、セルロース100及びヘミセルロース10
1よりなる繊維素を束ねるのはやはりリグニン102
で、一般的には機械パルプ繊維は重量比で約20〜33
%の、化学パルプ繊維では約2〜4%のリグニン102
を含有しているものである。
Although not shown in the chemical pulp fiber, the lignin 102 in FIG. 3 is extremely small, but the chemical pulp fiber is not completely free of the lignin 102, and the cellulose 100 and hemicellulose are not present. 10
It is also lignin 102 that bundles the fibrous material consisting of 1
In general, the mechanical pulp fiber has a weight ratio of about 20 to 33.
%, About 2-4% of chemical pulp fiber lignin 102
Is included.

【0012】そして、紙は新聞雑誌等が上記機械パルプ
繊維で作られ、事務用紙等は化学パルプ繊維で作られる
のが通常であるが、古紙となると両者が混合して回収さ
れることも多いく、含有リグニン量は常に一定量ではな
い。
Usually, newspapers and newspapers are made of the above mechanical pulp fibers, and office papers and the like are made of chemical pulp fibers. However, when used papers are often mixed and collected. The amount of lignin contained is not always constant.

【0013】そこで、本発明は、機械パルプ繊維と化学
パルプ繊維とが混合した古紙を乾式解繊、すなわち古紙
に機械的外力を加えて綿毛繊維状にに解離するので、水
の使用が不要で小型な装置で所望の処理能力の解繊がで
き、排水処理の必要性が無いという利点を有するが、古
紙より機械的にうまく繊維を解離したとしても、水と撹
拌力とで古紙を解離する従来例に比べては、繊維が切断
される蓋然性は大きくなる。しかし、機械的な乾式解繊
は繊維束に枝別れ部を形成する作用を呈し、従来のパル
パーを使用すると枝別れ部は溶けたり折れたりして消失
するのに比べ、本発明法では無論多くは外力によっても
ぎ取られるが、その際に外力が加わることで新たな枝別
れ部が生成され、結果として枝別れ部が低減せず、この
枝別れ部が絡み合って相互に結合し易くなる作用を呈す
るものである。
Therefore, according to the present invention, since the waste paper in which the mechanical pulp fibers and the chemical pulp fibers are mixed is dry defibrated, that is, the waste paper is dissociated into fluff fibers by applying a mechanical external force, it is not necessary to use water. It has the advantage that it can defibrate the desired treatment capacity with a small device and does not require wastewater treatment, but even if the fibers are mechanically dissociated better than used paper, the used paper is dissociated with water and stirring power. The probability that the fibers will be cut is greater than in the conventional example. However, mechanical dry defibration has the action of forming a branching portion in the fiber bundle, and when the conventional pulper is used, the branching portion melts or breaks and disappears. Is stripped off by an external force, but when an external force is applied at that time, a new branching part is generated, and as a result, the branching part is not reduced, and this branching part becomes entangled and becomes easy to connect to each other. It is a thing.

【0014】また、本発明法は解繊繊維と、気相のオゾ
ンとを接触させるので、含有するリグニンをオゾン酸化
リグニンに酸化する作用を呈する。
Further, in the method of the present invention, since the defibrated fiber is brought into contact with ozone in the gas phase, it exhibits an action of oxidizing contained lignin into ozone-oxidized lignin.

【0015】リグニンは分子量が非常に大きい複雑な構
成をしており、化学的に究めて安定した物質であるの
で、分解することも困難で接着性も悪い、そこで、究め
て強い酸化力を有するオゾンで分解できないかと試行し
たところ、リグニンを分解する以前にセルロースおよび
ヘミセルロースを分解するであろうとの推測に反し、オ
ゾンはセルロースを選択的に分解する作用を呈すること
が判明した。
Since lignin has a complicated structure with a very large molecular weight and is a chemically stable substance, it is difficult to decompose and has poor adhesiveness. Therefore, it has a strong oxidizing power. When we tried to decompose ozone, it was found that ozone exhibited a selective decomposition effect on cellulose, contrary to the assumption that cellulose and hemicellulose would be decomposed before the decomposition of lignin.

【0016】もっとも、オゾンがリグニンを分解すると
いっても、200〜300の分子量のリグニンを数個乃
至数十個の分子量の物質に分解するのでは無く、本発明
のオゾン酸化リグニンはその芳香核を解裂する程度にと
どめたもので、前記選択的分解もこの範囲で言えるもの
である。
Although ozone decomposes lignin, it does not decompose lignin having a molecular weight of 200 to 300 into a substance having a molecular weight of several to several tens, and the ozone-oxidized lignin of the present invention has its aromatic nucleus. The above-mentioned selective decomposition can be said within this range.

【0017】そして、元来、グニンンは物理的には表面
が平面的で、化学的には反応性が究めて小さいが、芳香
核が解裂されたオゾン酸化リグニンは表面が凹凸面的
で、化学的には反応性が大きくなる作用を、すなわち、
ボンディング特性を増す作用を呈するものである。
Originally, the surface of gnunn is physically flat and the reactivity is chemically small, but the ozone-oxidized lignin from which aromatic nuclei are cleaved has a rough surface. The effect of increasing the reactivity chemically, that is,
It has the effect of increasing the bonding characteristics.

【0018】なお、オゾンはリグニンを選択的に酸化す
るとしたが、セルロースおよびヘミセルロースを全く酸
化しないわけではなく、オゾン量が多かったり、オゾン
との接触時間が長いと、リグニンよりもセルロースおよ
びヘミセルロースが酸化され易い。そして、これらがオ
ゾン酸化されると、せっかくのパルプ繊維が破損を受け
てしまうことになる。そこで、本発明では重量比で含有
リグニン量の1%以上5%を越えざる範囲のオゾンに限
定することで、オゾンがリグニンを選択酸化することで
消費され、セルロースおよびヘミセルロースへのオゾン
の影響を最小にとどめる作用を呈するものである。
Although ozone is said to selectively oxidize lignin, it does not oxidize cellulose and hemicellulose at all, and when the amount of ozone is large and the contact time with ozone is long, cellulose and hemicellulose are more likely than lignin. It is easily oxidized. If these are ozone-oxidized, the pulp fibers will be damaged. Therefore, in the present invention, by limiting the ozone to the range of not less than 1% and not more than 5% of the amount of lignin contained by weight, ozone is consumed by selectively oxidizing lignin, and the influence of ozone on cellulose and hemicellulose is reduced. It has the effect of minimizing it.

【0019】[0019]

【実施例】次に、本発明の実施例を添附図面に従って説
明すれば以下の通りである。本発明法は、まず、リグニ
ンを含有する古紙を乾式解繊する。
Embodiments of the present invention will be described below with reference to the accompanying drawings. In the method of the present invention, first, waste paper containing lignin is dry defibrated.

【0020】古紙を乾式で解繊するには、「図2」に最
も明らかに示すごとき解繊機2が使用できる。すなわ
ち、21が解繊機2の本体で、この本体21には一端側
(図2奥側)に古紙を取り込む取入口22を、他端側に
(図手前側に)解繊したパルプ原料を排出する排出口2
3を設け、さらに該本体21内には一端側から他端側
(図において、奥手前方向)に水平に設けた駆動軸26
によって高速回転する回転子24を収納してある。
For dry defibration of waste paper, the defibration machine 2 as most clearly shown in FIG. 2 can be used. That is, 21 is the main body of the defibrating machine 2, and the main body 21 has an inlet 22 for taking in the used paper at one end side (the back side in FIG. 2) and discharging the defibrated pulp raw material for the other end side (to the front side in the figure) Outlet 2
3, and a drive shaft 26 horizontally provided in the main body 21 from one end side to the other end side (front side in the drawing).
A rotor 24 that rotates at high speed is stored.

【0021】そして、上記回転子24は多数の放射状翼
24a,24a,24a・・・で構成され、一方、本体
21の放射状翼24a,24a,24a・・・の先端よ
り所定の距離離れた位置にある内壁には奥手前方向に沿
って多数のライナー25,25,25,・・・を設け凹
凸面となしてある。なお、上記駆動軸26の一端側(回
転子24の手前側)には送風翼が取付けられ、取入口2
2より排出口23に向けて古紙を空気輸送するようにな
してある。
The rotor 24 is composed of a large number of radial blades 24a, 24a, 24a, ... A large number of liners 25, 25, 25, ... Are provided along the front direction on the inner wall in order to form an uneven surface. A blower blade is attached to one end side (front side of the rotor 24) of the drive shaft 26, and the intake port 2
The used paper is pneumatically transported from 2 toward the discharge port 23.

【0022】したがって、上記解繊機2の取入口22に
「図1」に示す古紙ホッパー1の排出口を連通させる
と、古紙ホッパー1内の古紙(本実施例では、古紙を2
〜8mm角程度にに予め裁断したものを使用してい
る。)は順次解繊機2内に流入し、本体21の内壁に衝
突して次第に解繊されて綿毛状の解繊繊維となって排出
口23より流出する。
Therefore, when the outlet 22 of the waste paper hopper 1 shown in FIG. 1 is communicated with the inlet 22 of the defibrating machine 2, the waste paper in the waste paper hopper 1 (in this embodiment, the waste paper 2
What is cut in advance to about 8 mm square is used. ) Sequentially flows into the defibration machine 2, collides with the inner wall of the main body 21 and is gradually defibrated into fluffy defibration fibers, and flows out from the outlet 23.

【0023】そして、パルプ繊維にはセルロースよりな
る繊維に種々の填料(クレー、滑石、炭酸カルシュー
ム、チタン白等で、紙の平滑度、不透明性、重量等を増
加するため配合される)が配合され、また印刷インキ等
が付着しているので必要に応じては解繊繊維と、填料及
び付着物とを分離する。この分離は古紙を解繊すると比
較的長い繊維物と、粒形が小さい粉状の填料及び付着物
とになるので両者の分離は容易で、篩分分離、分級分離
等の従来の乾式分離装置が使用できる。
The pulp fibers are made of cellulose and various fillers (such as clay, talc, calcium carbonate, and titanium white, which are added to increase the smoothness, opacity, and weight of the paper). Since the printing ink and the like are attached, the defibrated fiber is separated from the filler and the attached matter, if necessary. In this separation, when waste paper is defibrated, it becomes a relatively long fibrous material and powdery filler and deposits with a small particle shape, so it is easy to separate the two. Conventional dry separation equipment such as sieving separation and classification separation. Can be used.

【0024】なお、上記乾式分離装置の具体例としては
「図1」に示すごとき、従来公知な構成のサイクロン分
離装置4を使用すると、比重は小さいが大きくて重い繊
維はサイクロン本体41の下部にたまり、比重は大きい
が小さくて軽い填料及び付着物は気流に随伴して上部排
出口42から流出してバッグフィルター43等で捕集さ
れる。また、このサイクロン分離装置のサイクロン本体
41の下部にたまった繊維は気密ロータリーフィーダ4
4を介して下部排出口より順次取出すようになせばよ
い。
As shown in FIG. 1 as a concrete example of the dry separation device, if a cyclone separation device 4 having a conventionally known structure is used, large and heavy fibers having a small specific gravity are generated in the lower part of the cyclone body 41. Accumulation and small and light fillers and deposits having a large specific gravity flow out from the upper discharge port 42 along with the air flow and are collected by the bag filter 43 and the like. Further, the fibers accumulated in the lower portion of the cyclone body 41 of this cyclone separating device are airtight rotary feeder 4
It is sufficient to sequentially take out from the lower discharge port via 4.

【0025】そして、本発明は重量比で含有リグニン量
の1%以上5%を越えざる範囲で気相のオゾンと接触さ
せ、解繊繊維と共存するリグニンの表面をオゾンにより
酸化する。
According to the present invention, the surface of lignin coexisting with the defibrated fibers is oxidized by ozone by contacting with ozone in the gas phase within a range of not less than 1% and not more than 5% of the amount of lignin contained by weight.

【0026】気相オゾンは従来公知なオゾン発生装置3
で得ればよく、気相オゾンを得るには、放電式オゾナイ
ザーが好適であり、空気または酸素(純酸素を使用する
ことが望ましい。)を原料とし、この原料を放電界を通
過させることで原料中の酸素をオゾン化させる。
The vapor phase ozone is a conventionally known ozone generator 3
In order to obtain vapor phase ozone, a discharge type ozonizer is suitable, and air or oxygen (preferably pure oxygen is used) as a raw material, and this raw material is passed through a discharge field. Oxygenate oxygen in raw materials.

【0027】そして、上記オゾン酸化反応の制御は、解
繊繊維のリグニン量と気相オゾンとの混合比の他、接触
頻度、接触時間、反応時の温度等が条件項目として列挙
できるが、現実的にはオゾンの強力な酸化反応性からし
て、接触時間は数秒乃至数分という短時間で反応が完了
し、また温度条件にも大きな反応性の相違は認められな
いので、主に、混合比率のみの制御で酸化の程度を制御
できる。
In order to control the ozone oxidation reaction, contact frequency, contact time, temperature during reaction, etc. can be listed as condition items in addition to the mixing ratio of the lignin amount of the defibrated fiber and vapor phase ozone. In view of the strong oxidation reactivity of ozone, the reaction is completed within a short contact time of a few seconds to a few minutes, and there is no significant difference in reactivity under temperature conditions. The degree of oxidation can be controlled by controlling only the ratio.

【0028】したがって、リグニン含有率が明らかであ
れば、解繊繊維量と気相オゾンとの混合比を所定に保つ
ことによりほぼ安定した程度のオゾン酸化が確保できる
もので、攪拌装置等で所定量の解繊繊維を攪拌し流動床
となし、流動中の解繊繊維と一定比率のオゾンガスとを
接触するようになせばよい。なお、この両者の接触は解
繊繊維と気相オゾンとを夫々用意して、混合するように
なしてもよいが、本実施例では、解繊時に所定比率の気
相オゾンが接触するようになしてある。
Therefore, if the lignin content is clear, it is possible to secure a substantially stable degree of ozone oxidation by maintaining the mixing ratio of the defibrated fiber amount and the vapor phase ozone to a predetermined level. A certain amount of defibrated fibers may be stirred to form a fluidized bed, and the defibrated fibers being fluidized may be brought into contact with a fixed ratio of ozone gas. The contact between the two may be such that defibrated fibers and vapor-phase ozone are respectively prepared and mixed, but in the present embodiment, a predetermined ratio of vapor-phase ozone is contacted during defibration. Yes.

【0029】すなわち、「図1」に示す装置例が連続的
に機械パルプ繊維をオゾン酸化するもので、1が古紙ホ
ッパーで、この古紙ホッパー1には底部にロータリーフ
ィーダ等の定量供送装置11を設け、この定量供送装置
11の運転制御により古紙の供送量が調整できるように
なしてある。
That is, the example of the apparatus shown in FIG. 1 continuously oxidizes mechanical pulp fibers by ozone, and 1 is a waste paper hopper, and the waste paper hopper 1 has a fixed amount feeder 11 such as a rotary feeder at the bottom thereof. Is provided, and the amount of used paper fed can be adjusted by controlling the operation of the quantitative feeding device 11.

【0030】そして、上記定量供送装置11の下流側端
は解繊機2の取入口22に連通されるが、古紙の均一な
空気輸送を確保するため、上記取入口22には空気取り
入れ管5を連結して、該定量供送装置11の下流側端は
この空気取り入れ管5に連結してある。
The downstream end of the quantitative feeder 11 communicates with the inlet 22 of the defibrating machine 2, but the air inlet pipe 5 is provided in the inlet 22 in order to ensure uniform pneumatic transportation of waste paper. And the downstream side end of the constant quantity feeder 11 is connected to the air intake pipe 5.

【0031】そして、オゾン発生装置3の吐き出し口3
1を解繊機2の上流側に、具体的には上記空気取り入れ
管4の途中に連結し、オゾン発生装置3のオゾンと、ホ
ッパー1の古紙とが共に解繊機2に流入するようになし
てある。なお、上記オゾン発生装置3の吐き出し口31
と空気取り入れ管5とを連通する連管32の途中には流
量調整弁33を介挿し、気相オゾンの供送量は、この流
量調整弁33によって任意に調整できるようになしてあ
る。
The discharge port 3 of the ozone generator 3
1 is connected to the upstream side of the defibrating machine 2, specifically in the middle of the air intake pipe 4, so that ozone of the ozone generator 3 and waste paper of the hopper 1 both flow into the defibrating machine 2. is there. The outlet 31 of the ozone generator 3 is
A flow rate adjusting valve 33 is inserted in the middle of the connecting pipe 32 that connects the air intake pipe 5 with the air intake pipe 5, and the feed amount of vapor-phase ozone can be arbitrarily adjusted by the flow rate adjusting valve 33.

【0032】また、図示例では上記連管32の流量調整
弁33よりは上流側に、還流管34の一端を連結し、こ
の還流管34の他端はオゾン発生装置3の原料取り入れ
口35側に連結し、この還流管34に流量計36を取り
付け、この流量計36によってオゾン供送量を計測する
ようになしている。なお、この流量計36は連管32の
流量調整弁33よりは下流側に設けてもよいことは無論
であり、また、オゾン発生装置3にオゾン吐き出し量調
整機構を内蔵する場合は上記流量調整弁33を省略し、
該量調整機構の作動からオゾン供送量を計測するように
なしてもよいものである。
In the illustrated example, one end of a reflux pipe 34 is connected to the upstream side of the flow rate adjusting valve 33 of the connecting pipe 32, and the other end of the reflux pipe 34 is on the raw material intake port 35 side of the ozone generator 3. The flow meter 36 is attached to the reflux pipe 34, and the ozone supply amount is measured by the flow meter 36. It is needless to say that the flow meter 36 may be provided on the downstream side of the flow rate adjusting valve 33 of the connecting pipe 32. Further, when the ozone generator 3 has a built-in ozone discharge amount adjusting mechanism, the above flow rate adjusting is performed. Omit valve 33,
The ozone delivery amount may be measured from the operation of the amount adjusting mechanism.

【0033】なお、リグニン量はサンプリング弁51よ
りサンプルを適宜抜き取り分析してその値を測定する。
この値は機械パルプ古紙とと化学パルプ古紙との混合比
によって変化するもので、古紙の種類が変化した場合は
サンプリング分析を頻繁に行うことが望ましい。なお、
光学式連続分析装置によって色調の変化からリグニン量
を求めることも将来的には可能である。
The amount of lignin is measured by sampling a sample appropriately from the sampling valve 51 and analyzing it.
This value changes depending on the mixing ratio of mechanical pulp waste paper and chemical pulp waste paper, and it is desirable to perform sampling analysis frequently when the type of waste paper changes. In addition,
It is possible in the future to determine the amount of lignin from the change in color tone with an optical continuous analyzer.

【0034】また、60は制御盤で、この制御盤60は
りオゾン供送量と古紙供送量(ロータリーフィーダの回
転数)とをリグニン含有率を参照に所定の割合に保つよ
うになしてある。すなわち、ロータリーフィーダ11の
回転数等から古紙の時間あたりの供送量を検出し、サン
プリング分析して入力したリグニン含有率でリグニン量
を求め、流量調整弁33を制御してオゾンの供送量を所
定に保つようになしてある。なお、流量計36によって
オゾン供送量を検知して古紙供送量を制御してもよいの
は無論である。また、一般的なオゾン発生装置3はその
出力が固定、すなわち、単位時間あたりのオゾン発生量
は一定となっているが、このオゾン発生量が調整可能な
場合は、無論、このオゾン発生量を制御盤60で参照し
てオゾン供送量を調整するのは無論である。
Reference numeral 60 denotes a control panel which controls the amount of ozone fed and the amount of used paper fed (the number of rotations of the rotary feeder) to a predetermined ratio with reference to the lignin content. . That is, the amount of waste paper delivered per hour is detected from the number of revolutions of the rotary feeder 11, sampling analysis is performed to obtain the lignin amount by the input lignin content rate, and the flow rate adjustment valve 33 is controlled to deliver ozone. Is designed to be maintained at a predetermined level. Needless to say, the flowmeter 36 may detect the ozone feed amount and control the used paper feed amount. In addition, the output of the general ozone generator 3 is fixed, that is, the ozone generation amount per unit time is constant, but if this ozone generation amount is adjustable, of course, this ozone generation amount is adjusted. It is needless to say that the ozone feed amount is adjusted by referring to the control panel 60.

【0035】なお、オゾン量を含有リグニン量の1%以
上5%を越えざる範囲となしたのは、リグニンの表面を
オゾン酸化するには必要十分のの量であり、種々測定の
結果、3〜4%程度で最も効率的にリグニン表面を酸化
し、それ以上のオゾンは解繊繊維に直接作用し繊維を損
傷する傾向が認められた。
The amount of ozone was in the range of not less than 1% and not more than 5% of the amount of contained lignin, which was the amount necessary and sufficient for ozone oxidation of the surface of lignin. As a result of various measurements, 3 It was observed that the lignin surface was most efficiently oxidized at about 4%, and that ozone higher than that tends to directly act on the defibrated fiber and damage the fiber.

【0036】[0036]

【発明の効果】本発明は上記のごとく、古紙を乾式解繊
するため、簡易な装置で古紙を処理でき、多量の水を使
用することもないので都市近郊でも処理でき、しかも、
繊維の枝状構造が失われないオゾンによる解繊古紙のボ
ンディング特性改善方法を提供することができるもので
ある。
INDUSTRIAL APPLICABILITY As described above, according to the present invention, since waste paper is dry defibrated, it can be treated with a simple device, and since it does not use a large amount of water, it can be treated in the suburbs of the city.
It is possible to provide a method for improving the bonding property of defibrated waste paper by ozone in which the branch structure of the fiber is not lost.

【0037】また、本発明は含有リグニンをオゾンで酸
化し、オゾン酸化リグニンとなしてあるので、表面が凹
凸面的で、反応性が大きくなり、繊維どうしが絡み易く
なるオゾンによる解繊古紙のボンディング特性改善方法
を提供することができるものである。
Further, according to the present invention, since the contained lignin is oxidized with ozone to form ozone-oxidized lignin, the surface is uneven, the reactivity is increased, and the fibers are easily entangled. It is possible to provide a bonding characteristic improving method.

【0038】まお、本発明により得られた解繊繊維は、
再生紙原料として使用できることは無論であるが、加熱
プレスしてボードとし、さらには、適宜バインダーを加
えて建築資材ボードとなす等の種々の利用が可能で、こ
のように古紙の利用範囲を拡大することにより、リサイ
クル率を向上でき資源有効活用に大きな貢献ができるも
のである。
Mao, defibrated fiber obtained by the present invention,
Of course, it can be used as a recycled paper raw material, but it can be used in various ways, such as by heat-pressing it into a board, and then adding a binder to form a board for building materials. By doing so, the recycling rate can be improved and a great contribution can be made to effective use of resources.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明法を実施する装置例正面図である。FIG. 1 is a front view of an example of an apparatus for carrying out the method of the present invention.

【図2】本発明に使用される解繊機の一例を示す縦断面
図である。
FIG. 2 is a vertical sectional view showing an example of a defibrating machine used in the present invention.

【図3】パルプ繊維の断面略図である。FIG. 3 is a schematic sectional view of pulp fibers.

【符号の説明】[Explanation of symbols]

1 ホッパー 2 解繊機 3 オゾン発生装置 4 サイクイロン分離装置 1 Hopper 2 Defiberizer 3 Ozone generator 4 Cyclone separator

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 リグニンを含有する古紙を乾式解繊し、
重量比で含有リグニン量の1%以上5%を越えざる範囲
で気相のオゾンと接触させ、解繊繊維と共存するリグニ
ンの表面をオゾンにより酸化することを特徴としたオゾ
ンによる解繊古紙のボンディング特性改善方法。
1. Dry defibration of waste paper containing lignin,
In the defibrated waste paper by ozone, which is characterized in that the surface of lignin coexisting with defibrated fibers is oxidized by ozone by contacting with vapor phase ozone within the range of 1% or more and 5% or more of the lignin content in weight ratio. Bonding property improvement method.
JP13118193A 1993-05-07 1993-05-07 Method for improving the bonding characteristics of defibrated waste paper using ozone Expired - Fee Related JP3212759B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13118193A JP3212759B2 (en) 1993-05-07 1993-05-07 Method for improving the bonding characteristics of defibrated waste paper using ozone

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13118193A JP3212759B2 (en) 1993-05-07 1993-05-07 Method for improving the bonding characteristics of defibrated waste paper using ozone

Publications (2)

Publication Number Publication Date
JPH06316888A true JPH06316888A (en) 1994-11-15
JP3212759B2 JP3212759B2 (en) 2001-09-25

Family

ID=15051912

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP3212759B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012517346A (en) * 2009-02-11 2012-08-02 キシレコ インコーポレイテッド Biomass processing method

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012517346A (en) * 2009-02-11 2012-08-02 キシレコ インコーポレイテッド Biomass processing method
US9181567B2 (en) 2009-02-11 2015-11-10 Xyleco, Inc. Processing biomass
US9353344B2 (en) 2009-02-11 2016-05-31 Xyleco, Inc. Processing biomass
US9493495B2 (en) 2009-02-11 2016-11-15 Xyleco, Inc. Processing biomass
US10011625B2 (en) 2009-02-11 2018-07-03 Xyleco, Inc. Processing facility
US10519180B2 (en) 2009-02-11 2019-12-31 Xyleco, Inc. Processing biomass

Also Published As

Publication number Publication date
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