JP2007222710A - Method and apparatus for regenerating waste liquid of printer - Google Patents

Method and apparatus for regenerating waste liquid of printer Download PDF

Info

Publication number
JP2007222710A
JP2007222710A JP2006043808A JP2006043808A JP2007222710A JP 2007222710 A JP2007222710 A JP 2007222710A JP 2006043808 A JP2006043808 A JP 2006043808A JP 2006043808 A JP2006043808 A JP 2006043808A JP 2007222710 A JP2007222710 A JP 2007222710A
Authority
JP
Japan
Prior art keywords
waste liquid
liquid
water
container
regeneration
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Withdrawn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
JP2006043808A
Other languages
Japanese (ja)
Inventor
Yasuharu Suda
康晴 須田
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP2006043808A priority Critical patent/JP2007222710A/en
Publication of JP2007222710A publication Critical patent/JP2007222710A/en
Withdrawn legal-status Critical Current

Links

Images

Landscapes

  • Inking, Control Or Cleaning Of Printing Machines (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To easily separate washing waste liquid containing ink pigment, water and washing liquid used in a printer with a single device. <P>SOLUTION: In this method for regenerating the waste liquid containing ink pigment, organic washing liquid and water by charging the waste liquid into a waste liquid regeneration apparatus having a regeneration vessel, an emulsion treating agent for breaking emulsion mainly consisting of water and washing liquid and coagulating ink pigment particles is added to the waste liquid, then the waste liquid is separated into regenerated washing liquid, ink pigment and water by using a gravity settling method. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、印刷機のブランケット胴などのインキが付着する印刷機の構成部品の洗浄時に出る廃液を再生する方法に関し、特に、インキ顔料、油性の洗浄液、及び水の3成分が混在した系において、簡便な装置で3成分を分離する、印刷機の廃液再生方法および廃液再生装置に関する。さらに詳しくは、前記3成分が混在した廃液を強く攪拌すると発生するヘドロ状物質が含まれる系において、重力場、ろ過などの物理的な作用だけでは3成分が分離できないような状況でさえも、容易に前記3成分を分離することができる印刷機の廃液再生方法および廃液再生装置に関する。   TECHNICAL FIELD The present invention relates to a method for regenerating waste liquid generated when cleaning a printing press component such as a printing press blanket cylinder, particularly in a system in which three components of an ink pigment, an oily cleaning liquid, and water are mixed. The present invention relates to a waste liquid recycling method and a waste liquid recycling apparatus for a printing press, in which three components are separated by a simple device. More specifically, in a system containing sludge-like substances generated when the waste liquid mixed with the three components is vigorously stirred, even in a situation where the three components cannot be separated only by physical action such as gravity field and filtration, The present invention relates to a waste liquid recycling method and a waste liquid recycling apparatus for a printing press that can easily separate the three components.

印刷機のブランケット胴や圧胴の洗浄時には廃液が出るが、環境を考慮して、また洗浄剤のランニングコスト低減のため、この廃液を再生処理して洗浄液を再利用しようとする動きが出てきている。   Waste liquid comes out when cleaning the blanket cylinder and impression cylinder of the printing press. However, in consideration of the environment and to reduce the running cost of cleaning agents, there is a movement to recycle this waste liquid and reuse the cleaning liquid. ing.

再生方法として最も低コストな方法が沈降法である。図4に、洗浄液中に混入した顔料を沈降法によって分離する方式の廃液再生装置の概略構成を示す(特許文献1参照)。図4に示すように、従来の廃液再生装置51は、洗浄廃液(廃液)52を溜める容器53を備えており、この容器53の底壁には底部排出配管54が接続され、容器53の側壁には側部排出配管55が接続されている。さらに、これらの排出配管54,55のうち、底部排出配管54の出口下方には濃縮廃液回収容器56が配設され、側部排出配管55の出口下方には再生洗浄液回収容器57が配設されている。また、一方の底部排出配管54の通路には開閉バルブ58が接続され、他方の側部排出配管55の通路には、その上流側に開閉バルブ59が接続され、その下流側にフィルタ60が配設されている。   The lowest cost method for regeneration is the sedimentation method. FIG. 4 shows a schematic configuration of a waste liquid regenerating apparatus that separates the pigment mixed in the cleaning liquid by a sedimentation method (see Patent Document 1). As shown in FIG. 4, the conventional waste liquid regenerating apparatus 51 includes a container 53 for storing cleaning waste liquid (waste liquid) 52, and a bottom discharge pipe 54 is connected to the bottom wall of the container 53. A side discharge pipe 55 is connected to the. Further, of these discharge pipes 54 and 55, a concentrated waste liquid recovery container 56 is disposed below the outlet of the bottom discharge pipe 54, and a regenerated cleaning liquid recovery container 57 is disposed below the outlet of the side discharge pipe 55. ing. In addition, an opening / closing valve 58 is connected to the passage of one bottom discharge pipe 54, an opening / closing valve 59 is connected to the upstream side of the passage of the other side discharge pipe 55, and a filter 60 is arranged downstream thereof. It is installed.

このように構成された廃液再生装置51では、印刷機のブランケット胴等を洗浄した後の廃液52を容器53に溜め、インキ顔料(単に、顔料ともいう)61の沈降を促進する薬剤を廃液52に添加することにより、インキ顔料61を容器53の底部に沈降させる。次いで、沈降したインキ顔料、すなわち濃縮廃液63を底部排出配管54から濃縮廃液回収容器56に回収し、廃液52の上澄み液を側部排出配管55からフィルタ60で濾過することによりインキ顔料61を除去し、再生洗浄液回収容器57に回収する。こうして得られた洗浄液62は再利用されることになる。   In the waste liquid regenerating apparatus 51 configured in this way, the waste liquid 52 after washing the blanket cylinder of the printing press is stored in the container 53, and a chemical that promotes the sedimentation of the ink pigment (also simply referred to as pigment) 61 is used as the waste liquid 52. Is added to the bottom of the container 53. Subsequently, the settled ink pigment, that is, the concentrated waste liquid 63 is recovered from the bottom discharge pipe 54 to the concentrated waste liquid collection container 56, and the supernatant liquid of the waste liquid 52 is filtered through the side discharge pipe 55 through the filter 60 to remove the ink pigment 61. Then, it is recovered in the regenerated cleaning liquid recovery container 57. The cleaning liquid 62 thus obtained is reused.

ところが、この方法では再生洗浄液の純度が不充分なだけでなく、インキと洗浄液の組合せによってはインキ顔料61の沈降が不充分で、すぐにフィルタ60が目詰まりしてしまうことから、フィルタ60の交換もしくは清掃を頻繁に行なわなければならないという課題があった。
一方、電子写真の分野では、溶媒中に分散させた帯電トナーを電気泳動により静電潜像に付着させて可視化する湿式現像法も一部で採用されている。このシステムにおいて、クリーニング後の廃液から帯電したトナー粒子を電気的に除去する方式も提案されている(特許文献2)。
また、非特許文献1には、トナー粒子除去装置が提示されている。
However, in this method, not only the purity of the regenerated cleaning liquid is insufficient, but the ink pigment 61 is not sufficiently settled depending on the combination of the ink and the cleaning liquid, and the filter 60 is clogged immediately. There was a problem that replacement or cleaning had to be performed frequently.
On the other hand, in the field of electrophotography, a wet development method in which a charged toner dispersed in a solvent is made to adhere to an electrostatic latent image by electrophoresis and visualized is partially adopted. In this system, a method of electrically removing charged toner particles from the waste liquid after cleaning has also been proposed (Patent Document 2).
Non-Patent Document 1 presents a toner particle removing device.

特許第3586656号公報Japanese Patent No. 3586656 特開昭53−10440号公報JP-A-53-10440 黒鳥他,「液体現像剤を用いたフルカラー電子写真プリンター」,Japan Hardcopy ’96 論文集,1996年,p.153−156Kurotori et al., “Full-color electrophotographic printer using liquid developer”, Japan Hardcopy '96 Proceedings, 1996, p. 153-156

しかしながら、特許文献2および非特許文献1に開示された技術では、導電性の水が混入した場合は想定されていない。例えば非特許文献2の装置は、回収したキャリア液に水が含まれている場合に、キャリア液と水との比重の違いを利用して水分を分離しているが、この方式では大きな装置が必要なだけでなく、分離に長い時間が掛かってしまうのは必至である。   However, in the techniques disclosed in Patent Document 2 and Non-Patent Document 1, it is not assumed that conductive water is mixed. For example, the apparatus of Non-Patent Document 2 separates moisture using the difference in specific gravity between the carrier liquid and water when the recovered carrier liquid contains water. Not only is it necessary, it is inevitable that separation takes a long time.

また、近年は有機溶剤使用の制約が厳しくなっていることもあり、洗浄時に必要最低限の有機溶剤系洗浄剤を用いた後、水で仕上げ洗浄する方式が増えている。この場合、洗浄廃液は有機溶剤系洗浄剤、顔料及び水の3成分が混合した液となるが、図4の再生装置では水が混入した3成分の洗浄廃液の再生は想定されていない。
上記の3成分を含む洗浄廃液は、強く攪拌された場合、主として洗浄剤成分と水からなるエマルションが、嵩高いヘドロ状物質として形成される。この嵩高いヘドロ状物質であるエマルションを含む廃液を重力沈降で処理しようとしても、静置するだけではエマルションはほとんど減容しないため、再生して再利用できる洗浄液は極わずかになる。また、エマルションと洗浄液及び水とを分離するために濾過操作を行うと、インキ顔料だけでなくエマルションも固形分としてフィルタ上に濾し取られ、このヘドロ状のエマルションによってフィルタがすぐに目詰まりを起こし、廃液を濾過するのに多大の手間と時間を要する。
また、濾過したエマルションを廃棄するためには産業廃棄物として処理しなければならず、処理費用が発生するなどの課題がある。
In recent years, restrictions on the use of organic solvents are becoming stricter, and after using a minimum amount of organic solvent-based cleaning agent at the time of cleaning, a method of finishing cleaning with water is increasing. In this case, the cleaning waste liquid is a liquid in which three components of an organic solvent-based cleaning agent, a pigment, and water are mixed. However, the regeneration apparatus in FIG. 4 does not assume the regeneration of the three-component cleaning waste liquid mixed with water.
When the cleaning waste liquid containing the above three components is vigorously stirred, an emulsion mainly composed of a cleaning agent component and water is formed as a bulky sludge substance. Even if the waste liquid containing the emulsion, which is a bulky sludge-like substance, is to be treated by gravity sedimentation, the emulsion is hardly reduced only by standing, so that the cleaning liquid that can be regenerated and reused is extremely small. In addition, when the filtration operation is performed to separate the emulsion from the cleaning liquid and water, not only the ink pigment but also the emulsion is filtered as a solid content on the filter, and the sludge emulsion immediately causes the filter to be clogged. It takes a lot of labor and time to filter the waste liquid.
In addition, in order to discard the filtered emulsion, it must be treated as industrial waste, and there is a problem that processing costs are incurred.

本発明は、このような事情に鑑みてなされたものであって、印刷機で使用したインキ顔料、水、洗浄液を含む洗浄廃液を単一の装置で容易に分離することのできる印刷機の廃液再生方法及び廃液再生装置を提供することを目的とする。   The present invention has been made in view of such circumstances, and the waste liquid of a printing press that can easily separate the cleaning waste liquid containing ink pigment, water, and cleaning liquid used in the printing press with a single device. An object of the present invention is to provide a recycling method and a waste liquid recycling apparatus.

上記課題を解決するために、本発明の廃液再生方法及び廃液再生装置は、以下の手段を採用する。
本発明の印刷機の廃液再生方法は、インキ顔料、有機系洗浄液、及び水を含む廃液を、再生容器を有する再生装置に投入して再生する廃液再生方法であって、前記再生容器において前記廃液を、重力沈降を利用して再生洗浄液、インキ顔料、及び水に分離する分離工程を有し、前記分離工程より前に、水と洗浄液から主としてなるエマルションを破壊しかつインキ顔料粒子を凝集させるエマルション処理剤を前記廃液に添加するエマルション処理剤添加工程を有することを特徴とする。
上記本発明の印刷機の廃液再生方法では、インキ顔料、有機系洗浄液、及び水の3成分が混在した系を単一の装置で分離するために、エマルションを破壊する機能とインキ顔料を凝集させる機能を少なくとも有する物質(以後、「エマルション処理剤」と記す)を洗浄廃液に添加して重力沈降法で処理する。このエマルション処理剤の添加により、上記3成分を含む廃液が強く攪拌された場合に生じる洗浄液成分と水から主としてなるエマルションが凝集した嵩高いヘドロ状物質の容積を1/5以下、好ましくは1/10以下に減容できるため、廃液の攪拌状態に関わらず重力沈降法によりインキ顔料、洗浄剤、水の3成分を速やか且つ効率よく分離することが可能となる。インク顔料は、下部の水相と上部の洗浄剤相の界面に堆積する。インキ中では顔料粒子は1μm以下程度まで微細に分散されているが、前記界面に堆積したインク顔料は、エマルション処理剤の効果により凝集粒子となっているため、濾過で容易に分離できる。
In order to solve the above problems, the waste liquid recycling method and the waste liquid recycling apparatus of the present invention employ the following means.
The waste liquid recycling method for a printing press according to the present invention is a waste liquid recycling method for recycling a waste liquid containing an ink pigment, an organic cleaning liquid, and water into a recycling apparatus having a recycling container, wherein the waste liquid is contained in the recycling container. Has a separation step of separating the regenerated washing liquid, ink pigment, and water using gravity sedimentation, and before the separation step, destroys the emulsion mainly composed of water and the washing liquid and agglomerates the ink pigment particles. It has the emulsion processing agent addition process which adds a processing agent to the said waste liquid, It is characterized by the above-mentioned.
In the waste liquid recycling method for a printing press according to the present invention, the ink pigment is agglomerated with the function of breaking the emulsion in order to separate the system containing the three components of the ink pigment, the organic cleaning liquid, and water with a single device. A substance having at least a function (hereinafter referred to as “emulsion treating agent”) is added to the washing waste liquid and treated by gravity sedimentation. By adding this emulsion treatment agent, the volume of the bulky sludge substance in which the emulsion mainly composed of the cleaning liquid component and water produced when the waste liquid containing the above three components is vigorously stirred is reduced to 1/5 or less, preferably 1 / Since the volume can be reduced to 10 or less, it is possible to quickly and efficiently separate the three components of the ink pigment, the cleaning agent, and water by the gravity sedimentation method regardless of the stirring state of the waste liquid. The ink pigment is deposited at the interface between the lower aqueous phase and the upper detergent phase. In the ink, the pigment particles are finely dispersed to about 1 μm or less, but the ink pigment deposited on the interface is agglomerated particles due to the effect of the emulsion treating agent and can be easily separated by filtration.

前記エマルション処理剤は、非イオン性界面活性剤を主成分とするものが好ましい。
界面活性剤は構造的には一定の大きさの親水基と疎水基を分子内に併せ持つが、親水基が水中でイオン解離しない非イオン性界面活性剤、水中でイオン解離して界面活性剤がプラス帯電するカチオン界面活性剤、マイナス帯電するアニオン界面活性剤があり、カチオン活性剤とアニオン活性剤は自身が帯電する際には、自身の帯電特性と逆の帯電特性のイオン(カウンターイオン)を水中に放出する。
本発明のエマルション処理剤は、エマルションを破壊すると同時に顔料粒子を凝集させる作用を発現することが求められる。インキは油性インキであるため、顔料は油性インキとの親和性が高い表面、すなわち疎水性であるのが一般的である。イオン性界面活性剤はイオン性が強いため親水性が強く、疎水性顔料表面へ吸着しにくく、その点でイオン解離しない非イオン性界面活性剤が好ましい。
The emulsion treatment agent preferably contains a nonionic surfactant as a main component.
A surfactant structurally has both a hydrophilic group and a hydrophobic group of a certain size in the molecule, but the hydrophilic group is a nonionic surfactant that does not ionically dissociate in water. There are positively charged cationic surfactants and negatively charged anionic surfactants. When the cationic and anionic surfactants are charged by themselves, they have ions (counter ions) with opposite charging characteristics to their own charging characteristics. Release into water.
The emulsion treating agent of the present invention is required to exhibit an action of aggregating pigment particles at the same time as breaking the emulsion. Since the ink is an oil-based ink, the pigment is generally a surface having high affinity with the oil-based ink, that is, hydrophobic. The ionic surfactant is preferably a nonionic surfactant that is strong in ionicity and strong in hydrophilicity, hardly adsorbed on the surface of the hydrophobic pigment and does not dissociate in that respect.

前記非イオン性界面活性剤は、ポリオキシエチレン鎖を構造の一部として有する共重合体であり、HLBが10以下のものが好ましい。
エチレンオキサイドCHCHOを付加重合させて得られるポリオキシエチレン鎖(CHCHO)は親水基として機能し、このポリオキシエチレン鎖を構造の一部として有する非イオン性界面活性剤は、疎水基の種類やアルキレンオキサイドの付加モル数を変えることによって、目的の物性を持つ界面活性剤とすることが可能になる。
親水性と疎水性の強さのバランスを数値として表したものがHLB(Hydrophile − Lipophile Balance)で、非イオン界面活性剤の基本物性を表す代表的な指標である。親水基を全く持たない界面活性剤はHLB=0、またポリエチレングリコールのように親水基のものものはHLB=20となるので、非イオン性界面面活性剤のHLB範囲は0〜20となる。このHLB値は、数字が小さいほど疎水性が強く、大きいほど親水性が強いことを意味する。
The nonionic surfactant is a copolymer having a polyoxyethylene chain as a part of the structure, and preferably has an HLB of 10 or less.
Polyoxyethylene chain (CH 2 CH 2 O) n obtained by addition polymerization of ethylene oxide CH 2 CH 2 O functions as a hydrophilic group, and is a nonionic surfactant having this polyoxyethylene chain as part of the structure The agent can be made into a surfactant having the desired physical properties by changing the kind of hydrophobic group or the number of added moles of alkylene oxide.
A balance between hydrophilicity and hydrophobicity expressed as a numerical value is HLB (Hydrophile-Lipophile Balance), which is a representative index representing the basic physical properties of a nonionic surfactant. A surfactant having no hydrophilic group has HLB = 0, and a surfactant having a hydrophilic group such as polyethylene glycol has HLB = 20. Therefore, the HLB range of the nonionic surfactant is 0-20. This HLB value means that the smaller the number, the stronger the hydrophobicity, and the larger the number, the stronger the hydrophilicity.

インキ顔料、有機系洗浄液、及び水の3成分を含む廃液が強く攪拌された場合には、洗浄液成分と水から主としてなるエマルションが凝集した嵩高いヘドロ状物質が生じる。エマルションにはO/W型とW/O型があるが、インキの種類や洗浄液の種類の組み合わせが変わっても、常にO/W型かW/O型のどちらか一方のエマルションが形成されるか確認できていないが、HLBが10以下、好ましくは8以下の非イオン性界面活性剤を主成分とするエマルション処理剤を添加することで、前記へドロの発生を抑制できる、あるいは発生したヘドロの容積を1/5以下、好ましくは1/10以下まで減少できることを実験的に見出した。しかし、印刷機で使用されているインキの種類や洗浄液の種類にほとんど影響されること無く、本発明のエマルション処理剤が有効である理由は明確ではないが、現時点では以下のような仮説を立てている。   When the waste liquid containing the ink pigment, the organic cleaning liquid, and the three components of water is vigorously stirred, a bulky sludge substance in which an emulsion mainly composed of the cleaning liquid component and water is aggregated is generated. There are O / W type and W / O type emulsions, but either O / W type or W / O type emulsion is always formed even if the combination of ink type and cleaning liquid type changes. Although it has not been confirmed, by adding an emulsion treatment agent mainly composed of a nonionic surfactant having an HLB of 10 or less, preferably 8 or less, the generation of the sludge can be suppressed or generated. It has been experimentally found that the volume of can be reduced to 1/5 or less, preferably 1/10 or less. However, the reason for the effectiveness of the emulsion treatment agent of the present invention is not clear because it is hardly affected by the type of ink used in the printing press or the type of cleaning liquid. ing.

インキ中に含有されている界面活性物資が廃液中のエマルションを安定化させていると推定されるが、この界面活性物質がHLBを有するとすれば、おそらく中程度ないし高めのHLB値を持つために、HLBが10以下、好ましくは8以下のような低めのHLB値を持つエマルション処理剤の添加により、前記エマルションの不安定化ないしエマルションの破壊を引き起こし、エマルション発生防止、ないし発生したエマルションの減容が可能になると推定する。
また、前記のように、疎水性である顔料粒子表面に吸着しやすいという観点からも、HLBが10以下、好ましくは8以下のような低めのHLB値を持つエマルション処理剤が適する。
It is presumed that the surface-active substances contained in the ink stabilize the emulsion in the waste liquid, but if this surface-active substance has HLB, it probably has a medium to high HLB value. In addition, the addition of an emulsion treatment agent having a low HLB value such as an HLB of 10 or less, preferably 8 or less causes the emulsion to become unstable or break the emulsion, thereby preventing the occurrence of emulsion or reducing the generated emulsion. Estimate that it will be possible.
Also, as described above, an emulsion treatment agent having a low HLB value such as HLB of 10 or less, preferably 8 or less is suitable from the viewpoint of being easily adsorbed on the surface of hydrophobic pigment particles.

前記非イオン性界面活性剤の質量平均分子量(Mw;以下、単に「平均分子量」と呼ぶ)は、1200以上であることが好ましい。
本発明の再生方式では、エマルション処理剤を添加した後、重力沈降方式で、再生洗浄液と再生水に分離するが、微細なインキ顔料は再生水層表面に堆積させて、再生洗浄液とインキ顔料成分を分離する。この顔料粒子が微細なままであると、その後の濾過などの方法によって、洗浄液、顔料、を分離する際に時間が掛かってしまう。
しかしながら、平均分子量が1200以上の非イオン性界面活性剤を主成分とするエマルション処理剤には、エマルション発生防止あるいはエマルション減容化すると同時に、インキ顔料成分を凝集させて粗大化させる凝集剤としての機能があることを実験的に見出した。
The nonionic surfactant preferably has a mass average molecular weight (Mw; hereinafter simply referred to as “average molecular weight”) of 1200 or more.
In the regeneration method of the present invention, after the emulsion treatment agent is added, it is separated into the regenerated cleaning liquid and the reclaimed water by the gravity sedimentation method, but the fine ink pigment is deposited on the surface of the regenerated water layer to separate the regenerated cleaning liquid and the ink pigment component. To do. If the pigment particles remain fine, it takes time to separate the cleaning liquid and the pigment by a method such as subsequent filtration.
However, the emulsion treatment agent mainly composed of a nonionic surfactant having an average molecular weight of 1200 or more is a flocculant that aggregates and coarsens the ink pigment component at the same time as preventing emulsion generation or reducing the emulsion volume. Experimentally found that there is a function.

イオン性の界面活性剤の場合であれば、分子量がより小さくても、顔料の帯電特性の反対電荷(活性剤とそのカウンターイオンが電荷を持った状態で存在するため、顔料粒子がプラスまたはマイナスのどちらに帯電していても、活性剤とそのカウンターイオンのどちらかは、必ず顔料粒子と静電気的に引き合うことになる)が帯電した顔料表面に吸着して顔料粒子の電荷をキャンセルし、静電気的反発を無くすことで顔料粒子を凝集させることが可能である。しかし、本発明のエマルション処理剤は非イオン界面活性剤であるため、静電気的反発力の中和による凝集作用は発現できない。
非イオン性界面活性剤による顔料微粒子の凝集では、1つの非イオン性界面活性剤分子が複数の顔料微粒子に吸着して、それらの顔料粒子を絡め取るようにして凝集粒子を形成するため、非イオン性界面活性剤の分子鎖には、ある程度の長さが必要である。その必要な長さを確保するためには平均分子量が1200以上必要であることを実験的に見出したものである。
非イオン性界面活性剤による顔料微粒子の凝集により、濾過速度はエマルション処理剤未添加の場合の10倍以上に速くなる。濾過により顔料粒子を除去した洗浄廃液は有機系洗浄剤と水の比重差により、10〜15分で速やかに分離し、再生洗浄液を透明のクリーンな液として回収できる。
In the case of an ionic surfactant, even if the molecular weight is smaller, the charge opposite to the charging characteristics of the pigment (the activator and its counter ion are present in a charged state, so the pigment particles are positive or negative) The active agent and its counter ion must be electrostatically attracted to the pigment particles, regardless of whether they are charged.) It is possible to agglomerate the pigment particles by eliminating the repulsion. However, since the emulsion treatment agent of the present invention is a nonionic surfactant, it cannot exhibit an aggregating effect due to neutralization of electrostatic repulsion.
In the aggregation of pigment fine particles by a nonionic surfactant, one nonionic surfactant molecule is adsorbed on a plurality of pigment fine particles, and these pigment particles are entangled to form aggregated particles. The molecular chain of the ionic surfactant needs to have a certain length. It has been experimentally found that an average molecular weight of 1200 or more is necessary to ensure the necessary length.
Due to the aggregation of the pigment fine particles by the nonionic surfactant, the filtration rate becomes 10 times faster than when the emulsion treatment agent is not added. The washing waste liquid from which the pigment particles have been removed by filtration is quickly separated in 10 to 15 minutes due to the difference in specific gravity between the organic detergent and water, and the regenerated washing liquid can be recovered as a transparent clean liquid.

このような非イオン性界面活性剤としては、三洋化成工業株式会社のポリオキシエチレン・ポリオキシプロピレン・ブロックコポリマーであるニューポールPE−61(HLB 1.8〜2.0、ポリオキシプロピレン部分の平均分子量1,750)、ニューポールPE−62(HLB 4.0〜4.3、ポリオキシプロピレン部分の平均分子量1,750)、第一工業製薬株式会社のポリオキシエチレンラウリルエーテルであるDSK NL−15(HLB 5.0、ポリオキシエチレン部分の平均分子量2,900)、DSK NL−30(HLB 8.1、ポリオキシエチレン部分の平均分子量5,800)、ポリオキシエチレンオレイルセチルエーテルであるノイゲンET−69型(HLB 5.7、ポリオキシエチレン部分の平均分子量4,440)、ノイゲンET−89型(HLB 7.9、ポリオキシエチレン部分の平均分子量7,170)、ポリアルキレンポリアミン・プロピレンオキサイドーエチレンオキサイド付加物であるディスコール206(HLB 6.0 、平均分子量93,000)、ポリオキシエチレン・ラウリルエーテルであるノイゲンET−83(HLB 6.4、ポリオキシエチレン部分の平均分子量3,870)、ポリオキシエチレン・ポリオキシプロピレンのブロックポリマーであるエパン410(HLB 6.0、疎水基の分子量1,200・・・これに親水基の分子量が加わったものが活性剤の分子量)などがあるが、これらに限るものではない。   As such a nonionic surfactant, New Pole PE-61 (HLB 1.8-2.0, polyoxypropylene part) which is a polyoxyethylene-polyoxypropylene block copolymer of Sanyo Chemical Industries, Ltd. Average molecular weight 1,750), Newpol PE-62 (HLB 4.0-4.3, average molecular weight 1,750 of polyoxypropylene part), DSK NL which is polyoxyethylene lauryl ether of Daiichi Kogyo Seiyaku Co., Ltd. -15 (HLB 5.0, average molecular weight of polyoxyethylene part 2,900), DSK NL-30 (HLB 8.1, average molecular weight of polyoxyethylene part 5,800), polyoxyethylene oleyl cetyl ether Neugen ET-69 type (HLB 5.7, average molecule of polyoxyethylene moiety) 4,440), Neugen ET-89 type (HLB 7.9, average molecular weight 7,170 of polyoxyethylene part), polyalkylene polyamine / propylene oxide / ethylene oxide adduct 206 (HLB 6.0, Average molecular weight 93,000), polyoxyethylene lauryl ether Neugen ET-83 (HLB 6.4, polyoxyethylene part average molecular weight 3,870), polyoxyethylene polyoxypropylene block polymer Epan 410 (HLB 6.0, molecular weight of hydrophobic group 1,200..., The molecular weight of the active agent is obtained by adding the molecular weight of the hydrophilic group), but is not limited thereto.

前記エマルション処理剤添加工程は、前記分離工程までに前記エマルション処理剤の有効成分が前記廃液全体に対して0.05質量%以上5質量%になるように、前記エマルション処理剤を前記廃液に添加する工程とすることが好ましい。
本発明のエマルション処理剤を廃液に添加し攪拌した後に、静置すると、嵩高いへドロは減容し、上部が洗浄液層、中央部が減容したヘドロ層(このヘドロ層にインキ顔料成分が含まれる。エマルション処理剤の効果が十分なときは、ヘドロ層は消失しインキ顔料微粒子の堆積層となる)下部が水層の3層に分離するが、前記3成分(有機系洗浄液、インキ顔料、及び水)の分離時間は、エマルション処理剤濃度と相関性があり、基本的には添加濃度が高いほうが処理時間は短縮される。廃液によって多少の差はあるが、十分なヘドロ減容効果を得るためには、エマルション処理剤の添加量を少なくとも0.05質量%とする必要がある。
一方、エマルション処理剤の添加量が5質量%を超えると、エマルション処理剤処理費用アップや、さらに洗浄廃液を強攪拌した場合に、エマルション処理剤自体によって水層の中に洗浄剤が再乳化する場合があり、好ましくない。
In the emulsion treatment agent addition step, the emulsion treatment agent is added to the waste liquid so that the active ingredient of the emulsion treatment agent is 0.05% by mass or more and 5% by mass with respect to the whole waste liquid by the separation step. It is preferable to set it as the process to carry out.
When the emulsion treatment agent of the present invention is added to the waste liquid and stirred and then allowed to stand, the bulky sludge is reduced, the upper part is the washing liquid layer, and the middle part is the sludge layer (the ink pigment component is contained in this sludge layer). When the effect of the emulsion treating agent is sufficient, the sludge layer disappears and becomes a layer of ink pigment fine particles) The lower part is separated into three layers of an aqueous layer, but the above three components (organic cleaning liquid, ink pigment) , And water) have a correlation with the emulsion treatment agent concentration. Basically, the higher the addition concentration, the shorter the treatment time. Although there are some differences depending on the waste liquid, the addition amount of the emulsion treatment agent needs to be at least 0.05% by mass in order to obtain a sufficient sludge reduction effect.
On the other hand, when the addition amount of the emulsion treatment agent exceeds 5% by mass, the treatment agent is re-emulsified in the aqueous layer by the emulsion treatment agent itself when the treatment cost of the emulsion treatment agent is increased and the washing waste liquid is vigorously stirred. In some cases, it is not preferable.

なお、本発明のエマルション処理剤は低めのHLBを持つから、有機溶剤への溶解性があり、再生洗浄液中にも溶解しているため、再生洗浄液を使用してブランケット洗浄を行った後の廃液再生の際には、新たにエマルション処理剤を廃液に対して0.05質量%〜5質量%加える必要はないことは言うまでも無い。そのような場合は、前期適正濃度範囲以下になった場合に、不足分を補充すれば良い。
なおエマルション処理剤の廃液中の濃度管理方式としては、再生処理前の廃液中あるいは再生後の再生洗浄液中のエマルション処理剤濃度をモニターし、最適濃度範囲を下回りそうになったら補充する方式が好ましい。濃度モニターの方法としては、一定時間毎に化学分析する方法、一定時間または連続的に再生洗浄液の電気伝導率を測定する方法などがあるが、これに限るものではない。
最も簡素な濃度管理方法としては、最適濃度範囲になるようにエマルション処理剤を添加したブランケット洗浄液を最初から使用し、ブランケット洗浄液を補充する場合も、最適濃度範囲になるようにエマルション処理剤を添加したブランケット洗浄液を補充すればよい。
In addition, since the emulsion treating agent of the present invention has a low HLB, it is soluble in an organic solvent and is also dissolved in the regenerated cleaning liquid, so that the waste liquid after blanket cleaning is performed using the regenerated cleaning liquid. Needless to say, at the time of regeneration, it is not necessary to newly add 0.05 mass% to 5 mass% of the emulsion treatment agent to the waste liquid. In such a case, the deficiency may be replenished when the concentration falls below the appropriate concentration range in the previous period.
As the concentration control method in the waste liquid of the emulsion treatment agent, a method of monitoring the concentration of the emulsion treatment agent in the waste liquid before the regeneration treatment or in the regenerated cleaning liquid after the regeneration, and replenishing when it is likely to be below the optimum concentration range is preferable. . Examples of the concentration monitoring method include, but are not limited to, a method in which chemical analysis is performed at regular time intervals, and a method in which the electrical conductivity of the regenerated cleaning liquid is measured for a certain time or continuously.
The simplest concentration control method is to use a blanket cleaning solution with an emulsion treatment agent added to the optimum concentration range from the beginning, and when replenishing the blanket cleaning solution, add the emulsion treatment agent to the optimum concentration range. What is necessary is just to replenish the blanket washing liquid which was made.

本発明のエマルション処理液の添加方法としては、廃液にエマルション処理剤を添加した後、適度に攪拌し、廃液処理装置の重力沈降式の廃液再生容器で静置し分離処理すればよい。すなわち、上記本発明の印刷機の廃液再生方法は、印刷機から排出された前記廃液を前記再生装置に投入するまで該廃液を保管容器中に保管しておく保管工程を有し、該保管工程中において、前記エマルション処理剤添加工程を行い、前記廃液及び前記エマルション処理剤を含む液を攪拌し、前記保管工程の後に、前記再生装置において前記分離工程を行うこととしてもよい。あるいは、上記本発明の印刷機の廃液再生方法は、印刷機から排出された前記廃液を前記再生装置に投入するまで該廃液を保管容器中に保管しておく保管工程を有し、前記保管工程と前記分離工程との間において、前記保管容器と前記再生容器との間に設けられた廃液流路のいずこかで前記エマルション処理剤を前記廃液に添加し、前記廃液及び前記エマルション処理剤を含む液をそれ自身の流れで攪拌することにより前記エマルション処理剤添加工程を行うこととしてもよい。
従って、エマルション処理剤は、印刷機から排出された前記廃液を再生装置に投入するまで保管しておく保管容器中の廃液に添加してもよく、また、廃液貯留容器から廃液再生容器内の重力沈降層の間の廃液流路のどこかで、廃液に添加しても良い。
As an addition method of the emulsion treatment liquid of the present invention, an emulsion treatment agent may be added to the waste liquid, and then stirred appropriately, and left in a gravity sedimentation type waste liquid regeneration container of a waste liquid treatment apparatus for separation treatment. That is, the above-mentioned waste liquid recycling method for a printing press according to the present invention includes a storage step of storing the waste liquid in a storage container until the waste liquid discharged from the printing press is put into the recycling apparatus. It is good also as performing the said emulsion process agent addition process, stirring the liquid containing the said waste liquid and the said emulsion process agent, and performing the said isolation | separation process in the said reproducing | regenerating apparatus after the said storage process. Alternatively, the waste liquid recycling method for a printing press according to the present invention includes a storage step of storing the waste liquid in a storage container until the waste liquid discharged from the printing press is put into the recycling apparatus, and the storage step And the separation step, the emulsion treatment agent is added to the waste liquid at some point in the waste liquid flow path provided between the storage container and the regeneration container, and the waste liquid and the emulsion treatment agent are added. It is good also as performing the said emulsion processing agent addition process by stirring the liquid containing this by an own flow.
Therefore, the emulsion treatment agent may be added to the waste liquid in the storage container that stores the waste liquid discharged from the printing press until it is put into the regenerator, and the gravity of the waste liquid regeneration container from the waste liquid storage container may be added. It may be added to the waste liquid somewhere in the waste liquid flow path between the sedimentation layers.

あるいは、印刷機から排出される洗浄廃液の受け入れ槽に本発明のエマルション処理剤を添加しても良い。すなわち、上記本発明の印刷機の廃液再生方法において、前記エマルション処理剤添加工程は、前記エマルション処理剤を、印刷機から排出される廃液を受け入れる廃液受け入れ槽に添加する工程であってもよい。
この廃液受け入れ槽は、各印刷ユニット毎に設けられた廃液受け入れ槽でもよく、また各印刷ユニットから排出される洗浄廃液を集合して受け入れる廃液受け入れ槽でもよい。さらにまた、廃液受け入れ槽内の洗浄廃液は強く攪拌されるような状況でもよく、逆に攪拌はほとんどない(廃液がタンク内に液が流入することによる液の流動程度を指す)ような状況でも、差し支えない。
Or you may add the emulsion processing agent of this invention to the receiving tank of the washing | cleaning waste liquid discharged | emitted from a printing press. That is, in the waste liquid recycling method for a printing press according to the present invention, the emulsion treatment agent adding step may be a step of adding the emulsion treatment agent to a waste liquid receiving tank that receives the waste liquid discharged from the printing press.
The waste liquid receiving tank may be a waste liquid receiving tank provided for each printing unit, or may be a waste liquid receiving tank that collects and receives cleaning waste liquid discharged from each printing unit. Furthermore, the cleaning waste liquid in the waste liquid receiving tank may be agitated strongly, and conversely there is almost no agitation (refers to the degree of fluid flow caused by the liquid flowing into the tank). It ’s okay.

本発明の廃液再生装置は、インキ顔料、有機系洗浄剤、及び水を含む廃液を再生する廃液再生装置であって、前記廃液を一定時間滞留させ該廃液を重力沈降によって再生洗浄液、インキ顔料、及び水に分離する再生容器と、前記再生容器に隣接して設けられ、該再生容器内で分離された再生洗浄液を回収する再生液貯留容器と、前記再生容器に隣接して設けられ、該再生容器内で分離された再生水を回収する回収水貯留容器と、前記再生容器の下方に設けられ、内部にインキ顔料回収フィルタを備えた濾過器と、該濾過器からの濾液を重力沈降によって再生洗浄液と水に分離する濾液分離容器とを有する装置とすることができる。   The waste liquid regenerating apparatus of the present invention is a waste liquid regenerating apparatus for regenerating a waste liquid containing an ink pigment, an organic cleaning agent, and water, and the waste liquid is retained for a certain period of time to regenerate the cleaning liquid, ink pigment, And a regeneration container that is separated into water, a regeneration liquid storage container that is provided adjacent to the regeneration container and collects the regeneration cleaning liquid separated in the regeneration container, and that is disposed adjacent to the regeneration container, the regeneration container A recovered water storage container for recovering the reclaimed water separated in the container, a filter provided below the regenerator, and provided with an ink pigment recovery filter therein, and the filtrate from the filter is regenerated and washed by gravity sedimentation. And a filtrate separation container that separates into water.

この廃液再生装置を用いれば、バッチ方式又は連続方式により印刷機の廃液再生方法を行うことができる。バッチ方式によりインキ顔料、有機系洗浄剤、及び水を含む廃液を再生する廃液再生方法では、前記廃液を前記廃液再生装置に投入する工程と、前記廃液再生装置を用いて前記廃液を再生洗浄液、インキ顔料、及び水に分離する工程とが、バッチ方式で行われる。   If this waste liquid recycling apparatus is used, a waste liquid recycling method for a printing press can be performed by a batch system or a continuous system. In a waste liquid regeneration method for regenerating a waste liquid containing an ink pigment, an organic cleaning agent, and water by a batch method, a step of charging the waste liquid into the waste liquid regeneration apparatus, and a regeneration cleaning liquid for regenerating the waste liquid using the waste liquid regeneration apparatus, The process of separating into ink pigment and water is performed in a batch mode.

連続方式によりインキ顔料、有機系洗浄剤、及び水を含む廃液を再生する廃液再生方法では、前記廃液を前記廃液再生装置に供給する工程と、前記廃液再生装置を用いて前記廃液を再生洗浄液、インキ顔料、及び水に分離する工程とが、連続方式で同時に行われる。   In a waste liquid regeneration method for regenerating a waste liquid containing an ink pigment, an organic cleaning agent, and water by a continuous method, a step of supplying the waste liquid to the waste liquid regenerator, and a regeneration cleaning liquid for regenerating the waste liquid using the waste liquid regenerator, The step of separating the ink pigment and water is performed simultaneously in a continuous manner.

本発明によれば、インキ顔料、有機系洗浄液、及び水の3成分が混在した印刷機の洗浄廃液を単一の装置で容易に分離することができる。すなわち、エマルションを破壊する機能とインキ顔料を凝集させる機能を少なくとも有する物質(以後、エマルション処理剤と記す)を前記洗浄廃液に添加することで、上記3成分を含む洗浄廃液が強く攪拌された場合に生じる洗浄液成分と水から主としてなるエマルションが凝集した嵩高いヘドロ状物質の発生を防止する、あるいは発生した嵩高いヘドロの容積を1/5以下、好ましくは1/10以下に減容できるため、廃液の攪拌状態に関わらず重力沈降法により上部が洗浄液層、下部が水層で洗浄液と水の界面のインキ顔料層の3成分として速やか且つ効率よく分離することが可能となる。   According to the present invention, it is possible to easily separate a cleaning waste liquid of a printing press in which three components of an ink pigment, an organic cleaning liquid, and water are mixed with a single device. That is, when the cleaning waste liquid containing the above three components is vigorously stirred by adding to the cleaning waste liquid a substance having at least a function of breaking the emulsion and aggregating the ink pigment (hereinafter referred to as an emulsion treatment agent). In order to prevent the generation of a bulky sludge substance in which an emulsion mainly composed of a cleaning liquid component and water is aggregated, or to reduce the volume of the bulky sludge generated to 1/5 or less, preferably 1/10 or less, Regardless of the agitation state of the waste liquid, it is possible to quickly and efficiently separate the three components of the ink pigment layer at the interface between the cleaning liquid and water with the upper part being the washing liquid layer and the lower part being the water layer by the gravity settling method.

さらに、印刷機の洗浄廃液の静置により上部が洗浄液層、下部が水層で洗浄液と水の界面のインキ顔料層の3成分として分離した廃液から顔料を取り除くために濾過する場合も、本発明のエマルション処理剤を洗浄廃液に添加することで、微粒子状態で存在しているインキ顔料粒子が凝集して粗大化し、濾過が極めて容易になるため、処理速度の向上が可能となる。   Furthermore, the present invention also applies to the case where filtration is performed in order to remove the pigment from the waste liquid separated as the three components of the ink pigment layer at the interface between the cleaning liquid and the water, with the upper part being the cleaning liquid layer and the lower part being the water layer by leaving the cleaning waste liquid of the printing press By adding this emulsion treatment agent to the washing waste liquid, the ink pigment particles present in the fine particle state are aggregated and coarsened, and filtration becomes extremely easy, so that the treatment speed can be improved.

以下、図面および実施例により、本発明の実施の形態について説明する。
[廃液再生装置]
図1は本発明の廃液再生装置を示すもので、図1はその廃液再生装置の側面方向から見た模式的な断面図である。
図1に示すように、この廃液再生装置1には、廃液を一定時間滞留させ該廃液を重力沈降によって再生洗浄液3と水2に分離する廃液再生容器5と、該廃液再生容器5内で分離された再生洗浄液である再生液を回収する再生洗浄液貯留容器6と、該廃液再生容器内で分離された再生水を回収する回収水貯留容器7と、該廃液再生容器の下方に配置され、内部にインキ顔料回収フィルタ8を備えた濾過タンク(濾過器及び濾液分離容器)9とが備えられている。
Hereinafter, embodiments of the present invention will be described with reference to the drawings and examples.
[Waste liquid recycling equipment]
FIG. 1 shows a waste liquid regenerating apparatus according to the present invention, and FIG. 1 is a schematic cross-sectional view of the waste liquid regenerating apparatus as viewed from the side.
As shown in FIG. 1, the waste liquid regeneration apparatus 1 includes a waste liquid regeneration container 5 that retains the waste liquid for a certain period of time and separates the waste liquid into a regenerated cleaning liquid 3 and water 2 by gravity sedimentation, and the waste liquid regeneration container 5 separates the waste liquid in the waste liquid regeneration container 5. The regenerated cleaning liquid storage container 6 for recovering the regenerated liquid that is the regenerated cleaning liquid, the recovered water storage container 7 for recovering the reclaimed water separated in the waste liquid regenerating container, and disposed below the waste liquid regenerating container, A filtration tank (filter and filtrate separation container) 9 provided with an ink pigment recovery filter 8 is provided.

まず、本発明の廃液再生装置1をバッチ方式で用いる場合について説明する。
廃液再生容器5の側部に設けられ、この廃液再生容器5とこれに隣接する回収水貯留容器7との間の流路を開閉する開閉弁11、及び廃液再生容器5の底部に設けられた開閉弁12を閉じ、廃液再生容器5に廃液を投入する廃液投入管13に設けられた開閉弁14を開いた後、この廃液投入管13からエマルション処理剤が添加された洗浄廃液15を廃液再生容器5内に送り込む。廃液再生容器5と再生液貯留容器6の間の壁16を洗浄廃液15がオーバーフローして、廃液再生容器5に隣接する再生液貯留容器6や回収水貯留容器7に流れ込む前に洗浄廃液15の送液を止めて、廃液投入管13に設けられた開閉弁14を閉じる。
その後、廃液再生容器5内で洗浄廃液15を静置することにより、洗浄廃液15は再生洗浄液3、インキ顔料4、及び水2に分離する。図1には、再生洗浄液3、インキ顔料4、及び水2が分離された状態を示している。
First, the case where the waste liquid recycling apparatus 1 of the present invention is used in a batch system will be described.
An opening / closing valve 11 provided at the side of the waste liquid regeneration container 5 for opening and closing the flow path between the waste liquid regeneration container 5 and the recovered water storage container 7 adjacent thereto, and provided at the bottom of the waste liquid regeneration container 5 After closing the on-off valve 12 and opening the on-off valve 14 provided in the waste liquid input pipe 13 for introducing the waste liquid into the waste liquid regeneration container 5, the cleaning waste liquid 15 to which the emulsion treating agent has been added is recycled from the waste liquid input pipe 13. Feed into container 5. The cleaning waste liquid 15 overflows the wall 16 between the waste liquid regeneration container 5 and the regeneration liquid storage container 6 and flows into the regeneration liquid storage container 6 and the recovered water storage container 7 adjacent to the waste liquid regeneration container 5. The liquid feeding is stopped and the on-off valve 14 provided in the waste liquid input pipe 13 is closed.
Thereafter, the cleaning waste liquid 15 is allowed to stand in the waste liquid regeneration container 5, whereby the cleaning waste liquid 15 is separated into the regeneration cleaning liquid 3, the ink pigment 4, and the water 2. FIG. 1 shows a state in which the regenerated cleaning liquid 3, the ink pigment 4, and the water 2 are separated.

分離に要する時間はエマルション処理剤添加量と相関するため、処理時間を短くしたい時は、適正添加量の範囲でエマルション処理剤の添加量を増加させればよい。大まかな目安としては、ヘドロ状物質がある場合でも廃液に対するエマルション処理剤濃度0.2質量%となるように添加して数時間静置すれば分離できる場合が多い。しかし、洗浄液及びインキの種類によって差はあるため、夫々のケースについて、処理時間との関係でエマルション処理剤の添加量を決めればよい。エマルション処理剤を添加しなければ、ヘドロ状物質がある場合は廃液を廃液再生容器5内で一晩静止しても分離できないことは言うまでもない。   Since the time required for the separation correlates with the addition amount of the emulsion treatment agent, when it is desired to shorten the treatment time, the addition amount of the emulsion treatment agent may be increased within the range of the appropriate addition amount. As a rough guide, even if there is a sludge-like substance, it can often be separated by adding it to a concentration of 0.2% by mass of the emulsion treatment agent relative to the waste liquid and allowing it to stand for several hours. However, since there are differences depending on the types of cleaning liquid and ink, the amount of the emulsion treatment agent to be added may be determined in relation to the processing time in each case. Needless to say, if the emulsion treatment agent is not added, if there is a sludge-like substance, the waste liquid cannot be separated even if it is left standing overnight in the waste liquid regeneration container 5.

再生洗浄液3、インキ顔料4、水2が分離されたら、廃液再生容器5の底部に設けられた開閉弁12を開き、濾過タンク9に分離した廃液を流し落とす。このとき、分離した3成分が再び混合してしまうことを避けるために、勢いよく流し落とすことは避けることが好ましい。分離した状態で流し落とされた廃液は、濾過タンク9内に設けられたフィルタ8によって濾過される。エマルション処理剤の顔料凝集作用でインキ顔料4は嵩高い凝集体18となっているため、インキ顔料4の凝集体18は濾過タンク9内のフィルタ8を目詰まりさせることなくフィルタ8上に濾し取られ、水2と再生洗浄液3は速やかに濾出されて濾過タンク9に貯蔵される。   When the regenerated cleaning liquid 3, the ink pigment 4, and the water 2 are separated, the on-off valve 12 provided at the bottom of the waste liquid regeneration container 5 is opened, and the separated waste liquid is poured into the filtration tank 9. At this time, in order to avoid the separated three components from being mixed again, it is preferable to avoid flushing away. The waste liquid that has been washed away in a separated state is filtered by a filter 8 provided in the filtration tank 9. Since the ink pigment 4 is a bulky aggregate 18 due to the pigment aggregation action of the emulsion treatment agent, the aggregate 18 of the ink pigment 4 is filtered on the filter 8 without clogging the filter 8 in the filtration tank 9. Then, the water 2 and the regenerated cleaning liquid 3 are quickly filtered out and stored in the filtration tank 9.

濾過後、濾過タンク9に貯蔵された水と再生洗浄液の界面が安定したら、濾過タンク9の下部に接続する抜き出し管20を開閉するための開閉弁21を開き、濾過タンク9の側壁の一部を構成する透明の覗き窓22から前記界面の位置を確認しながら、抜き出し管20から濾過タンク9に貯蔵された水を抜き出す。前記界面が抜き出し管20の開閉弁21に接近し、再生洗浄液が抜き出し管20に差し掛かったら、この開閉弁21を閉じる。抜き出し管20より抜き出され、回収された水は、必要によっては適切な処理をした後、廃棄すればよい。   After the filtration, when the interface between the water stored in the filtration tank 9 and the regenerated cleaning liquid is stabilized, the on-off valve 21 for opening and closing the extraction pipe 20 connected to the lower part of the filtration tank 9 is opened, and a part of the side wall of the filtration tank 9 is opened. The water stored in the filtration tank 9 is extracted from the extraction pipe 20 while confirming the position of the interface from the transparent observation window 22 constituting the structure. When the interface approaches the on-off valve 21 of the extraction pipe 20 and the regenerated cleaning liquid reaches the extraction pipe 20, the on-off valve 21 is closed. The water extracted and recovered from the extraction pipe 20 may be disposed of after appropriate processing if necessary.

次に抜き出し管20の開閉弁21を開いて、抜き出し管20から出てくる再生洗浄液を適当な容器(図示略)に移す。容器に移された再生洗浄液は、印刷機の洗浄に再利用すればよい。
上記のような濾過操作を何回か繰り返して、フィルタ8の濾過速度が遅くなってきた時点で、濾過タンク9からフィルタ8を取り外し、新しいフィルタ8と交換する、あるいはフィルタ8上に溜まったインキ顔料を除去した後、再び濾過タンク9にフィルタ8を取り付けるなどの対応をすれば良い。
上記の操作を終了したら、再び同じ操作を繰り返し、バッチ方式で洗浄廃液15の再生処理を繰り返せばよい。
Next, the on-off valve 21 of the extraction pipe 20 is opened, and the regenerated cleaning liquid coming out of the extraction pipe 20 is transferred to an appropriate container (not shown). The regenerated cleaning liquid transferred to the container may be reused for cleaning the printing press.
The filtration operation as described above is repeated several times, and when the filtration speed of the filter 8 becomes slow, the filter 8 is removed from the filtration tank 9 and replaced with a new filter 8 or ink accumulated on the filter 8. After removing the pigment, a countermeasure such as attaching the filter 8 to the filtration tank 9 again may be taken.
When the above operation is completed, the same operation is repeated again, and the regeneration process of the cleaning waste liquid 15 may be repeated in a batch manner.

次に、本発明の廃液再生装置1を連続方式で用いる場合について説明する。
廃液再生容器5の底部に設けられた開閉弁12及び廃液投入管13に設けられた開閉弁14を閉じ、廃液再生容器5と回収水貯留容器7との間の流路を開閉するように廃液再生容器5側部に設けられた開閉弁11と、再生洗浄液貯留容器6の下部に接続された再生洗浄液流出管25を開閉する開閉弁26と、回収水貯留容器7の側部に接続された回収水流出管28を開閉する開閉弁29とを開く。次に、回収水流出管28の入り口から水が多少流出するまで廃液再生容器5に水を蓄える。水は廃液再生容器5上部の蓋30を取って、上から入れてもよい。
Next, the case where the waste liquid recycling apparatus 1 of the present invention is used in a continuous manner will be described.
The on-off valve 12 provided at the bottom of the waste liquid regeneration container 5 and the on-off valve 14 provided on the waste liquid input pipe 13 are closed to open and close the flow path between the waste liquid regeneration container 5 and the recovered water storage container 7. An on-off valve 11 provided on the side of the regeneration container 5, an on-off valve 26 for opening / closing the regeneration cleaning liquid outflow pipe 25 connected to the lower part of the regeneration cleaning liquid storage container 6, and a side of the recovered water storage container 7. The on-off valve 29 that opens and closes the recovered water outflow pipe 28 is opened. Next, the water is stored in the waste liquid recycling container 5 until some water flows out from the inlet of the recovered water outflow pipe 28. The water may be put from above by removing the lid 30 on the upper part of the waste liquid regeneration container 5.

次に前記の水の上に洗浄液層を形成する。すなわち、廃液再生容器5と再生液貯留容器6の間の壁16を洗浄液がわずかにオーバーフローする程度まで、先に入れた水と混合しないように廃液再生容器5内に静かに洗浄液を注ぎこむ。この洗浄剤は新しいものでも良いが、再生した洗浄剤でもよい。
この後、廃液投入管13に設けられた開閉弁14を開き、廃液投入管1313からエマルション処理剤が添加された洗浄廃液15を廃液再生容器5内に徐々に送り込む。この時の洗浄廃液15の送液速度は、廃液再生容器5内部で洗浄廃液15が再生洗浄液3、インキ顔料4、水2の3成分に分離するのに必要な滞留時間となるような送液速度とする必要がある。廃液再生容器5内で滞留する間に、洗浄廃液15は再生洗浄液3、インキ顔料4、水2に分離する。再生洗浄液3は、廃液再生容器5と再生洗浄液貯留容器6の間の壁16をオーバーフローして再生洗浄液貯留溶液6に流れ込む。一方、水2は廃液再生容器5の側部に設けられた開閉弁11を通過して回収水貯留容器7に流れ込む。
Next, a cleaning liquid layer is formed on the water. That is, the cleaning solution is gently poured into the waste solution regeneration container 5 so that the wall 16 between the waste solution regeneration container 5 and the regeneration solution storage container 6 does not mix with the previously introduced water until the cleaning solution slightly overflows. This cleaning agent may be new or may be a regenerated cleaning agent.
Thereafter, the on-off valve 14 provided in the waste liquid input pipe 13 is opened, and the cleaning waste liquid 15 to which the emulsion treating agent is added is gradually fed into the waste liquid regeneration container 5 from the waste liquid input pipe 1313. At this time, the feeding speed of the cleaning waste liquid 15 is such that the cleaning waste liquid 15 has a residence time required for separating the cleaning waste liquid 15 into the three components of the regenerating cleaning liquid 3, the ink pigment 4, and the water 2 inside the waste liquid regeneration container 5. Need to be speed. While staying in the waste liquid regeneration container 5, the cleaning waste liquid 15 is separated into the regenerated cleaning liquid 3, the ink pigment 4, and the water 2. The regenerated cleaning liquid 3 overflows the wall 16 between the waste liquid regenerating container 5 and the regenerated cleaning liquid storage container 6 and flows into the regenerated cleaning liquid storage solution 6. On the other hand, the water 2 passes through the on-off valve 11 provided on the side of the waste liquid regeneration container 5 and flows into the recovered water storage container 7.

連続方式で洗浄廃液15を再生する際には、再生洗浄液流出管25と回収水流出管28のそれぞれの開閉弁26、28は開けておき、再生洗浄液貯留容器6及び回収水貯留容器7にそれぞれ回収された再生洗浄液および水が、それぞれ貯蔵される貯蔵容器(図示略)に流れ込むようにしておくと良い。再生洗浄液は再び印刷機の洗浄液として再利用すればよい。回収水は必要によって適切な処理をした後、廃棄すればよい。   When regenerating the cleaning waste liquid 15 in a continuous manner, the on-off valves 26 and 28 of the regenerated cleaning liquid outflow pipe 25 and the recovered water outflow pipe 28 are opened, and the regenerated cleaning liquid storage container 6 and the recovered water storage container 7 are respectively opened. The recovered regenerated cleaning liquid and water may be allowed to flow into storage containers (not shown) in which they are stored. The regenerated cleaning liquid may be reused again as a cleaning liquid for the printing press. The recovered water may be disposed of after appropriate treatment if necessary.

ここで、分離に要する時間、すなわち必要な滞留時間は、エマルション処理剤添加量と相関するため、処理時間を短くしたい時は、適正添加量の範囲でエマルション処理剤の添加量を増加させればよい。大まかな目安としては、廃液再生容器5の容量が20リットルの場合、ヘドロ状物質がある場合でも廃液に対するエマルション処理剤濃度0.2質量%とすると、廃液の送液速度2.5リットル/時間(滞留時間8時間)で処理ができる場合が多いが、洗浄液、インキの種類によって差はあるため、夫々のケースについて、処理時間との関係を確認すればよい。エマルション処理剤を添加しなければ、ヘドロ状物質がある場合は廃液を廃液再生容器内で滞留時間を24時間としても処理できないことは言うまでもない。   Here, since the time required for separation, that is, the necessary residence time correlates with the amount of emulsion treatment agent added, when it is desired to shorten the treatment time, the addition amount of the emulsion treatment agent should be increased within the range of the appropriate addition amount. Good. As a rough guideline, when the capacity of the waste liquid recycling container 5 is 20 liters, even if there is a sludge-like substance, if the emulsion treatment agent concentration is 0.2 mass% with respect to the waste liquid, the waste liquid feed rate is 2.5 liters / hour. In many cases, the treatment can be performed with a residence time of 8 hours. However, since there is a difference depending on the type of cleaning liquid and ink, the relationship with the treatment time may be confirmed in each case. Needless to say, if the emulsion treatment agent is not added, if there is a sludge substance, the waste liquid cannot be treated even if the residence time is 24 hours in the waste liquid regeneration container.

洗浄廃液15の再生処理を進めていくと、インキ顔料4は廃液再生容器5内部の再生洗浄液3と水2の界面に蓄積されていくため、インキ顔料4がある程度蓄積した時点で、洗浄廃液15の再生処理を一度中断し、インキ顔料4の排出を行う必要がある。このインキ顔料排出操作を以下に説明する。
廃液再生容器5の側部に設けられた開閉弁11と廃液投入管13に設けられた14を閉じた後、廃液再生容器5の底部に設けられた開閉弁12を開き、廃液再生容器5内部に残留している再生洗浄液3、インキ顔料4、及び水2を濾過タンク9に流し落とす。このとき、分離した3成分が再び混合してしまうことを避けるために、勢いよく流し落とすことは避けることが好ましい。流し落とされた再生洗浄液3、インキ顔料4、及び水2は、濾過タンク9内に設けられたフィルタ8によって濾過される。エマルション処理剤の顔料凝集作用でインキ顔料4は嵩高い凝集体18となっているため、インキ顔料4の凝集体18は濾過タンク9内のフィルタ8を目詰まりさせることなくフィルタ8上に濾し取られ、水2と再生洗浄液3は速やかに濾出されて濾過タンク9に貯蔵される。
As the cleaning waste liquid 15 is regenerated, the ink pigment 4 is accumulated at the interface between the regenerated cleaning liquid 3 and the water 2 inside the waste liquid regeneration container 5. Therefore, when the ink pigment 4 is accumulated to some extent, the cleaning waste liquid 15 is accumulated. It is necessary to interrupt the regeneration process once and discharge the ink pigment 4. This ink pigment discharge operation will be described below.
After closing the on-off valve 11 provided on the side of the waste liquid regeneration container 5 and 14 provided on the waste liquid input pipe 13, the on-off valve 12 provided on the bottom of the waste liquid regeneration container 5 is opened, and the inside of the waste liquid regeneration container 5 is opened. The regenerated cleaning liquid 3, the ink pigment 4 and the water 2 remaining in the water are poured into the filtration tank 9. At this time, in order to avoid the separated three components from being mixed again, it is preferable to avoid flushing away. The regenerated cleaning liquid 3, the ink pigment 4, and the water 2 that have been washed away are filtered by a filter 8 provided in the filtration tank 9. Since the ink pigment 4 is a bulky aggregate 18 due to the pigment aggregation action of the emulsion treatment agent, the aggregate 18 of the ink pigment 4 is filtered on the filter 8 without clogging the filter 8 in the filtration tank 9. Then, the water 2 and the regenerated cleaning liquid 3 are quickly filtered out and stored in the filtration tank 9.

濾過後、濾過タンク9に貯蔵された水と再生洗浄液の界面が安定したら、濾過タンク9の下部に接続する抜き出し管20を開閉するための開閉弁21を開き、濾過タンク9の側壁の一部を構成する透明の覗き窓22から前記界面の位置を確認しながら、抜き出し管20から濾過タンク9に貯蔵された水を抜き出す。前記界面が抜き出し管20の開閉弁21に接近し、再生洗浄液が抜き出し管20に差し掛かったら、この開閉弁21を閉じる。抜き出し管20より抜き出され、回収された水は、必要によって適切な処理をした後、廃棄すればよい。
次に抜き出し管20の開閉弁21を開いて、抜き出し管20から出てくる再生洗浄液を適当な容器(図示略)に移す。容器に移された再生洗浄液は、再生洗浄液流出管25から回収された再生洗浄液と一緒に印刷機の洗浄に再利用すればよい。
After the filtration, when the interface between the water stored in the filtration tank 9 and the regenerated cleaning liquid is stabilized, the on-off valve 21 for opening and closing the extraction pipe 20 connected to the lower part of the filtration tank 9 is opened, and a part of the side wall of the filtration tank 9 is opened. The water stored in the filtration tank 9 is extracted from the extraction pipe 20 while confirming the position of the interface from the transparent observation window 22 constituting the structure. When the interface approaches the on-off valve 21 of the extraction pipe 20 and the regenerated cleaning liquid reaches the extraction pipe 20, the on-off valve 21 is closed. The water extracted and recovered from the extraction pipe 20 may be disposed of after being appropriately treated as necessary.
Next, the on-off valve 21 of the extraction pipe 20 is opened, and the regenerated cleaning liquid coming out of the extraction pipe 20 is transferred to an appropriate container (not shown). The regenerated cleaning liquid transferred to the container may be reused for cleaning the printing press together with the regenerated cleaning liquid recovered from the regenerated cleaning liquid outflow pipe 25.

上記のような濾過操作を何回か繰り返して、フィルタ8の濾過速度が遅くなってきた時点で、濾過タンク9からフィルタ8を取り外し、新しいフィルタ8と交換する、あるいはフィルタ8上に溜まったインキ顔料を除去した後、再び濾過タンク9にフィルタ8を取り付けるなどの対応をすれば良い。
上記の操作を終了したら、再び同じ操作を繰り返し、連続方式で洗浄廃液15の再生処理を繰り返せばよい。
The filtration operation as described above is repeated several times, and when the filtration speed of the filter 8 becomes slow, the filter 8 is removed from the filtration tank 9 and replaced with a new filter 8 or ink accumulated on the filter 8. After removing the pigment, a countermeasure such as attaching the filter 8 to the filtration tank 9 again may be taken.
When the above operation is completed, the same operation is repeated again, and the regeneration process of the cleaning waste liquid 15 may be repeated in a continuous manner.

[洗浄廃液(模擬廃液)]
以下のインキと洗浄液、および水を混合して模擬廃液を調製し廃液再生テストを実施した。
(インキ)
1)ハイエコーMZ(東洋インキ製造株式会社製)
2)ジオスーGN(大日本インキ化学工業株式会社製)
3)スーパーテックプラスH(株式会社ティーアンドケイ東華製)
4)ダイアトーンM(サカタインクス株式会社製)
5)セルボY(東京インキ株式会社製)
[Washing waste liquid (simulated waste liquid)]
The following ink, cleaning liquid, and water were mixed to prepare a simulated waste liquid, and a waste liquid regeneration test was performed.
(ink)
1) High Echo MZ (Toyo Ink Manufacturing Co., Ltd.)
2) Geosu GN (Dainippon Ink Chemical Co., Ltd.)
3) Super Tech Plus H (manufactured by T & K Toka)
4) Diatone M (manufactured by Sakata Inx Corporation)
5) Celvo Y (manufactured by Tokyo Ink Co., Ltd.)

(洗浄液)
1)ダイクリーン(大日本インキ化学工業株式会社製)
2)オートクリーン(日研化学株式会社製)
3)ブラクリンS(ニッカ株式会社製)
4)プリントクリーナ(東洋インキ製造株式会社製)
5)スーパークリーン(ザ・インクテック株式会社製)
(Cleaning solution)
1) Die Clean (Dainippon Ink Chemical Co., Ltd.)
2) Auto Clean (Nikken Chemical Co., Ltd.)
3) Bracrine S (made by Nikka Corporation)
4) Print cleaner (Toyo Ink Manufacturing Co., Ltd.)
5) Super Clean (made by The Ink Tech Co., Ltd.)

[実施例1]
ハイエコーMZの藍、紅、黄、墨の4色のインキを均等に混合して、ダイクリーンで顔料濃度2質量%に希釈し、さらに顔料を分散した洗浄液と同量の水を加えて、模擬廃液を20kg調製した。この模擬廃液をホモジナイザー(商品名 ULTRA TURRAX Disperser T−50、MASUDA製)で15分攪拌した後、10分間静置したが、模擬廃液全体が洗浄液と水からなるエマルションと推定される物質(流動性が低く、特に下部は弾力のあるゼリー状である。以後、「ヘドロ状物質」と記載する)になっており、洗浄液層や水層は目視で確認できなかった。この状態の模擬廃液を模擬廃液201とする。図2に、模擬廃液201の構成図を示す。
この模擬廃液201にエマルション処理剤としてニューポールPE−61((HLB 1.8〜2.0、ポリオキシプロピレン部分の平均分子量1,750、三洋化成製)を模擬廃液201に対して0.05質量%となるように添加した。
[Example 1]
High-echo MZ indigo, red, yellow, and black inks are mixed evenly, diluted with dye clean to a pigment concentration of 2% by mass, and then added with the same amount of water as the washing liquid in which the pigment is dispersed. 20 kg of waste liquid was prepared. The simulated waste liquid was stirred for 15 minutes with a homogenizer (trade name ULTRA TURRAX Disperser T-50, manufactured by MASUDA) and allowed to stand for 10 minutes. However, the simulated waste liquid was estimated to be an emulsion composed of a cleaning liquid and water (fluidity). In particular, the lower part is in the form of an elastic jelly, which is hereinafter referred to as “sludge substance”), and the cleaning liquid layer and the water layer could not be visually confirmed. The simulated waste liquid in this state is referred to as simulated waste liquid 201. FIG. 2 shows a configuration diagram of the simulated waste liquid 201.
New emulsion PE-61 ((HLB 1.8-2.0, polyoxypropylene part average molecular weight 1,750, manufactured by Sanyo Chemical Co., Ltd.) as an emulsion treatment agent was added to this simulated waste liquid 201 to 0.05. It added so that it might become mass%.

このエマルション処理剤を添加した模擬廃液211(20リットル)を、廃液投入管13から廃液再生装置1の廃液再生容器5内にポンプで4リットル/時の送液速度で送液した。廃液再生容器5と再生液貯留容器6の間の壁16を模擬廃液211がオーバーフローする前に模擬廃液211の送液を止めて、廃液投入管13に設けられた開閉弁14を閉じた後、模擬廃液211を廃液再生容器5内で8時間静置した。図3は、エマルション処理剤を添加し、攪拌後、8時間静置した模擬廃液221の状態を示す模式図である。
この8時間静置後の模擬廃液221を、廃液再生容器5の底部に設けられた開閉弁12を半開にして、濾過タンク9にゆっくり流し落とし、約5分で20リットルの液を濾過した。
The simulated waste liquid 211 (20 liters) to which the emulsion treating agent was added was fed from the waste liquid input pipe 13 into the waste liquid regeneration container 5 of the waste liquid regeneration apparatus 1 by a pump at a liquid feed speed of 4 liters / hour. Before the simulated waste liquid 211 overflows the wall 16 between the waste liquid regeneration container 5 and the regenerated liquid storage container 6, the simulated waste liquid 211 is stopped from being fed, and the on-off valve 14 provided in the waste liquid input pipe 13 is closed. The simulated waste liquid 211 was left in the waste liquid regeneration container 5 for 8 hours. FIG. 3 is a schematic diagram showing the state of the simulated waste liquid 221 that has been added with the emulsion treating agent and left to stand for 8 hours after stirring.
The simulated waste liquid 221 after standing for 8 hours was slowly dropped into the filtration tank 9 with the on-off valve 12 provided at the bottom of the waste liquid regeneration container 5 being half-opened, and 20 liters of liquid was filtered in about 5 minutes.

覗き窓22から濾過タンク9内を観察し、濾過後15分で濾過タンク9の回収水と再生洗浄液の界面が安定したため、抜き出し管20の開閉弁21を開いた。廃液再生容器5に設けられた覗き窓22から前記界面の位置を確認しながら抜き出し管20から回収水を抜き出した。前記界面が抜き出し管20の開閉弁21に接近し、再生洗浄液が抜き出し管20に差し掛かったところで、この開閉弁21を閉じた。回収水は回収水用貯蔵容器に受け入れ、必要に応じて生物学的酸素要求量(BOD)や化学的酸素要求量(COD)の基準値を満たすように廃水処理をした後、廃棄した。   The inside of the filtration tank 9 was observed from the observation window 22, and the opening / closing valve 21 of the extraction pipe 20 was opened because the interface between the recovered water and the regenerated cleaning liquid in the filtration tank 9 was stabilized 15 minutes after the filtration. The recovered water was extracted from the extraction pipe 20 while confirming the position of the interface from the observation window 22 provided in the waste liquid regeneration container 5. When the interface approached the open / close valve 21 of the extraction pipe 20 and the regenerated cleaning liquid reached the extraction pipe 20, the open / close valve 21 was closed. The recovered water was received in a storage container for recovered water, treated with waste water so as to meet the reference values of biological oxygen demand (BOD) and chemical oxygen demand (COD) as necessary, and then discarded.

次に抜き出し管20の開閉弁21を開いて、抜き出し管20から出てくる再生洗浄液を再生洗浄液用貯蔵容器に受け入れ、印刷機の洗浄に再利用した。
上記のような模擬廃液を5回繰り返し処理した。5回目の再生処理における濾過時間は初回再生処理の濾過時間に比べて約2倍の濾過時間を要したため、濾過タンク9からフィルタ8を取り外し、新しいフィルタ8と交換した。
このようにして5回の再生処理で回収された再生洗浄液は約47リットル、再生水は約48リットル、インキ顔料(液を含む湿潤な状態)は約0.35kgであった。
Next, the on-off valve 21 of the extraction pipe 20 was opened, and the regenerated cleaning liquid coming out of the extraction pipe 20 was received in the regenerated cleaning liquid storage container and reused for cleaning the printing press.
The simulated waste liquid as described above was repeatedly treated 5 times. Since the filtration time in the fifth regeneration process required about twice as long as the filtration time in the first regeneration process, the filter 8 was removed from the filtration tank 9 and replaced with a new filter 8.
Thus, the regenerated washing liquid recovered by the five regenerating processes was about 47 liters, the regenerated water was about 48 liters, and the ink pigment (wet state including the liquid) was about 0.35 kg.

本実施例の処理方法によれば、重力沈降および濾過操作だけで再生処理できない嵩高いヘドロ状物質を含有する洗浄廃液に、エマルション処理剤を添加することで、バッチ方式により重力沈降と濾過操作で洗浄液、インキ顔料、回収水に分離でき再生処理することが可能となる。すなわち、本実施例の処理方法では、処理嵩高いヘドロ状物質を含有する洗浄廃液を有機系洗浄液、インキ顔料、及び水に分離する時間を短縮できるとともに、最終的に分離された洗浄液は再利用が可能であり、廃棄されるインキ顔料の容積も減容するため、廃棄処理コストを含む印刷機のランニングコストの低減ができる。
また、本実施例の処理方法は、エマルション処理剤を添加する以外は、洗浄廃液の分離に電力などのエネルギーを使用しないため、環境にやさしい処理方法である。
According to the treatment method of this example, by adding an emulsion treatment agent to a washing waste liquid containing a bulky sludge-like substance that cannot be regenerated only by gravity sedimentation and filtration operation, it is possible to perform gravity sedimentation and filtration operation by a batch method. It can be separated into cleaning liquid, ink pigment, and recovered water, and can be recycled. That is, in the treatment method of the present embodiment, it is possible to shorten the time for separating the cleaning waste liquid containing the bulky sludge substance into the organic cleaning liquid, the ink pigment, and water, and the cleaning liquid finally separated is reused. Since the volume of the ink pigment to be discarded is reduced, the running cost of the printing press including the disposal cost can be reduced.
In addition, the treatment method of this example is an environment-friendly treatment method because energy such as electric power is not used for separation of the cleaning waste liquid except that an emulsion treatment agent is added.

[比較例1]エマルション処理剤の添加なし
実施例1において、模擬廃液201にエマルション処理剤としてニューポールPE−61(三洋化成製)を添加しなかった以外は、同様にして模擬廃液201を処理した。
静置8時間後、廃液再生容器5の底部に設けられた開閉弁12を半開にして、濾過タンク9に廃液をゆっくり流し落とした。最初1分ほどで約1リットルほどの濾液(再生洗浄剤と回収水の合計)がタンク内に溜まったが、その後はフィルタ8が目詰まりを起こし、8時間たっても濾液は2リットル程度であり、20リットルの廃液は8時間では濾過処理できなかった。
[Comparative Example 1] No addition of emulsion treatment agent In Example 1, the simulation waste solution 201 was treated in the same manner except that New Pole PE-61 (manufactured by Sanyo Chemical) was not added to the simulation waste solution 201 as an emulsion treatment agent. did.
After 8 hours of standing, the on-off valve 12 provided at the bottom of the waste liquid regeneration container 5 was opened half way, and the waste liquid was slowly poured into the filtration tank 9. About 1 liter of filtrate (total of regenerated cleaning agent and recovered water) collected in the tank in about 1 minute at the beginning, but after that, the filter 8 was clogged and the filtrate was about 2 liters even after 8 hours. 20 liters of waste liquid could not be filtered in 8 hours.

[実施例2]
実施例1と同じ模擬廃液201に対してエマルション処理剤としてニューポールPE−61((HLB 1.8〜2.0、ポリオキシプロピレン部分の平均分子量1,750、三洋化成製)を0.2質量%添加した液を、模擬廃液211とした。
廃液再生容器5の底部に設けられた開閉弁12、14を閉じ、開閉弁11を26、29を開いた後、廃液再生容器5上部の蓋30を取って、回収水流出管28の入り口から水が多少流出するまで廃液再生容器5に水を蓄えた。
次に廃液再生容器5と再生液貯留容器6の間の壁16を洗浄液がわずかにオーバーフローする程度まで、先に入れた水と混合しないように廃液再生容器5内に静かに新しい洗浄液を注ぎこんだ。
[Example 2]
0.2% of New Pole PE-61 ((HLB 1.8-2.0, average molecular weight of polyoxypropylene part 1,750, manufactured by Sanyo Chemical Co., Ltd.)) as an emulsion treatment agent for the same simulated waste liquid 201 as in Example 1. The liquid added with mass% was designated as simulated waste liquid 211.
After closing the on-off valves 12 and 14 provided at the bottom of the waste liquid regeneration container 5 and opening the on-off valves 11 and 26 and 29, the lid 30 on the upper part of the waste liquid regeneration container 5 is removed and the recovery water outflow pipe 28 is opened. The water was stored in the waste liquid recycling container 5 until some water flowed out.
Next, gently pour the new cleaning liquid into the waste liquid regeneration container 5 so that the cleaning liquid slightly overflows the wall 16 between the waste liquid regeneration container 5 and the regeneration liquid storage container 6 so as not to mix with the previously added water. It is.

この後、開閉弁14を開き廃液投入管13からエマルション処理剤が添加された前記模擬廃液211の50リットルを廃液再生容器5内に2.5リットル/時間の送液速度で連続的に送り込んだ。廃液再生容器5に送り込まれた模擬廃液211は廃液再生容器5に滞留する間に再生洗浄液、インキ顔料、及び水に分離された。
再生洗浄液は、廃液再生容器5と再生洗浄液貯留容器6の間の壁16をオーバーフローして再生洗浄液貯留溶液6に流れ込み、更に再生洗浄液流出管25から流出させて再生洗浄液用貯蔵容器に貯蔵した。再生できた洗浄液の量は約24リットルであった。
Thereafter, the on-off valve 14 was opened and 50 liters of the simulated waste liquid 211 added with the emulsion treatment agent from the waste liquid input pipe 13 was continuously fed into the waste liquid regeneration container 5 at a liquid feeding speed of 2.5 liters / hour. . The simulated waste liquid 211 sent into the waste liquid regeneration container 5 was separated into a regenerated cleaning liquid, an ink pigment, and water while staying in the waste liquid regeneration container 5.
The regenerated cleaning liquid overflowed the wall 16 between the waste liquid regenerating container 5 and the regenerated cleaning liquid storage container 6 to flow into the regenerated cleaning liquid storage solution 6, and was further discharged from the regenerated cleaning liquid outflow pipe 25 and stored in the regenerated cleaning liquid storage container. The amount of the cleaning solution that could be regenerated was about 24 liters.

一方、水は廃液再生容器5側部の開閉弁11を通過して回収水貯留容器7に流れ込み、更に回収水流出管28から流出させて回収水用貯蔵容器に受け入れた。回収水は約24.5リットルで、下水に排出できる水質であることを分析により確認した後、排水した。
インキ顔料は廃液再生容器5内に残留していたが、模擬廃液211の処理を続けることは可能であった。しかし、残留しているインキ顔料の量を確認するため、以下の手順でインキ顔料を排出した。
廃液再生容器5側部の開閉弁11及び廃液投入管13の開閉弁14を閉じた後、廃液再生容器5底部の開閉弁12を半開にして、廃液再生容器5に残留している再生洗浄液、インキ顔料、水を濾過タンク9にゆっくり流し落とし、濾過した。
On the other hand, the water passed through the on-off valve 11 on the side of the waste liquid regeneration container 5 and flowed into the recovered water storage container 7, and was further discharged from the recovered water outflow pipe 28 and received in the recovered water storage container. The recovered water was approximately 24.5 liters, and was drained after confirming by analysis that the water quality could be discharged into sewage.
Although the ink pigment remained in the waste liquid recycling container 5, it was possible to continue the treatment of the simulated waste liquid 211. However, in order to confirm the amount of the remaining ink pigment, the ink pigment was discharged by the following procedure.
After closing the on-off valve 11 on the side of the waste liquid regeneration container 5 and the on-off valve 14 of the waste liquid input pipe 13, the on-off valve 12 on the bottom of the waste liquid regeneration container 5 is opened halfway to regenerate the cleaning liquid remaining in the waste liquid regeneration container 5, The ink pigment and water were slowly poured into the filtration tank 9 and filtered.

覗き窓22から濾過タンク9内を観察し、濾過終了後15分で濾過タンク9の回収水と再生洗浄液の界面が安定したため、抜き出し管20の開閉弁21を開いた。廃液再生容器5に設けられた覗き窓22から前記界面の位置を確認しながら抜き出し管20から回収水を抜き出した。前記界面が抜き出し管20の開閉弁21に接近し、再生洗浄液が抜き出し管20に差し掛かったところで、この開閉弁21を閉じた。回収水は回収水用貯蔵容器に受け入れ、上記と同様にして排水した。
次に抜き出し管20の開閉弁21を開いて、抜き出し管20から出てくる再生洗浄液を再生洗浄液用貯蔵容器に受け入れ、印刷機の洗浄に再利用した。
その後、濾過タンク9からフィルタ8を取り外し、湿潤状態のインキ顔料の重量を測ったところ約0.18kgであった。なお、濾過タンク9には新しいフィルタ8を装着した。
The inside of the filtration tank 9 was observed through the observation window 22, and the interface between the recovered water and the regenerated cleaning liquid in the filtration tank 9 was stabilized 15 minutes after the completion of filtration, and therefore the opening / closing valve 21 of the extraction pipe 20 was opened. The recovered water was extracted from the extraction pipe 20 while confirming the position of the interface from the observation window 22 provided in the waste liquid regeneration container 5. When the interface approached the open / close valve 21 of the extraction pipe 20 and the regenerated cleaning liquid reached the extraction pipe 20, the open / close valve 21 was closed. The recovered water was received in a storage container for recovered water and drained in the same manner as described above.
Next, the on-off valve 21 of the extraction pipe 20 was opened, and the regenerated cleaning liquid coming out of the extraction pipe 20 was received in the regenerated cleaning liquid storage container and reused for cleaning the printing press.
Thereafter, the filter 8 was removed from the filtration tank 9, and the weight of the wet ink pigment was measured and found to be about 0.18 kg. A new filter 8 was attached to the filtration tank 9.

本実施例の処理方法によれば、重力沈降および濾過操作だけで再生処理できない嵩高いヘドロ状物質を含有する洗浄廃液に、エマルション処理剤を添加し、連続方式の重力沈降で、洗浄液、インキ顔料、回収水に分離でき洗浄液を再生処理することが可能となる。すなわち、本実施例の処理方法では、処理嵩高いヘドロ状物質を含有する洗浄廃液を有機系洗浄液、インキ顔料、及び水に連続処理で、かつ短時間で分離できるとともに、最終的に分離された洗浄液は再利用が可能であり、廃棄されるインキ顔料の容積も減容するため、廃棄処理コストを含む印刷機のランニングコストの低減ができる。
また、本実施例の処理方法は、エマルション処理剤を添加する以外は、洗浄廃液の分離に電力などのエネルギーを使用しないため、環境にやさしい処理方法である。
According to the processing method of this example, an emulsion treatment agent is added to a cleaning waste liquid containing a bulky sludge-like substance that cannot be regenerated only by gravity sedimentation and filtration. Then, it can be separated into recovered water, and the cleaning liquid can be regenerated. That is, in the processing method of this example, the cleaning waste liquid containing the bulky sludge-like substance can be separated into the organic cleaning liquid, the ink pigment, and water continuously in a short time and finally separated. Since the cleaning liquid can be reused and the volume of the ink pigment to be discarded is reduced, the running cost of the printing press including the disposal cost can be reduced.
In addition, the treatment method of this example is an environment-friendly treatment method because energy such as electric power is not used for separation of the cleaning waste liquid except that an emulsion treatment agent is added.

[比較例2]エマルション処理剤の添加なし
実施例2において、模擬廃液201にエマルション処理剤としてニューポールPE−61(三洋化成製)を添加しなかった以外は、同様にして模擬廃液201を処理した。
開閉弁14を開き廃液投入管13からエマルション処理剤が添加されてない模擬廃液201を廃液再生容器5内に2.5リットル/時間の送液速度で連続で送り込んだ。送液開始後約4時間後に、本来透明な再生洗浄液が流出してくるはずの再生洗浄液流出管25から洗浄廃液(模擬廃液201)そのものが流出してきたため、その時点で送液をストップした。廃液再生容器5の蓋30を外して廃液再生容器5内部を観察すると、廃液再生容器内部はヘドロ状物質で充満しており、洗浄液、インキ顔料、水への分離は全く出来てないことを確認した。
[Comparative Example 2] No addition of emulsion treatment agent In Example 2, the simulation waste solution 201 was treated in the same manner except that New Pole PE-61 (manufactured by Sanyo Chemical) was not added as an emulsion treatment agent to the simulation waste solution 201. did.
The on-off valve 14 was opened, and the simulated waste liquid 201 to which the emulsion treatment agent was not added was continuously fed from the waste liquid charging pipe 13 into the waste liquid regeneration container 5 at a liquid feeding speed of 2.5 liters / hour. About 4 hours after the start of liquid feeding, since the cleaning waste liquid (simulated waste liquid 201) itself flowed out from the regenerated cleaning liquid outflow pipe 25 from which the transparent regenerated cleaning liquid should flow out originally, the liquid feeding was stopped at that time. When the lid 30 of the waste liquid regeneration container 5 is removed and the inside of the waste liquid regeneration container 5 is observed, it is confirmed that the inside of the waste liquid regeneration container is filled with sludge-like substances and that it cannot be separated into cleaning liquid, ink pigment, and water at all. did.

廃液再生装置の一例を示す模式断面図である。It is a schematic cross section showing an example of a waste liquid recycling apparatus. 実施例及び比較例で再生処理した模擬廃液の、エマルション処理剤を添加しない状態を示す模式図である。It is a schematic diagram which shows the state which does not add an emulsion processing agent of the simulation waste liquid regenerated by the Example and the comparative example. 実施例で再生処理した模擬廃液にエマルション処理剤を添加し、攪拌後、8時間静置した状態を示す模式図である。It is a schematic diagram which shows the state which added the emulsion processing agent to the simulation waste liquid regenerated in the Example, and left still for 8 hours after stirring. 沈降法で用いられる従来の廃液再生装置の概略構成を示す図である。It is a figure which shows schematic structure of the conventional waste-liquid reproduction | regeneration apparatus used with a sedimentation method.

符号の説明Explanation of symbols

1 廃液再生装置
2 水
3 再生洗浄液
4 インキ顔料
5 廃液再生容器
6 再生洗浄液貯留容器
7 回収水貯留容器
8 インキ顔料回収フィルタ
9 濾過タンク
11 開閉弁
12 開閉弁
13 廃液投入管
14 開閉弁
15 洗浄廃液
16 壁
18 インキ顔料の凝集体
20 抜き出し管
21 開閉弁
22 覗き窓
25 再生洗浄液流出管
26 開閉弁
28 回収水流出管
29 開閉弁
30 蓋
DESCRIPTION OF SYMBOLS 1 Waste liquid regeneration apparatus 2 Water 3 Recycled cleaning liquid 4 Ink pigment 5 Waste liquid regeneration container 6 Recycled cleaning liquid storage container 7 Recovered water storage container 8 Ink pigment recovery filter 9 Filtration tank 11 On-off valve 12 On-off valve 13 Waste liquid input pipe 14 On-off valve 15 Washing waste liquid 16 Wall 18 Aggregate of ink pigment 20 Extraction pipe 21 On-off valve 22 Viewing window 25 Recycled washing liquid outflow pipe 26 On-off valve 28 Collected water outflow pipe 29 On-off valve 30 Lid

Claims (12)

インキ顔料、有機系洗浄液、及び水を含む廃液を、再生容器を有する再生装置に投入して再生する廃液再生方法であって、
前記再生容器において前記廃液を、重力沈降を利用して再生洗浄液、インキ顔料、及び水に分離する分離工程を有し、
前記分離工程より前に、水と洗浄液から主としてなるエマルションを破壊しかつインキ顔料粒子を凝集させるエマルション処理剤を前記廃液に添加するエマルション処理剤添加工程を有することを特徴とする、印刷機の廃液再生方法。
A waste liquid recycling method in which a waste liquid containing an ink pigment, an organic cleaning liquid, and water is put into a regeneration device having a regeneration container to regenerate,
A separation step of separating the waste liquid in the regeneration container into a regenerated cleaning liquid, an ink pigment, and water using gravity sedimentation;
A waste liquid for a printing press, characterized by having an emulsion treatment agent addition step for adding an emulsion treatment agent that breaks an emulsion mainly composed of water and a washing liquid and agglomerates ink pigment particles to the waste solution before the separation step. Playback method.
前記エマルション処理剤が、非イオン性界面活性剤を主成分とすることを特徴とする、請求項1に記載の印刷機の廃液再生方法。   The method for regenerating a waste liquid of a printing press according to claim 1, wherein the emulsion treatment agent contains a nonionic surfactant as a main component. 前記非イオン性界面活性剤が、ポリオキシエチレン鎖を構造の一部として有する共重合体であり、HLBが10以下であることを特徴とする、請求項2に記載の印刷機の廃液再生方法。   The waste liquid recycling method for a printing press according to claim 2, wherein the nonionic surfactant is a copolymer having a polyoxyethylene chain as a part of the structure, and the HLB is 10 or less. . 前記非イオン性界面活性剤が、ポリオキシエチレン鎖を構造の一部として有する共重合体であり、HLBが8以下であることを特徴とする、請求項2に記載の印刷機の廃液再生方法。   The waste liquid recycling method for a printing press according to claim 2, wherein the nonionic surfactant is a copolymer having a polyoxyethylene chain as a part of the structure, and the HLB is 8 or less. . 前記非イオン性界面活性剤の質量平均分子量が1200以上であることを特徴とする、請求項2から請求項4のいずれかに記載の印刷機の廃液再生方法。   The method for reclaiming waste liquid from a printing press according to any one of claims 2 to 4, wherein the nonionic surfactant has a mass average molecular weight of 1200 or more. 前記エマルション処理剤添加工程が、前記分離工程までに前記エマルション処理剤の有効成分が前記廃液全体に対して0.05質量%以上5質量%になるように、前記エマルション処理剤を前記廃液に添加する工程であることを特徴とする、請求項1から請求項5のいずれかに記載の印刷機の廃液再生方法。   In the emulsion treatment agent addition step, the emulsion treatment agent is added to the waste liquid so that the active ingredient of the emulsion treatment agent is 0.05% by mass or more and 5% by mass with respect to the whole waste liquid by the separation step. The method for recycling waste liquid of a printing press according to any one of claims 1 to 5, wherein 印刷機から排出された前記廃液を前記再生装置に投入するまで該廃液を保管容器中に保管しておく保管工程を有し、
該保管工程中において、前記エマルション処理剤添加工程を行い、前記廃液及び前記エマルション処理剤を含む液を攪拌し、
前記保管工程の後に、前記再生装置において前記分離工程を行うことを特徴とする、請求項1から請求項6のいずれかに記載の印刷機の廃液再生方法。
A storage step of storing the waste liquid in a storage container until the waste liquid discharged from the printing press is put into the regenerator;
In the storage step, the emulsion treatment agent addition step is performed, and the liquid containing the waste liquid and the emulsion treatment agent is stirred,
The waste liquid regeneration method for a printing press according to any one of claims 1 to 6, wherein the separation step is performed in the regeneration device after the storage step.
印刷機から排出された前記廃液を前記再生装置に投入するまで該廃液を保管容器中に保管しておく保管工程を有し、
前記保管工程と前記分離工程との間において、前記保管容器と前記再生容器との間に設けられた廃液流路のいずこかで前記エマルション処理剤を前記廃液に添加し、前記廃液及び前記エマルション処理剤を含む液をそれ自身の流れで攪拌することにより前記エマルション処理剤添加工程を行うことを特徴とする、請求項1から請求項6のいずれかに記載の印刷機の廃液再生方法。
A storage step of storing the waste liquid in a storage container until the waste liquid discharged from the printing press is put into the regenerator;
Between the storage step and the separation step, the emulsion treatment agent is added to the waste liquid somewhere in the waste liquid flow path provided between the storage container and the regeneration container, and the waste liquid and the The waste liquid regeneration method for a printing press according to any one of claims 1 to 6, wherein the emulsion treatment agent addition step is performed by stirring the liquid containing the emulsion treatment agent in its own flow.
前記エマルション処理剤添加工程が、前記エマルション処理剤を、印刷機から排出される廃液を受け入れる廃液受け入れ槽に添加する工程であることを特徴とする、請求項1から請求項6のいずれかに記載の印刷機の廃液再生方法。   The said emulsion processing agent addition process is a process of adding the said emulsion processing agent to the waste liquid receiving tank which receives the waste liquid discharged | emitted from a printing machine, The any one of Claims 1-6 characterized by the above-mentioned. Method for recycling waste liquids in Japanese printing presses. インキ顔料、有機系洗浄剤、及び水を含む廃液を再生する廃液再生装置であって、
前記廃液を一定時間滞留させ該廃液を重力沈降によって再生洗浄液、インキ顔料、及び水に分離する再生容器と、
前記再生容器に隣接して設けられ、該再生容器内で分離された再生洗浄液を回収する再生液貯留容器と、
前記再生容器に隣接して設けられ、該再生容器内で分離された再生水を回収する回収水貯留容器と、
前記再生容器の下方に設けられ、内部にインキ顔料回収フィルタを備えた濾過器と、
該濾過器からの濾液を重力沈降によって再生洗浄液と水に分離する濾液分離容器とを有することを特徴とする、印刷機の廃液再生装置。
A waste liquid regenerating apparatus for regenerating a waste liquid containing an ink pigment, an organic cleaning agent, and water,
A regeneration container that retains the waste liquid for a certain period of time and separates the waste liquid into a regenerated cleaning liquid, an ink pigment, and water by gravity sedimentation;
A regenerative liquid storage container that is provided adjacent to the regenerative container and collects the regenerated cleaning liquid separated in the regenerative container;
A recovered water storage container that is provided adjacent to the regeneration container and collects the recycled water separated in the regeneration container;
A filter provided below the regeneration container and having an ink pigment recovery filter therein;
A waste liquid recycling apparatus for a printing press, comprising: a filtrate separation container for separating a filtrate from the filter into a regenerated washing liquid and water by gravity sedimentation.
インキ顔料、有機系洗浄剤、及び水を含む廃液を再生する廃液再生方法であって、
前記廃液を請求項10に記載の廃液再生装置に投入する工程と、
前記廃液再生装置を用いて前記廃液を再生洗浄液、インキ顔料、及び水に分離する工程とを、バッチ方式で行うことを特徴とする印刷機の廃液再生方法
A waste liquid regeneration method for regenerating a waste liquid containing an ink pigment, an organic cleaning agent, and water,
Charging the waste liquid into the waste liquid recycling apparatus according to claim 10;
A waste liquid recycling method for a printing press, characterized in that the step of separating the waste liquid into a recycled cleaning liquid, an ink pigment, and water using the waste liquid recycling apparatus is performed in a batch system.
インキ顔料、有機系洗浄剤、及び水を含む廃液を再生する廃液再生方法であって、
前記廃液を前記請求項10に記載の廃液再生装置に供給する工程と、
前記廃液再生装置を用いて前記廃液を再生洗浄液、インキ顔料、及び水に分離する工程とを、連続方式で同時に行うことを特徴とする印刷機の廃液再生方法。
A waste liquid regeneration method for regenerating a waste liquid containing an ink pigment, an organic cleaning agent, and water,
Supplying the waste liquid to the waste liquid recycling apparatus according to claim 10;
A method of recycling a waste liquid of a printing press, wherein the step of separating the waste liquid into a regenerated cleaning liquid, an ink pigment, and water using the waste liquid recycling apparatus is simultaneously performed in a continuous manner.
JP2006043808A 2006-02-21 2006-02-21 Method and apparatus for regenerating waste liquid of printer Withdrawn JP2007222710A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2006043808A JP2007222710A (en) 2006-02-21 2006-02-21 Method and apparatus for regenerating waste liquid of printer

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2006043808A JP2007222710A (en) 2006-02-21 2006-02-21 Method and apparatus for regenerating waste liquid of printer

Publications (1)

Publication Number Publication Date
JP2007222710A true JP2007222710A (en) 2007-09-06

Family

ID=38545013

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2006043808A Withdrawn JP2007222710A (en) 2006-02-21 2006-02-21 Method and apparatus for regenerating waste liquid of printer

Country Status (1)

Country Link
JP (1) JP2007222710A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2016055256A (en) * 2014-09-10 2016-04-21 富士フイルム株式会社 Liquid separation device

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2016055256A (en) * 2014-09-10 2016-04-21 富士フイルム株式会社 Liquid separation device

Similar Documents

Publication Publication Date Title
CN107001081A (en) The processing method of washer draining and the processing unit of washer draining
WO2006084110A2 (en) Ballasted flocculation process and system incorporating an electro-coagulation reactor for treating water or wastewater
JP4466216B2 (en) Magnetic separation and purification method and apparatus
US4149953A (en) Apparatus for removing impurities from waste water
EP1640053B1 (en) Waste water filtration system vehicle
CN104649482B (en) A kind of method for processing waste emulsified mixture
CN103922518B (en) Rinse pretreatment process and the system of sewage
JP2007222710A (en) Method and apparatus for regenerating waste liquid of printer
WO1994010611A1 (en) Developer circulating method in flexographic plate making step and apparatus for practicing the same
JP2005111424A (en) Method and apparatus for removing substance to be removed from fluid and sludge separation and recovery apparatus
JP2678699B2 (en) Grinding waste liquid purification method
US7472651B2 (en) Waste liquid regenerator of printing machine
JP3981489B2 (en) Wet image forming apparatus and wet image forming method
JP2007160177A (en) Waste liquid reproduction method of printing press, and emulsion treating agent for waste liquid reproduction of printing press
JP2004105901A (en) Method and apparatus for continuously recovering paint waste
CN114641456A (en) Accelerated settling of flocs after electrocoagulation/electrochemical process using ballasted flocculation
JP3697123B2 (en) Waste liquid recycling device for printing press
JP3586656B2 (en) Waste liquid regenerating apparatus and waste liquid regenerating method for printing press
KR100603855B1 (en) Treatment method of metalworking fluid and cleansing solution and treatment system thereof
KR100483253B1 (en) Method for recycling of aqueous cleaner solution and synthetic chemical solution using ozone and system thereof
JP3592997B2 (en) Waste liquid recycling device for printing press
JP3637262B2 (en) Waste liquid recycling device for printing press
JP6086287B2 (en) Manufacturing method of recording material
JP2947745B2 (en) Cleaning liquid regeneration processing method and cleaning liquid regeneration processing apparatus
JP2004167372A (en) Flocculating method and apparatus for suspended particle

Legal Events

Date Code Title Description
A300 Withdrawal of application because of no request for examination

Free format text: JAPANESE INTERMEDIATE CODE: A300

Effective date: 20090512