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JPS6256763B2 - - Google Patents

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Publication number
JPS6256763B2
JPS6256763B2 JP56179012A JP17901281A JPS6256763B2 JP S6256763 B2 JPS6256763 B2 JP S6256763B2 JP 56179012 A JP56179012 A JP 56179012A JP 17901281 A JP17901281 A JP 17901281A JP S6256763 B2 JPS6256763 B2 JP S6256763B2
Authority
JP
Japan
Prior art keywords
solvent
waste ink
pigment
ink
dispersibility
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP56179012A
Other languages
Japanese (ja)
Other versions
JPS5881410A (en
Inventor
Masataka Mizutani
Kazuo Sakanaya
Hayami Nagano
Masashi Hirao
Atsushi Kametaka
Masato Yamaguchi
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.)
Dai Nippon Printing Co Ltd
Mitsubishi Heavy Industries Ltd
Original Assignee
Dai Nippon Printing Co Ltd
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 Dai Nippon Printing Co Ltd, Mitsubishi Heavy Industries Ltd filed Critical Dai Nippon Printing Co Ltd
Priority to JP56179012A priority Critical patent/JPS5881410A/en
Publication of JPS5881410A publication Critical patent/JPS5881410A/en
Publication of JPS6256763B2 publication Critical patent/JPS6256763B2/ja
Granted legal-status Critical Current

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  • Filtration Of Liquid (AREA)
  • Inks, Pencil-Leads, Or Crayons (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Extraction Or Liquid Replacement (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

本発明は廃インキから顔料および溶剤等の有価
物を回収する方法に関する。 凸板、凹板、オフセツト、グラビア等各種の印
刷に適用されるインキは、一般に、顔料、樹脂、
溶剤、可塑剤等の添加剤からなり、第1図に模式
的に示すように、顔料粒子1が樹脂2を介在して
溶剤3中に均一に分散しているものと考えられ
る。 この顔料粒子は、体質顔料、無機系顔料、有機
系顔料に大別され、それぞれ表1に示すような物
性を有している。
The present invention relates to a method for recovering valuables such as pigments and solvents from waste ink. Inks used for various types of printing, such as convex, concave, offset, and gravure, generally contain pigments, resins,
It consists of additives such as a solvent and a plasticizer, and as schematically shown in FIG. 1, it is thought that pigment particles 1 are uniformly dispersed in a solvent 3 with a resin 2 interposed therebetween. These pigment particles are broadly classified into extender pigments, inorganic pigments, and organic pigments, each of which has physical properties as shown in Table 1.

【表】【table】

【表】 なお、溶剤、樹脂、可塑剤等の添加剤は、上記
の顔料の種類に応じて適切なものが使用されるこ
とはいうまでもない。 新品インキの色相は、大別して赤、青、黄、白
および黒系統であり、用途に応じて単独もしくは
二色以上を混合して用いる。 ところで、色が黒くくすんで使用できなくなつ
たインキや、印刷機等を洗浄したあとの廃液は、
廃インキとしてインキ製造工程や印刷工場等から
大量に排出され、いずれの廃インキも各色相のイ
ンキが混合したものであつて、色のくすんだ廃イ
ンキ中にはカーボンブラツクからなる黒インキ
や、フタロシアニンブルーからなる青インキが含
まれている。 上記の廃インキから顔料、溶剤等の有価物を回
収することは困難で、従来は、殆んどが焼却ある
いは投棄され、まれに廃インキ中に熱風、蒸気等
を注入して溶剤を放散させ、凝縮器等により回収
することもあつたが、充分な回収を行うことはで
きなかつた。 本発明者等は、廃インキから顔料や溶剤等の有
価物を回収し、しかも回収顔料の再利用度を高め
るべく、色のくすみの原因となるカーボンブラツ
クや青色顔料(フタロシアニンブルー)を除去
し、赤、黄、茶色等の色相の鮮やかな顔料を回収
する方法について研究を重ねた結果、次のような
知見を得た。 先ず、表1に示したインキに使用される顔料粒
子は、表2に示すように溶剤の種類によつて異な
つた分散性を示すこと。
[Table] It goes without saying that appropriate additives such as solvents, resins, and plasticizers are used depending on the type of pigment mentioned above. The hues of new inks are broadly classified into red, blue, yellow, white, and black, and depending on the purpose, they are used alone or in combination of two or more colors. By the way, ink that has become black and dull and can no longer be used, as well as waste liquid after cleaning printing machines, etc.
A large amount of waste ink is discharged from ink manufacturing processes, printing factories, etc., and each waste ink is a mixture of inks of various hues, and the dull colored waste ink includes black ink made of carbon black, Contains blue ink consisting of phthalocyanine blue. It is difficult to recover valuable materials such as pigments and solvents from the above waste ink, and conventionally, most of it has been incinerated or dumped, and in rare cases, hot air, steam, etc. have been injected into the waste ink to dissipate the solvent. , recovery using a condenser or the like was possible, but sufficient recovery could not be achieved. The present inventors recovered valuable materials such as pigments and solvents from waste ink, and in order to increase the degree of reuse of the recovered pigments, we removed carbon black and blue pigments (phthalocyanine blue) that cause dull colors. As a result of repeated research on methods for recovering pigments with vivid hues such as red, yellow, and brown, the following findings were obtained. First, the pigment particles used in the inks shown in Table 1 show different dispersibility depending on the type of solvent, as shown in Table 2.

【表】【table】

【表】 次に、前記したように顔料粒子をインキに使用
する際には樹脂(第1図中の2)を介在させる
が、この樹脂の種類によつても、表2の分散性は
次のように異なつてくること。 (1) トルエン、キシレン等の芳香族炭化水素は、
表2に示すようにいずれの顔料も分散せず、沈
降する傾向にあり、しかも介在樹脂の種類にか
かわらず、この傾向は変わらない。 (2) メチルセロソルブ等のエーテル類、シクロヘ
キサノン等のケトン類は、表2に示すようにい
ずれの顔料も良く分散し、しかも介在樹脂の種
類にかかわらず、この傾向は変わらない。 (3) 酢酸エチル等のエステル類、メチルアルコー
ル、エチルアルコール、イソプロピルアルコー
ル等のアルコール類は、表2に示すように顔料
の種類によつて分散性に選択性を示し、しかも
介在樹脂の種類によつても、例えば、 メチルアルコール、エチルアルコール: 介在樹脂がアルキツド樹脂の場合、これら
のアルコールはアルキツド樹脂を溶解する作
用がないため、顔料の種類にかかわらず、分
散性は悪い、 介在樹脂がニトロセルロースの場合は、こ
れらのアルコールはニトロセルロースを溶解
する作用があるため、表2と同様の分散性を
示す、 イソプロピルアルコール: 介在樹脂がアルキツド樹脂、ニトロセルロ
ースいずれの場合も、イソプロピルアルコー
ルはこれらの樹脂を溶解する作用がないた
め、顔料の種類にかかわらず分散性は悪い、 酢酸エチル: 介在樹脂がアルキツド樹脂、ニトロセルロ
ースいずれの場合も、酢酸エチルはこれらの
樹脂を溶解する作用があるため、表2と同様
の分散性を示す、 のように分散性に選択性を示す。 (4) 青色顔料(フタロシアニンブルー)およびカ
ーボンブラツクは、いずれの溶剤にもやや分散
し易い傾向がある。 更に、廃インキから顔料を回収し、再インキ化
して再使用する際、回収顔料中に上記のニトロセ
ルロース類やアルキツド樹脂類等の樹脂類が多く
含まれると印刷適性上不具合が生じるので、顔料
を回収する工程で、これら樹脂類を分離する必要
がある。一方、顔料粒子の分離の面からすれば、
顔料の凝集が促進され粒子径が大きくなる程、分
離が容易になる。これらを同時に満足させるため
には、顔料分散性の良い溶剤と悪い溶剤とを混合
して用いればよいこと。 すなわち、溶剤中でのインキ顔料の分散・凝集
性と上記樹脂類(主としてニトロセルロース)の
間には、第2図に示すような関連性があることを
実験の結果確めた。第2図から明らかなように、
顔料分散性の悪い溶剤は、ニトロセルロースの溶
解性に乏しいため、この溶剤で回収した顔料中に
は多くの樹脂類が残存して顔料の再利用には不具
合である。ただし、この場合、同図から明らかな
ように、顔料の凝集性は良いので、溶剤から顔料
を分離することは容易である。一方、顔料分散性
の良い溶剤は、同図から明らかなように、ニトロ
セルロースの溶解性が良いので、廃インキ中のニ
トロセルロース等の樹脂類は溶剤側へ移行し、こ
の溶剤で回収した顔料中には樹脂類は含まれな
い。ただし、この溶剤は、顔料の分散性が良い反
面、凝集性が悪いため、顔料は微細粒子となつて
分散してしまい、溶剤からの顔料分の分離は困難
となる。従つて、顔料分散性の良い溶剤と悪い溶
剤を混合して用いれば、顔料の凝集が促進され、
溶剤からの分離が容易となり、しかも樹脂類がか
なり除去された顔料が回収できるのである。 本発明は、以上の知見に基づいてなされたもの
であり、更に本発明では処理の容易さ、および装
置の小型化を図るべく、廃インキ中の夾雑物の除
去と、廃インキの濃縮を前処理として行うと共
に、顔料分離後の液から溶剤回収を行うものであ
る。 すなわち本発明は、廃インキから有価物を回収
する方法において、 (a) 廃インキを50メツシユ以上のフイルタからな
る過器に通し、夾雑物を除去する工程、 (b) 夾雑物を除去した廃インキを減圧蒸発器にて
濃縮する工程、 (c) 濃縮した廃インキを冷却し、その後顔料分散
性の悪い溶剤と良い溶剤を混合した溶剤と混
合、分散する工程、 (d) 上記溶剤と混合、分散された廃インキを遠心
分離器で固液分離し、次いで固形物から顔料を
回収する一方、分離液から溶剤を回収する工
程、 からなることを特徴とする廃インキからの有価物
回収方法に関するものである。 以下、添付図面を参照して本発明方法を詳細に
説明する。 第3図は本発明方法の一実施態様例を示すフロ
ーシートである。 第3図において、印刷機から発生する廃インキ
は、印刷工程にもとづいて間欠的に発生するた
め、一旦廃インキ貯留タンク1に入れられる。次
いで含まれ砂、紙屑、錆等の印刷適性を失なう原
因となる夾雑物を過分離するため過器2に送
る。該過器2は、次のような実験の結果、50メ
ツシユ以上のフイルタで構成されていればよいこ
とが確認されている。 すなわち、メツシユの異なるSUS304製の金網
フイルターを用いて夾雑物の除去効果を調べたと
ころ、第4図の結果が得られた。同図から明らか
なように、廃インキ中の夾雑物を除去するには、
50以上のメツシユ、好ましくは100〜200メツシユ
の範囲にあるフイルターを使用するのがよいこと
が判る。なおフイルターの材質は、廃インキのPH
が5〜7とやや酸性側にあることから、腐食を考
慮してSUS製を使用するのがよい。 過器2を出た廃インキは、ポンプ3により廃
インキ濃縮器4に送る。ここでは主として低沸点
溶剤を蒸発させ、通常1/2〜1/5に減容する。この
廃インキ濃縮器4は、減容による装置の小型化を
指向すると共に、次工程(顔料分散工程)におい
て最適溶剤組成となるよう調合できる範囲の溶剤
成分に置き代えるための準備操作の一段階であ
る。なお、廃インキを濃縮していくと、インキの
粘度が増大し、以降の取扱いが難しくなる。従つ
て、濃縮廃インキの粘度は、輸送、取扱い等を考
慮すると、150〜200(センチポイズ)が操作可能
な粘度の上限であることが確められている。第5
図は廃インキ中の顔料濃度と廃インキの粘度の関
係の一例を示す図表である。同図を参考にして廃
インキの濃縮度を決定すればよい。 また、廃インキ濃縮器4では、顔料の加熱によ
る変質、混合されている添加剤や樹脂の内壁への
固結を防止するため、大きな熱変化、温度差を与
えないよう減圧蒸発方式とすると共に、リボイラ
5と廃インキ濃縮器4との間の液移動方式とす
る。更に、リボイラ5は、上記の変質、内壁への
固結等を防止するために加熱体と壁面および液と
の温度差を小さくすべくライン5′からの温水に
よる加熱方式とする。このリボイラ5と上記の減
圧蒸発方式の廃インキ濃縮器4間を廃インキが流
動することにより、廃インキの均一化、混合効
果、固結・閉塞防止等に好結果が与えられる。 廃インキ濃縮器4を出た廃インキは、流量制御
装置6を経て、冷却器7で一旦室温近くまで降温
した後、分散槽8へ入る。分散槽8では、最適な
分散溶剤組成、すなわち顔料分散性の良い溶剤と
顔料分散性が悪く凝集効果のある溶剤を廃インキ
の性状に応じて、それぞれ溶剤タンク9と溶剤タ
ンク10とから一定量かつ一定割合で供給し、混
合タンク11で充分混合した後、加え、撹拌また
は液循環方式によつて廃インキと充分混合接触さ
せ、顔料粒子の分離性を良くすると共に、顔料粒
子に吸着されている樹脂、添加剤等を解離、溶出
させる。この時、色のくすみの原因となるカーボ
ンブラツクや青色顔料は、前記したように、顔料
分散性の悪い溶剤、良い溶剤のいずれにも余り分
散性を失うことがないので、溶剤側に残る。 上記の顔料分散性の悪い溶剤としては、前記し
た知見から明らかなように、トルエン、キシレン
等の芳香族炭化水素が用いられ、顔料分散性の良
い溶剤としては、シクロヘキサノン、メチルイソ
ブチルケトン等のケトン類、メチルセロソルブ等
のエーテル類が用いられる。 これら顔料分散性の悪い溶剤と良い溶剤との混
合割合は、容量比で70/30〜0/100程度とすること
が望ましい。その理由は次の通りである。 顔料分散性の良い溶剤と悪い溶剤との混合割合
は、回収顔料の純度に影響を及ぼすフアクターと
なる。第6図にこの混合溶剤の組成割合と回収顔
料の純度との関係を示す。同図から明らかなよう
に、回収顔料の純度を95%以上とする場合、顔料
分散性の悪い溶剤/顔料分散性の良い溶剤の組成
割合は、容量比で概略70/30〜0/100、好ましくは
70/30〜10/90であることが判る。 そして、上記混合溶剤の廃インキへの添加割合
は、第7図に示す廃インキからの顔料分離効率と
混合溶剤/廃インキ比(容量比)との関係の一例
から、混合溶剤/廃インキ=2〜3(容量比)が
好ましいことが判る。 分散槽8を出た廃インキと上記溶剤との混合物
は、次いで遠心分離器12へ送られ、1000G以
上、30秒以上の分離操作が行われる。第8図に顔
料分離率と遠心分離器の遠心効力の関係の一例を
示す。同図から明らかなように廃インキから効率
的に顔料を分離回収するには、遠心分離器の遠心
効力は1000G以上、好ましくは2000G以上である
ことがわかる。なお、遠心分離に先立つて、色の
くすみの原因となる顔料を除去するために、静
置、傾瀉を行うことが好ましいことは言うまでも
ない。 遠心分離器12で分離された固形分は乾燥器1
3で一定量の溶剤を除去した後、ライン19から
回収顔料として取出し、再利用する。 一方、分離液は、分離液タンク14に入り、予
熱器15を経て、蒸発器16に送る。蒸発器16
では、リボイラ17で分離液を加熱すると共に、
真空ポンプ18で蒸発器16内を減圧にして分離
液中の溶剤の蒸発を促進させ、溶剤をライン20
から回収し、再利用する。なお、分離液中に残る
インキ成分のうち、樹脂、添加剤等は、蒸発器1
6の底部に濃縮されるので、廃棄処理するか、燃
料油等に混ぜて燃焼させ、一部を熱として回収す
る。 なお、本発明方法は廃インキからの顔料の回収
の他、顔料と類似の性質をもつ染料の分離、回収
にも適用し得るものである。 実施例 表3に示した性状を有する廃インキ1を200
メツシユの金網フイルタに通して砂、紙くず、鉄
さび等を除去した後、70℃にて系内圧力100mmHg
で2時間減圧蒸発して、インキ中の顔料が15wt
%になるまで濃縮し、つぎにトルエン/酢酸エチ
ルの容量比が50/50からなる希釈溶剤を濃縮した
廃インキ容量に対して3倍量添加したのち激しく
かきまぜる。その後、この混合液を遠心分離機に
かけ、2200Gの遠心効果を与えて、5分間回転
し、顔料固形分を液相から分離して、約60gの顔
料を回収した。 このようにして回収した顔料は鮮やかな色相を
有し、再インキ化した結果、インキとして再利用
できることが判明した。 表―3 廃インキ性状 色 相:焦茶 比 重:0.94 粘 度:33cs(Cat20℃) 顔料含有量:7wt% 溶剤含有量:88.5wt% 溶剤組成: メタノール 1.1wt% 酢酸エチル 18.4 イソプロパノール 16.2 トルエン 48.1 酢酸ブチル 0.6 キシレン 5.7 メチルセロソルブ 6.2 シクロヘキサノン 3.8
[Table] Next, as mentioned above, when pigment particles are used in ink, a resin (2 in Figure 1) is used, but depending on the type of resin, the dispersibility in Table 2 is as follows. to come in different ways. (1) Aromatic hydrocarbons such as toluene and xylene are
As shown in Table 2, none of the pigments is dispersed and tends to settle, and this tendency does not change regardless of the type of intervening resin. (2) With ethers such as methyl cellosolve and ketones such as cyclohexanone, all pigments are well dispersed as shown in Table 2, and this tendency does not change regardless of the type of intervening resin. (3) As shown in Table 2, esters such as ethyl acetate, alcohols such as methyl alcohol, ethyl alcohol, and isopropyl alcohol exhibit selectivity in dispersibility depending on the type of pigment, and also depending on the type of intervening resin. For example, methyl alcohol, ethyl alcohol: If the intervening resin is an alkyd resin, these alcohols have no effect of dissolving the alkyd resin, so regardless of the type of pigment, the dispersibility is poor. In the case of cellulose, these alcohols have the effect of dissolving nitrocellulose, so they show the same dispersibility as shown in Table 2. Isopropyl alcohol: Regardless of whether the intervening resin is an alkyd resin or nitrocellulose, isopropyl alcohol has the effect of dissolving nitrocellulose. Ethyl acetate: Ethyl acetate has the effect of dissolving these resins, regardless of whether the intervening resin is alkyd resin or nitrocellulose. Shows dispersibility similar to Table 2, and shows selectivity in dispersion as shown in Table 2. (4) Blue pigments (phthalocyanine blue) and carbon black tend to be somewhat easily dispersed in any solvent. Furthermore, when collecting pigments from waste ink and reusing them by remaking them into ink, if the recovered pigments contain a large amount of resins such as the above-mentioned nitrocelluloses and alkyd resins, printing problems will occur. It is necessary to separate these resins in the process of recovering them. On the other hand, from the perspective of separation of pigment particles,
As pigment aggregation is promoted and the particle size becomes larger, separation becomes easier. In order to satisfy these requirements at the same time, it is sufficient to use a mixture of a solvent with good pigment dispersibility and a solvent with poor pigment dispersibility. That is, as a result of experiments, it was confirmed that there is a relationship as shown in FIG. 2 between the dispersion/coagulation properties of ink pigments in a solvent and the above-mentioned resins (mainly nitrocellulose). As is clear from Figure 2,
Solvents with poor pigment dispersibility have poor solubility of nitrocellulose, and therefore, a large amount of resin remains in the pigment recovered with this solvent, which is a problem in reusing the pigment. However, in this case, as is clear from the figure, the pigment has good cohesiveness, so it is easy to separate the pigment from the solvent. On the other hand, as is clear from the figure, solvents with good pigment dispersibility have good solubility of nitrocellulose, so resins such as nitrocellulose in waste ink migrate to the solvent side, and the pigments recovered with this solvent It does not contain resins. However, although this solvent has good pigment dispersibility, it has poor aggregation properties, so the pigment becomes fine particles and disperses, making it difficult to separate the pigment from the solvent. Therefore, if a mixture of a solvent with good pigment dispersibility and a solvent with poor pigment dispersibility is used, the aggregation of the pigment will be promoted.
Separation from the solvent becomes easy, and the pigment can be recovered from which a considerable amount of resin has been removed. The present invention has been made based on the above findings, and furthermore, in order to facilitate processing and downsize the device, the present invention removes impurities from waste ink and concentrates the waste ink beforehand. This is done as a treatment and also to recover the solvent from the liquid after pigment separation. That is, the present invention provides a method for recovering valuables from waste ink, which includes the following steps: (a) passing the waste ink through a filter consisting of 50 meshes or more to remove impurities; A process of concentrating the ink in a vacuum evaporator; (c) A process of cooling the concentrated waste ink and then mixing and dispersing it with a solvent that is a mixture of a solvent with poor pigment dispersibility and a solvent with good pigment dispersibility; (d) A process of mixing with the above solvent. A method for recovering valuables from waste ink, comprising the following steps: separating the dispersed waste ink into solid and liquid using a centrifugal separator, and then recovering the pigment from the solid matter while recovering the solvent from the separated liquid. It is related to. Hereinafter, the method of the present invention will be explained in detail with reference to the accompanying drawings. FIG. 3 is a flow sheet showing an embodiment of the method of the present invention. In FIG. 3, waste ink generated from a printing machine is temporarily put into a waste ink storage tank 1 because it is generated intermittently based on the printing process. Next, it is sent to a filter 2 in order to over-separate impurities such as sand, paper waste, rust, etc. that cause a loss of printing suitability. As a result of the following experiment, it has been confirmed that the filter 2 only needs to be composed of a filter having 50 meshes or more. That is, when the effect of removing impurities was investigated using wire mesh filters made of SUS304 with different meshes, the results shown in FIG. 4 were obtained. As is clear from the figure, in order to remove impurities from waste ink,
It has been found that it is better to use a filter with a mesh size of 50 or more, preferably in the range of 100 to 200 meshes. The filter material is based on the pH of the waste ink.
Since it is on the acidic side at 5 to 7, it is better to use SUS in consideration of corrosion. The waste ink leaving the filter 2 is sent to a waste ink concentrator 4 by a pump 3. Here, the low boiling point solvent is mainly evaporated, and the volume is usually reduced to 1/2 to 1/5. This waste ink concentrator 4 is intended to reduce the size of the device by reducing its volume, and is a step in the preparation operation for replacing the solvent components with a range that can be blended to achieve the optimum solvent composition in the next process (pigment dispersion process). It is. Note that as waste ink is concentrated, the viscosity of the ink increases, making subsequent handling difficult. Therefore, it has been confirmed that the viscosity of concentrated waste ink is 150 to 200 (centipoise) as the upper limit of the operable viscosity, considering transportation, handling, etc. Fifth
The figure is a chart showing an example of the relationship between the pigment concentration in waste ink and the viscosity of waste ink. The concentration level of waste ink can be determined by referring to the figure. In addition, the waste ink concentrator 4 uses a reduced pressure evaporation method to prevent large thermal changes and temperature differences, in order to prevent the pigment from changing due to heating and the mixed additives and resin from solidifying on the inner wall. , the liquid is transferred between the reboiler 5 and the waste ink concentrator 4. Further, the reboiler 5 is heated by hot water from the line 5' in order to reduce the temperature difference between the heating element, the wall surface, and the liquid in order to prevent the above-mentioned deterioration and solidification on the inner wall. By flowing the waste ink between the reboiler 5 and the waste ink concentrator 4 of the reduced-pressure evaporation method, good results are achieved in terms of uniformity of the waste ink, mixing effect, and prevention of caking and clogging. The waste ink leaving the waste ink concentrator 4 passes through a flow rate control device 6 and is once cooled down to near room temperature in a cooler 7, and then enters a dispersion tank 8. In the dispersion tank 8, a certain amount of the optimal dispersion solvent composition, that is, a solvent with good pigment dispersibility and a solvent with poor pigment dispersibility and a flocculating effect, is supplied from the solvent tank 9 and the solvent tank 10, respectively, depending on the properties of the waste ink. After supplying the ink at a constant rate and thoroughly mixing it in the mixing tank 11, the ink is added and thoroughly mixed and brought into contact with the waste ink by stirring or liquid circulation to improve the separation of the pigment particles and prevent adsorption to the pigment particles. dissociates and elutes resins, additives, etc. At this time, carbon black and blue pigments, which cause dullness of color, remain on the solvent side because they do not lose much of their dispersibility in either solvents with poor pigment dispersibility or solvents with good pigment dispersibility, as described above. As is clear from the above findings, aromatic hydrocarbons such as toluene and xylene are used as solvents with poor pigment dispersibility, while ketones such as cyclohexanone and methyl isobutyl ketone are used as solvents with good pigment dispersibility. esters, methyl cellosolve, and other ethers are used. The mixing ratio of these solvents with poor pigment dispersibility and solvents with good pigment dispersibility is preferably about 70/30 to 0/100 in terms of volume ratio. The reason is as follows. The mixing ratio of a solvent with good pigment dispersibility and a solvent with poor pigment dispersibility is a factor that affects the purity of the recovered pigment. FIG. 6 shows the relationship between the composition ratio of this mixed solvent and the purity of the recovered pigment. As is clear from the figure, when the purity of the recovered pigment is 95% or more, the composition ratio of solvent with poor pigment dispersibility/solvent with good pigment dispersibility is approximately 70/30 to 0/100 in terms of volume ratio. Preferably
It turns out that it is 70/30 to 10/90. The addition ratio of the mixed solvent to the waste ink can be determined from the example of the relationship between the pigment separation efficiency from the waste ink and the mixed solvent/waste ink ratio (volume ratio) shown in FIG. It turns out that 2 to 3 (capacity ratio) is preferable. The mixture of waste ink and the above solvent that has come out of the dispersion tank 8 is then sent to a centrifugal separator 12, where a separation operation is performed at 1000 G or more for 30 seconds or more. FIG. 8 shows an example of the relationship between the pigment separation rate and the centrifugal efficiency of the centrifugal separator. As is clear from the figure, in order to efficiently separate and recover pigments from waste ink, the centrifugal force of the centrifugal separator is 1000 G or more, preferably 2000 G or more. It goes without saying that prior to centrifugation, it is preferable to allow the mixture to stand and decant in order to remove pigments that cause dullness of color. The solid content separated by the centrifugal separator 12 is transferred to the dryer 1
After removing a certain amount of the solvent in step 3, it is taken out as a recovered pigment through line 19 and reused. On the other hand, the separated liquid enters the separated liquid tank 14, passes through the preheater 15, and is sent to the evaporator 16. Evaporator 16
Now, while heating the separated liquid in the reboiler 17,
The vacuum pump 18 reduces the pressure inside the evaporator 16 to promote evaporation of the solvent in the separated liquid, and the solvent is transferred to the line 20.
Collect from and reuse. Of the ink components remaining in the separated liquid, resins, additives, etc. are removed from the evaporator 1.
Since it is concentrated at the bottom of the tank, it is either disposed of or mixed with fuel oil and burned, and a portion is recovered as heat. The method of the present invention can be applied not only to the recovery of pigments from waste ink but also to the separation and recovery of dyes having similar properties to pigments. Example Waste ink 1 having the properties shown in Table 3 was
After passing through a mesh wire mesh filter to remove sand, paper scraps, iron rust, etc., the system internal pressure is 100 mmHg at 70℃.
After evaporating under reduced pressure for 2 hours, the pigment in the ink was reduced to 15wt.
%, and then add a dilution solvent consisting of toluene/ethyl acetate in a volume ratio of 50/50 in an amount three times the volume of the concentrated waste ink, and stir vigorously. Thereafter, this mixed solution was applied to a centrifuge and rotated for 5 minutes under a centrifugal effect of 2200 G to separate the pigment solids from the liquid phase, and about 60 g of pigment was recovered. It was found that the pigment recovered in this way had a bright hue and could be reused as ink by remaking it into ink. Table-3 Waste ink properties Color Phase: Dark brown Specific gravity: 0.94 Viscosity: 33cs (Cat 20℃) Pigment content: 7wt% Solvent content: 88.5wt% Solvent composition: Methanol 1.1wt% Ethyl acetate 18.4 Isopropanol 16.2 Toluene 48.1 Acetic acid Butyl 0.6 Xylene 5.7 Methyl cellosolve 6.2 Cyclohexanone 3.8

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

第1図はインキ中の顔料粒子の分散状況を模式
的に示す図、第2図は顔料分散性の良い溶剤と悪
い溶剤中での顔料の分散性および凝集性とニトロ
セルロースの溶解性の関係を示す図表、第3図は
本発明方法の一実施態様例を示すフローシート、
第4図はフイルタのメツシユと廃インキ中夾雑物
の除去率の関係を示す図表、第5図は廃インキ濃
縮時の廃インキ中の顔料濃度と廃インキの粘度の
関係を示す図表、第6図は顔料分散性の良い溶剤
と悪い溶剤との混合溶剤の組成と回収顔料の純度
の関係を示す図表、第7図は上記混合溶剤/廃イ
ンキ比と廃インキからの顔料分離効率の関係を示
す図表、第8図は顔料分散性の良い溶剤と悪い溶
剤との混合溶剤が添加された廃インキを遠心分離
する際の顔料分離率と遠心力の関係を示す図表で
ある。
Figure 1 is a diagram schematically showing the dispersion status of pigment particles in ink, and Figure 2 is the relationship between the dispersibility and aggregation of pigments and the solubility of nitrocellulose in solvents with good and poor pigment dispersibility. 3 is a flow sheet showing an embodiment of the method of the present invention,
Figure 4 is a chart showing the relationship between filter mesh and the removal rate of impurities in waste ink, Figure 5 is a chart showing the relationship between pigment concentration in waste ink and viscosity of waste ink when waste ink is concentrated, The figure shows the relationship between the composition of a mixed solvent of a solvent with good pigment dispersibility and a solvent with bad pigment dispersibility and the purity of the recovered pigment. Figure 7 shows the relationship between the mixed solvent/waste ink ratio and the efficiency of pigment separation from waste ink. The chart shown in FIG. 8 is a chart showing the relationship between the pigment separation rate and the centrifugal force when waste ink to which a mixed solvent of a solvent with good pigment dispersibility and a solvent with poor pigment dispersibility is added is centrifuged.

Claims (1)

【特許請求の範囲】 1 廃インキから有価物を回収する方法におい
て、 (a) 廃インキを50メツシユ以上のフイルタからな
る過器に通し、夾雑物を除去する工程、 (b) 夾雑物を除去した廃インキを減圧蒸発器にて
濃縮する工程、 (c) 濃縮した廃インキを冷却し、その後顔料分散
性の悪い溶剤と良い溶剤を混合した溶剤と混
合、分散する工程、 (d) 上記溶剤と混合、分散された廃インキを遠心
分離器で固液分離し、次いで固形物から顔料を
回収する一方、分離液から溶剤を回収する工
程、 からなることを特徴とする廃インキからの有価物
回収方法。
[Claims] 1. A method for recovering valuables from waste ink, including (a) passing the waste ink through a filter consisting of a filter of 50 or more meshes to remove impurities; (b) removing impurities. (c) the process of cooling the concentrated waste ink and then mixing and dispersing it with a mixture of a solvent with poor pigment dispersibility and a solvent with good pigment dispersibility; (d) the above solvent A process of separating solid-liquid waste ink mixed and dispersed with a centrifuge using a centrifugal separator, and then recovering pigment from the solid matter and recovering a solvent from the separated liquid. Collection method.
JP56179012A 1981-11-10 1981-11-10 Recovery of valuable from waste ink Granted JPS5881410A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP56179012A JPS5881410A (en) 1981-11-10 1981-11-10 Recovery of valuable from waste ink

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP56179012A JPS5881410A (en) 1981-11-10 1981-11-10 Recovery of valuable from waste ink

Publications (2)

Publication Number Publication Date
JPS5881410A JPS5881410A (en) 1983-05-16
JPS6256763B2 true JPS6256763B2 (en) 1987-11-27

Family

ID=16058568

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56179012A Granted JPS5881410A (en) 1981-11-10 1981-11-10 Recovery of valuable from waste ink

Country Status (1)

Country Link
JP (1) JPS5881410A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5199981A (en) * 1991-01-18 1993-04-06 Sicpa Holding Sa Pigment compositions including intaglio printing ink waste

Also Published As

Publication number Publication date
JPS5881410A (en) 1983-05-16

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