JP2005206978A - Method for producing waste paper pulp - Google Patents
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- JP2005206978A JP2005206978A JP2004015566A JP2004015566A JP2005206978A JP 2005206978 A JP2005206978 A JP 2005206978A JP 2004015566 A JP2004015566 A JP 2004015566A JP 2004015566 A JP2004015566 A JP 2004015566A JP 2005206978 A JP2005206978 A JP 2005206978A
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- 239000010893 paper waste Substances 0.000 title claims abstract description 49
- 229920001131 Pulp (paper) Polymers 0.000 title claims abstract description 46
- 238000004519 manufacturing process Methods 0.000 title claims abstract description 21
- 239000000701 coagulant Substances 0.000 claims abstract description 34
- 239000002994 raw material Substances 0.000 claims abstract description 18
- 238000000034 method Methods 0.000 claims description 18
- 229920002873 Polyethylenimine Polymers 0.000 claims description 7
- 238000004061 bleaching Methods 0.000 claims description 7
- 239000002761 deinking Substances 0.000 claims description 7
- 239000000428 dust Substances 0.000 claims description 7
- 229920002401 polyacrylamide Polymers 0.000 claims description 6
- 229920000768 polyamine Polymers 0.000 claims description 6
- 238000005406 washing Methods 0.000 claims description 6
- 239000000203 mixture Substances 0.000 claims description 5
- 229920000642 polymer Polymers 0.000 claims description 5
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 claims description 3
- RRHXZLALVWBDKH-UHFFFAOYSA-M trimethyl-[2-(2-methylprop-2-enoyloxy)ethyl]azanium;chloride Chemical compound [Cl-].CC(=C)C(=O)OCC[N+](C)(C)C RRHXZLALVWBDKH-UHFFFAOYSA-M 0.000 claims description 3
- 239000000945 filler Substances 0.000 abstract description 9
- 239000010802 sludge Substances 0.000 abstract description 5
- 238000004140 cleaning Methods 0.000 abstract 1
- 239000000123 paper Substances 0.000 description 16
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 12
- 239000002002 slurry Substances 0.000 description 8
- 230000000052 comparative effect Effects 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- 230000000694 effects Effects 0.000 description 6
- 238000011156 evaluation Methods 0.000 description 5
- 229920003171 Poly (ethylene oxide) Polymers 0.000 description 4
- -1 and further Substances 0.000 description 4
- 125000000129 anionic group Chemical group 0.000 description 4
- 229920006318 anionic polymer Polymers 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 238000004064 recycling Methods 0.000 description 3
- 238000009472 formulation Methods 0.000 description 2
- 239000000976 ink Substances 0.000 description 2
- 229910010272 inorganic material Inorganic materials 0.000 description 2
- 239000011147 inorganic material Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 150000008442 polyphenolic compounds Chemical class 0.000 description 2
- 235000013824 polyphenols Nutrition 0.000 description 2
- 238000007639 printing Methods 0.000 description 2
- 229920005989 resin Polymers 0.000 description 2
- 239000011347 resin Substances 0.000 description 2
- KXGFMDJXCMQABM-UHFFFAOYSA-N 2-methoxy-6-methylphenol Chemical class [CH]OC1=CC=CC([CH])=C1O KXGFMDJXCMQABM-UHFFFAOYSA-N 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 239000006229 carbon black Substances 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 229920006317 cationic polymer Polymers 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000005202 decontamination Methods 0.000 description 1
- 230000003588 decontaminative effect Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000011234 economic evaluation Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 238000005188 flotation Methods 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000003112 inhibitor Substances 0.000 description 1
- 239000002655 kraft paper Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000002791 soaking Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
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- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/64—Paper recycling
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Abstract
Description
本発明は、古紙パルプの製造方法に関し、特に高灰分の古紙パルプの製造方法に関するものである。 The present invention relates to a method for producing waste paper pulp, and more particularly to a method for producing waste paper pulp having a high ash content.
従来、抄紙段階における填料や微細繊維の歩留り向上については、種々の歩留り剤及び歩留りシステムが検討・採用されている。最も多く採用されてきたシステムはカチオン性ポリマーを用いたポリマー単独処方である。しかしながら、古紙再生処理工程においては、古紙に由来する汚れ、カーボンブラック等の印刷インクを除去する必要があるため、これらの阻害物質の除去を困難にする凝結剤の使用は全く考えられなかった。また、凝結剤を使用しても、古紙に含まれる機械パルプやアニオン性物質や懸濁コロイド物質などの影響によりその効果が発揮できなくなるという欠点があった。 Conventionally, various yield agents and yield systems have been studied and adopted for improving the yield of fillers and fine fibers in the papermaking stage. The most widely adopted system is a single polymer formulation using a cationic polymer. However, in the used paper recycling process, it is necessary to remove stains derived from used paper and printing inks such as carbon black, and therefore it has not been considered at all to use a coagulant that makes it difficult to remove these inhibitors. Further, even when a coagulant is used, there is a drawback that the effect cannot be exhibited due to the influence of mechanical pulp, anionic substance, suspended colloidal substance, etc. contained in the used paper.
そこで、従来の一般的な古紙パルプの製造方法においては、古紙原料中の灰分に関係なく、離解、除塵、漂白、脱墨、洗浄の各工程を経て古紙パルプが製造され、かつ洗浄工程で灰分除去を実施し、低灰分の古紙パルプを製造する方法が主流であった。 Therefore, in the conventional general waste paper pulp manufacturing method, waste paper pulp is manufactured through the steps of disaggregation, dust removal, bleaching, deinking, and washing regardless of the ash content in the waste paper raw material, and the ash content in the washing step. The mainstream method is to carry out the removal and produce waste paper pulp with low ash content.
また、古紙再生処理工程においてアニオン性ポリマーを用いる処方も検討されるが、ポリマー自身がアニオン性であることから、古紙に含まれる機械パルプやアニオン性物質や懸濁コロイド物質などの影響は受け難い特徴をもっているものの、古紙再生処理工程内でのアニオン性のポリマーの循環により脱墨、漂白を阻害する要因になるという欠点があった。 In addition, prescription using an anionic polymer in the used paper recycling process is also considered, but since the polymer itself is anionic, it is not easily affected by mechanical pulp, anionic substances and suspended colloidal substances contained in the used paper. Although it has the characteristics, there is a drawback in that deinking and bleaching are hindered by the circulation of the anionic polymer in the used paper recycling process.
さらに、ポリエチレンオキサイドを歩留り向上システムに用いる技術も検討され、古紙に含まれる機械パルプやアニオン性物質や懸濁コロイド物質などの影響は受け難いという利点があるが、ポリエチレンオキサイド単独で使用されることは少なく、ポリエチレンオキサイドとポリフェノール樹脂(スルホン化フェノールホルムアルデヒド樹脂)を併用する方法が知られている(例えば、特許文献1参照。)。
ところが、従来の古紙パルプの製造方法では、古紙パルプの灰分が低くなり、そのため抄紙工程で使用する填料が増加してコスト高になるという問題がある一方で、製造工程から排出される廃棄物が増加するために環境悪化の原因になるという問題がある。 However, the conventional waste paper pulp manufacturing method has a problem that the ash content of the waste paper pulp is low, which increases the cost of the filler used in the paper making process, while the waste discharged from the manufacturing process is high. There is a problem that the increase causes environmental degradation.
また、ポリエチレンオキサイドとポリフェーノール樹脂を併用する処方でも、2液を用いることから薬品コストが高くなるという問題があり、さらに古紙処理工程内の循環によりアニオン性ポリマーと同様に、脱墨、漂白の効率・効果を阻害する要因になるという欠点がある。 Also, the formulation using both polyethylene oxide and polyphenol resin has the problem of high chemical costs due to the use of two liquids, and further, deinking and bleaching in the same way as anionic polymers due to circulation in the waste paper treatment process. There is a disadvantage that it becomes a factor that hinders the efficiency and effectiveness of the system.
本発明は、上記従来の問題点に鑑み、高灰分印刷古紙から高灰分で高白色度の古紙パルプが得られ、スラッジ灰の低減と使用填料の低減を図ることができる古紙パルプの製造方法を提供することを課題とする。 In view of the above-mentioned conventional problems, the present invention provides a method for producing waste paper pulp that can obtain waste paper pulp having high ash content and high whiteness from high ash printed waste paper, which can reduce sludge ash and use fillers. The issue is to provide.
本発明の古紙パルプの製造方法は、古紙の離解、除塵、漂白、脱墨、洗浄の各処理工程を経た古紙パルプに対して、抄紙機の原料調整工程へ流送する前に凝結剤を添加するものである。 The method for producing waste paper pulp of the present invention is to add a coagulant to waste paper pulp that has been subjected to the treatment processes of waste paper decontamination, dust removal, bleaching, deinking, and washing, before being sent to the raw material adjustment process of the paper machine. To do.
市中から回収された古紙を原料とした古紙パルプは、古紙由来の汚れ、カーホンブラック等の印刷インキ成分を多く含むため、上記のように離解、除塵、漂白、脱墨、洗浄工程等を経て不純物を除去して原料パルプとして再生されており、かつ再生された古紙パルプの完成原料にはクラフトパルプと比して依然填料等の無機物を多く含むとともに、その無機物は脱墨、漂白工程を経ているため、概ね白色度が高く、原料パルプに含まれていても原料パルプとしての使用を妨げるものではない。そこで、本発明では古紙パルプの製造工程の最終段階に凝結剤を添加することで、古紙パルプに灰分が凝結され、高灰分で高白色度の古紙パルプが得られる。かくして、古紙パルプを用いた抄紙機の原料調整工程以降での灰分流出を防止してスラッジ灰の発生量を抑制することができるとともに、使用填料を低減してコスト低下を図ることができる。 Waste paper pulp made from waste paper collected from the city contains a lot of printing ink components such as dirt derived from waste paper and carphone black, so as described above, disaggregation, dust removal, bleaching, deinking, washing process, etc. After the removal of impurities, it is recycled as raw material pulp, and the finished material of recycled recycled paper pulp still contains more inorganic materials such as fillers than kraft pulp, and the inorganic materials are subjected to deinking and bleaching processes. Therefore, the whiteness is generally high, and even if it is contained in the raw material pulp, it does not hinder the use as the raw material pulp. Therefore, in the present invention, by adding a coagulant to the final stage of the used paper pulp manufacturing process, ash is condensed in the used paper pulp, and used paper pulp having high ash content and high whiteness can be obtained. Thus, it is possible to prevent the outflow of ash after the raw material adjustment step of the paper machine using waste paper pulp and suppress the generation amount of sludge ash, and to reduce the use filler and reduce the cost.
また、凝結剤を添加する流送原料は、パルプ濃度が2〜5%、温度が20〜60℃、PH4〜10に収めておくことが好ましい。そして、凝結剤の添加量は、対絶乾パルプ100〜1000重量ppmが好適である。100重量ppm未満では十分な効果が発揮されず、1000重量ppmを超えるとパイプ汚れ等の問題を生じる恐れがある。 Further, it is preferable that the feed material to which the coagulant is added is stored in a pulp concentration of 2 to 5%, a temperature of 20 to 60 ° C., and a pH of 4 to 10. And, the addition amount of the coagulant is preferably 100 to 1000 ppm by weight against the dry pulp. If it is less than 100 ppm by weight, sufficient effects are not exhibited, and if it exceeds 1000 ppm by weight, problems such as pipe contamination may occur.
また、凝結剤は、硫酸アルミニウム、ポリアクリルアミド、ポリダドマック、ポリアミン、ポリエチレンイミン、2−(メタクリロイルオキシ)エチルトリメチルアンモニウムクロリド重合物、変性ポリエチレンイミンから選択された何れか1つ若しくは複数の混合物から成るのが好適である。 The coagulant is composed of any one or a mixture selected from aluminum sulfate, polyacrylamide, polydadomac, polyamine, polyethyleneimine, 2- (methacryloyloxy) ethyltrimethylammonium chloride polymer, and modified polyethyleneimine. Is preferred.
凝結剤の添加場所は、流送ポンプまたは流送チェストで添加するのが好適である。 The addition place of the coagulant is preferably added by a flow pump or a flow chest.
本発明によれば、古紙パルプを抄紙機の原料調整工程へ流送する前に、その流送原料に凝結剤を添加することで高灰分で高白色度の古紙パルプが得られ、スラッジ灰の発生量を抑制することができかつ使用填料を低減してコスト低下を図ることができる。 According to the present invention, before the waste paper pulp is fed to the raw material adjustment process of the paper machine, a waste paper pulp having high ash content and high whiteness can be obtained by adding a coagulant to the feed raw material. The generation amount can be suppressed, and the cost can be reduced by reducing the filler used.
以下、本発明の古紙パルプの製造方法の一実施形態について、図1を参照して詳細に説明する。 Hereinafter, an embodiment of the method for producing waste paper pulp of the present invention will be described in detail with reference to FIG.
図1において、1は、高灰分印刷古紙をパルパーにて解離し、解離したパルプに対して除塵処理と、アルカリソーキング処理と、フローテーション処理及び/又は洗浄処理を行って脱墨し、必要に応じて漂白して完成した古紙パルプ(DIP)を貯留する古紙パルプタンク(DIPタンク)である。DIPタンク1中のDIPは、取出ポンプ2にて必要量づつ取り出されて流送チェスト3に送給され、流送チェスト3から白水ピット4中の白水で2〜5%程度の所定濃度のDIPスラリーに希釈されて流送ポンプ5にて抄紙機11の原料調整工程部6に流送される。
In FIG. 1, 1 is a high-ash content waste paper dissociated by a pulper, and deinked by performing dust removal treatment, alkali soaking treatment, flotation treatment and / or washing treatment on the dissociated pulp. It is a used paper pulp tank (DIP tank) which stores used paper pulp (DIP) which was bleached in response. The required amount of DIP in the DIP tank 1 is taken out by the take-
原料調整工程部6では、その入口部に脱水装置7が配設され、流送されたDIPスラリーはこの脱水装置7によって抄紙原料として配合するのに適した濃度に脱水される。脱水した白水は白水ピット8に一旦貯留された後、DIP製造工程部の白水ピット4に還流される。脱水装置7にて所定濃度とされたDIPスラリーは、DIPチェスト9に一旦受け入れられた後、配合チェスト10に送給され、他の各種原料と配合された後、抄紙機11に送給される。
In the raw material adjusting process section 6, a
DIP製造工程部の最終段階で、流送チェスト3内のDIPスラリーに対して凝結剤12を添加するように構成されている。なお、流送チェスト3内に添加する代わりに仮想線で示すように流送ポンプ5のサクション側に添加するようにしても良い。このようにDIP製造工程部の最終段階でDIPスラリーに凝結剤12を添加することで、高灰分印刷古紙を離解した古紙パルプで、含有灰分10%以上の古紙パルプが得られる。
The
凝結剤12としては、硫酸アルミニウム、ポリアクリルアミド、ポリダドマック、ポリアミン、ポリエチレンイミン、2−(メタクリロイルオキシ)エチルトリメチルアンモニウムクロリド重合物、変性ポリエチレンイミンが好適であり、これらの内から1種若しくは複数種の混合物を添加するのが好適である。また、添加量は、対絶乾パルプ100〜1000重量ppm程度が好適である。100重量ppm未満では十分に凝結効果が発揮されず、1000重量ppmを超えると、過剰の添加剤が洩れ出して流送パイプにゴミの固まりを作ってしまう恐れがあり、好ましくない。
As the
このように古紙パルプ製造工程の最終段階で、流送チェスト3または流送ポンプ5のサクション側でDIPスラリーに凝結剤12を添加することで、凝結剤12にて灰分をパルプに凝結させることができて高灰分で高白色度の古紙パルプが得られる。そのため、古紙パルプを用いた抄紙機11の原料調整工程6以降での灰分流出を防止してスラッジ灰の発生量を抑制することができるとともに、使用填料を低減してコスト低下を図ることができる。
In this way, at the final stage of the used paper pulp manufacturing process, the
なお、原料調整工程6の脱水装置7においても、ポリアクリルアミド、ポリダドマック、ポリアミン、ポリエチルイミンなどの凝結剤を添加することで フィルタでの灰分歩留りが向上し、白水へ流出する灰分の低減を図り、排水への灰分流出を低減することができる。
In addition, in the
次に、本発明のいくつかの実施例と比較例を説明する。 Next, some examples and comparative examples of the present invention will be described.
高灰分印刷古紙を用いて脱墨処理された古紙パルプ(DIP)を用い、所要量の填料を添加してLWCP(Low Weight Coated Paper )を抄造するに際して、流送チェスト3又は流送ポンプ5で、表1に示すように、実施例1〜7と比較例1、2として、ポリアクリルアミド、ポリダドマック、ポリアミン、ポリエチレンイミンを、対絶乾パルプで50、100、500、1000、2000重量ppm添加した。また、比較例3として、DIPスラリーに凝結剤を添加せずに同じくLWCPを抄造した。 When making LWCP (Low Weight Coated Paper) using waste paper pulp (DIP) that has been deinked using high ash printed waste paper, As shown in Table 1, as Examples 1 to 7 and Comparative Examples 1 and 2, polyacrylamide, polydadomac, polyamine, and polyethyleneimine were added at 50, 100, 500, 1000, and 2000 ppm by weight as dry dry pulp. . Further, as Comparative Example 3, LWCP was similarly made without adding a coagulant to the DIP slurry.
そして、各実施例1〜7及び比較例1〜3について、灰分の歩留りを示すパルプ中の灰分含有率(%)と返送水のSS(ppm)を測定した。また、添加する凝結剤の添加量から経済性について○と×に相対評価し、総合評価を行った。その結果を表1に示す。 And about each Examples 1-7 and Comparative Examples 1-3, the ash content rate (%) in the pulp which shows the yield of ash content, and SS (ppm) of returned water were measured. In addition, from the amount of the coagulant to be added, the economic efficiency was evaluated relative to ○ and ×, and comprehensive evaluation was performed. The results are shown in Table 1.
表1中の実施例1〜7から、凝結剤を100〜1000重量ppm、流送チェスト又は流送ポンプで添加することで、灰分含有量11%以上を確保することができることが分かる。また、凝結剤としては、実施例1〜3のポリアクリルアミド、ポリダドマック、ポリアミンと、実施例4〜7のポリエチルイミンを比較すると、ポリエチルイミンを添加した実施例4〜7において返送水のSSが明らかにより低減できているため、特に効果的であることが分かる。また、実施例5、6、7から、凝結剤の添加量を上記範囲内で増加するのに伴ってより大きな効果が発揮されることが分かる。そして、凝結剤としてポリエチルイミンを500重量ppm、流送チェスト又は流送ポンプで添加したものが、総合評価で最良となった。 From Examples 1 to 7 in Table 1, it can be seen that an ash content of 11% or more can be ensured by adding a coagulant at 100 to 1000 ppm by weight with a flow chest or flow pump. In addition, as a coagulant, the polyacrylamide, polydadomac, and polyamine of Examples 1 to 3 and the polyethylimine of Examples 4 to 7 were compared. In Examples 4 to 7 to which polyethylimine was added, SS of the return water was used. It can be seen that this is particularly effective because it can be clearly reduced. Further, Examples 5, 6, and 7 show that a greater effect is exhibited as the amount of the coagulant is increased within the above range. And what added polyethylimine as a coagulant 500 weight ppm with a flow chest or a flow pump became the best in comprehensive evaluation.
これに対して、凝結剤を2000重量ppm添加した比較例1では、灰分含有量及び返送水のSSが、凝結剤を1000重量ppm添加した実施例7と殆ど変わらないので、無駄に凝結剤コストが高くなるため経済性が悪く、総合評価は不良である。また、表中には表示していないが過剰の凝結剤によって流送パイプにゴミの固まりを生じ易く、メンテナンス回数が増加する恐れも考えられる。また、凝結剤を50重量ppm添加した比較例2では、凝結剤の添加効果があまり得られず、灰分含有量10%を確保するのがやっとであり、返送水のSSも高く、経済性は良いが、効果が低いので総合評価は不良である。また、凝結剤を添加していない比較例3では、灰分含有量が低く、特に返送水のSSが500ppmと高く、灰分回収ができていないことが分かる。 On the other hand, in Comparative Example 1 in which the coagulant was added by 2000 ppm by weight, the ash content and the SS of the return water were almost the same as those in Example 7 in which the coagulant was added by 1000 ppm by weight. Therefore, the economic evaluation is poor and the overall evaluation is poor. In addition, although not shown in the table, excessive coagulant tends to cause a lump of dust in the flow pipe, which may increase the number of maintenance. Further, in Comparative Example 2 in which 50 ppm by weight of the coagulant was added, the effect of adding the coagulant was not obtained so much, and it was finally possible to secure an ash content of 10%, the SS of the return water was high, and the economic efficiency was Although good, the overall evaluation is poor because the effect is low. Moreover, in the comparative example 3 which has not added the coagulant | flocculant, it turns out that ash content is low, especially SS of return water is as high as 500 ppm, and ash content collection | recovery has not been performed.
本発明の古紙パルプの製造方法は、古紙パルプを抄紙機の原料調整工程へ流送する前にその流送原料に凝結剤を添加することで、高灰分で高白色度の古紙パルプが得られ、スラッジ灰の発生量を抑制しかつ使用填料を低減してコスト低下を図ることができるので、全ての古紙パルプを用いた抄造製品に有用である。 The method for producing waste paper pulp of the present invention provides a high whiteness and high whiteness waste paper pulp by adding a coagulant to the feed material before feeding the waste paper pulp to the raw material adjustment step of the paper machine. In addition, since it is possible to reduce the cost by suppressing the amount of sludge ash generated and reducing the amount of filler used, it is useful for all papermaking products using waste paper pulp.
1 古紙パルプタンク(DIPタンク)
3 流送チェスト
5 流送ポンプ
12 凝結剤
1 Waste paper pulp tank (DIP tank)
3 Flowing chest 5
Claims (4)
The method for producing waste paper pulp according to any one of claims 1 to 3, wherein the coagulant is added to a flow pump or a flow chest.
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Cited By (2)
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JP2005206979A (en) * | 2004-01-23 | 2005-08-04 | Daio Paper Corp | Method for producing waste paper pulp |
WO2008123493A1 (en) | 2007-03-30 | 2008-10-16 | Nippon Paper Industries Co., Ltd. | Process for producing coated-paper base and for producing coated paper |
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