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JPS6146033B2 - - Google Patents
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JPS6146033B2 - - Google Patents

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Publication number
JPS6146033B2
JPS6146033B2 JP54132395A JP13239579A JPS6146033B2 JP S6146033 B2 JPS6146033 B2 JP S6146033B2 JP 54132395 A JP54132395 A JP 54132395A JP 13239579 A JP13239579 A JP 13239579A JP S6146033 B2 JPS6146033 B2 JP S6146033B2
Authority
JP
Japan
Prior art keywords
oil
quaternary ammonium
cleaning
ammonium salt
carbon atoms
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
JP54132395A
Other languages
Japanese (ja)
Other versions
JPS5657899A (en
Inventor
Noboru Suzuki
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.)
Duskin Franchise Co Ltd
Original Assignee
Duskin Franchise Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Duskin Franchise Co Ltd filed Critical Duskin Franchise Co Ltd
Priority to JP13239579A priority Critical patent/JPS5657899A/en
Publication of JPS5657899A publication Critical patent/JPS5657899A/en
Publication of JPS6146033B2 publication Critical patent/JPS6146033B2/ja
Granted legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Lubricants (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)

Description

【発明の詳細な説明】 本発明は高沸点汚油の再生回収法に関し、より
詳細には、使用済清掃用含油繊維製品をダスト吸
着用油剤を洗浄液として洗浄して得られる汚濁成
分及びノニオン界面活性剤を含有する高沸点汚油
に、相分離した水の実質上非存在下に、下記式 式中、R1,R2,R3の各々は炭素数2乃至5の
アルキル基であり、R4は炭素数2乃至5のアル
キル基若しくはアルキル部分の炭素数が2以上で
あるアラールキル基でありXはノニオンである、 で表される第4級アンモニウム塩を0.5乃至10重
量%の量で添加し、50乃至95℃の温度で加熱撹拌
し、放置して汚濁物質を凝集沈殿させ、上澄清浄
油を分取することを特徴とする高沸点汚油の再生
回収法に関する。 使用済みの含油繊維清掃材料は、ダスト吸着剤
としてのカチオン性、ノニオン性或は両性系界面
活性剤と不揮発性の鉱物油乃至は合成油の組み合
わせを含有するほかに、多量の泥、ホコリ、その
他の無機性或は有機性の汚れ、カビ、細菌類等が
付着している。かくしてこの清掃材料の再生洗浄
に際して排出される廃水は、乳化した状態の油分
を極めて高濃度で含有し、COD及びSS等の汚濁
成分も高濃度で含有し、その廃水処理が困難であ
ると共に、廃水処理に際して、1次処理更に2次
処理等の多数の工程を要すると共に、その処理コ
ストもかなり高価なものとなつている。 このような欠点を解消するために、使用済みの
汚れた清掃用含油繊維製品を、繊維にホコリを吸
着させるためのダスト吸着性油剤そのものを用い
て洗浄を行つた後、残留の油剤量を適当な範囲に
調整することによつて、洗浄と含油の両工程を一
貫して行うことが既に提案されている(特公昭53
−37471号公報)。 この方法は、上述した如く、洗浄と含油との両
工程が一貫して行われ、更に洗浄後の廃水処理を
必要としない点で優れたものではあるが、洗浄操
作を反復するに従つて汚濁成分が油剤中に蓄積
し、この汚濁成分の除去が困難であるという問題
を生ずる。ダスト吸着用油剤は常態で不揮発生で
あることからも明らかな様に、高沸点であり、通
常のドライークリーニング溶剤の場合の様な簡単
な手段では蒸留による精製が困難である。またこ
の油剤は、高粘度であつて過による精製も比較
的困難であり、仮に過したとしても含有される
汚濁成分を充分に除去することは実質上不可能で
ある。更に吸着性高分子物質或いは活性炭等を加
えて脱色過する方法をこの汚染油に適用したと
しても前述した過の困難性の問題の他に吸着済
みの高分子物質や活性炭を再生することが容易で
なく、経済性の面で不利を免れない。 本発明者等は、使用済清掃用含油繊維製品の洗
浄により得られた汚染油の様に汚濁成分及び界面
活性剤を含有する高沸点油に、特定の第4級アン
モニウム塩を添加混合し、この混合物を50乃至95
℃の温度に加温する時には汚濁成分が極めて効果
的に凝集沈降、分離され、清浄化された油分が上
澄として有効に回収されることを見出した。 本発明は、この様に汚濁成分及びノニオン界面
活性剤を含有する高沸点汚油に短鎖アルキル基含
有第4級アンモニウム塩を添加し加熱撹拌すると
水の非存在下においても高沸点汚油中の汚濁成分
が選択的に凝集沈降するという新規短見に基づく
ものである。 清掃用含油繊維には、この繊維の吸湿率に応じ
た水分が含有されており、この水分等が油中に移
行することがあつたとしても、この水分は油中に
溶解した状態で存在しており、油から相分離した
形で存在することはない。この水分量は高々5%
以内である。 本発明において、油中において汚濁成分の凝集
沈降が生ずる理由は十分に明らかではないが、前
述した短鎖アルキル基含有第4級アンモニウム塩
が油中で負に帯電している汚濁成分と結合し、油
中に存在するノニオン系界面活性剤の作用で凝集
沈降するものと思われる。この推定は、ノニオン
系界面活性剤を含有しない高沸点汚油に対して、
短鎖アルキル基含有第4級アンモニウム塩を添加
しても汚濁成分の凝集沈降が生じないという事実
ともよく符合している。 本発明によれば更に、凝集沈降に使用した第4
級アンモニウム塩は沈降汚濁成分を水で抽出し、
必要によりそれ自体公知の濃縮法を適用すること
により再使用可能な形で容易に回収し得る。 本発明で対象とする高沸点油としては、鉱物
油、合成潤滑油或はこれらの混合物から成り、ダ
スト吸着用油剤としての適性を有するものが何れ
も使用される。これらの油剤は、常態(20℃、1
気圧)で不揮発性(不乾燥性)であり、100〓で
測定して8乃至100cP、好適には10乃至90cPの粘
度を有している。好適には、前記油剤のアニリン
点は20乃至80、好ましくは40〜60であり、発火点
は少くとも130℃であり、沸点は少くとも280℃で
あり、更に70℃で測定して15mmHgよりも低い蒸
気圧を有する。鉱物油は、パラフイン系炭化水
素、ナフテン系炭化水素、芳香族炭化水素或はこ
れらの混合物から成つていることが出来、その適
当な例は、液状パラフイン、スピンドル油、マシ
ン油、冷凍機油及び他の石油系潤滑油である。合
成潤滑油としては、ポリオレフイン油(α−オレ
フイン油)、ポリグリコール油、ポリブテン油、
アルキルベンゼン油、ジエステル油、ポリオール
エステル油、ポリフエニルエーテル油、イソパラ
フイン油等を挙げることができる。 清掃用含油繊維製品の場合には、上述した油剤
に加えて、前記油剤にダスト吸着性を賦与し、或
は更に自己乳化性、自己吸尽性を賦与する目的
で、カチオン系界面活性剤を非イオン界面活性剤
との組み合わせ、或は第4級アンモニウム基或は
アミノ基の様なカチオン活性基とカルボン酸又は
スルホン酸基の様なアニオン活性基とを有する両
性界面活性剤乃至は前記カチオン活性基とポリエ
チレンオキサイド基の様な非イオン活性基とを含
む両性界面活性剤が含有されている。 更に清掃用含油繊維製品には、油剤の変質を防
止するための酸化防止剤、カビや菌の増殖を防止
するための防カビ剤、抗菌剤等が含有されてお
り、これらの添加剤は、後述する洗浄及び脱油処
理に際して、洗浄媒体たる油剤中にその一部が移
行する。 使用済含油繊維の汚れは、前述した各種の汚れ
が複雑に混じつた状態で繊維に付着したり、吸着
したりしており、しかも長期間の使用乃至は放置
で繊維にこびりついた状態となつているものもあ
る。 このため、清掃用含油繊維製品の油剤そのもの
を洗浄媒体とした洗浄再生に際しては、洗浄力を
増強するために、非イオン界面活性剤、特にノニ
ルフエノール或は高級アルコールのエチレンオキ
サイド付加物からなる非イオン界面活性剤、就
中、エチレンオキサイドの平均付加モルが1乃至
10モルのものを添加する。添加量は、洗浄媒体た
る油剤に対して3乃至20重量%の範囲が好適であ
る。 洗浄機としては、市販の回転型ワツシヤーを用
いてもよいが、洗浄と脱油(油保持量の調節)が
可能なワツシヤー例えば、米国ワセツクス社製フ
ローテアなどがよい。洗浄は、常温において好適
に行われるが、場合により60乃至80℃の加温下に
30分乃至1時間行うことも出来る。繊維に残す油
剤量は、繊維基材の種類によつても相違するが、
繊維重量に対して12乃至30重量%、特に18乃至23
重量%の範囲が適当である。 洗浄後、回収される油剤は、まず粗い繊維くず
やゴミを金網を通して分離し、ついで必要により
酸性白土やケイソウ土等の過助剤を用いて過
を行つた後、本発明の再生処理に賦する。 本発明においては、前述した汚染油に一般式
()の第4級アンモニウム塩を0.5乃至10重量
%、特に望ましくは1乃至3重量%の量で添加す
ることが汚濁成分の凝集沈降を有効に行う上で重
要である。 まず、使用する第4級アンモニウム塩の分子中
のアルキル基は2乃至5の炭素数を有するもので
なければならない。陽イオン界面活性剤として一
般に使用されている長鎖アルキル基を有する第4
級アンモニウム塩、例えばセチルピリジウムクロ
ライド、トリオクチルメチルアンモニウムクロラ
イド、ジメチルジミリスチルベンジルアンモニウ
ムクロライド、ジメチルジステアリルアンモニウ
ムクロライド、ジメチルアルキルベンジルアンモ
ニウムクロライド、ジメチルジアルキルアンモニ
ウムクロライド等は、何れも汚染油中の汚濁成分
を凝集沈降させる能力を有していない。即ち、使
用済含油繊維製品の洗浄により得られた汚染油
は、褐色乃至黒色に汚濁しており、その吸光度は
一般に2.0以上である。この汚染油に上に例示し
た長鎖アルキル基を有する第4級アンモニウム塩
を添加した場合には、これらの汚濁成分の沈降は
全く起こらず、その処理液の吸光度は汚染油のま
まである。これに対して本発明に従い、アルキル
基の炭素数が2乃至5の範囲にある第4級アンモ
ニウム塩を添加すると汚濁成分が顕著に凝集沈降
するのであつてこの事実は後述する実施例から明
白であろう。尚、本発明に使用する第4級アンモ
ニウム塩においては、4個のアルキル基の内1個
のみがベンジル基の様なアラールキル基で置換さ
れていてもよい。 第4級アンモニウム塩のアニオンとしては、ハ
ライドイオン特にクロライドイオンが望ましい。
その適当な例は、テトラエチルアンモニウムクロ
ライド、テトラ−n−プロピルアンモニウムクロ
ライド、テトラ−nブチルアンモニウムクロライ
ド、テトラ−n−ペンチルアンモニウムクロライ
ド、テトラ−n−ブチルアンモニウムブロマイ
ド、テトラ−n−ブチルアンモニウムアイオダイ
ド、ベンジルトリ−n−ブチルアンモニウムクロ
ライド等であり、これらは単独でも2種以上の組
み合わせでも使用し得る。最も好適なものは、テ
トラ−n−ブチルアンモニウムクロライドであ
る。 第4級アンモニウム塩を添加した混合物は、50
乃至95℃、特に60乃至80℃の温度で加温撹拌し、
第4級アンモニウム塩を均一に分散させる。次い
でこの液を静置、放冷すると汚濁成分が凝集沈降
して、上層に清澄で殆んど透明な油分が分離す
る。この分離は1時間以内、特に30分以内に完了
する。しかしながら分離を促進するために遠心分
離操作を行うことも勿論可能である。 更に本発明によれば、凝集沈降剤として使用し
た前記第4級アンモニウム塩は、凝集沈降分離し
た汚濁物質層を水で5乃至10倍に稀釈し、50乃至
95℃に加温し、暫時放置するか、または5乃至10
倍に稀釈した後、食塩または芒硝等の無機塩類
を、稀釈した水の量に対して2乃至10%濃度にな
るように添加することにより前記第4級アンモニ
ウム塩の清澄な水溶液が得られる。この水溶液を
有機溶剤による抽出、或いは蒸発濃縮することに
より、再使用することが可能となる。 以下本発明方法の1つの実施態様を示す第1図
に従つて本発明を説明する。 汚染油A及び汚染油Aに対して1.5乃至10重量
%の量の凝集沈降剤Bを撹拌槽1にて50乃至95℃
の温度で加熱撹拌する。次にこの混合液Cを凝集
沈降槽3に移し、そこで放冷、放置する。暫時放
置した後上層に清澄な殆んど無色の汚濁成分の除
去された油層Dが得られる。この再生油層Dを撹
拌層4に移し、活性白土Gを添加、混合撹拌し、
これをプレコート過の操作に賦し、再生油とす
る。また凝縮沈殿槽にて凝縮沈殿した汚濁成分
(タール分)Eを水Fで5乃至10倍に稀釈し撹拌
槽6において50乃至90℃で混合撹拌する。ここで
必要とあらば、食塩或いは芒硝等の無機塩類を、
稀釈した水の量に対して3乃至10重量%添加、混
合し次の沈殿槽7で暫時放置することにより、汚
濁成分(タール分)を含む油層と前記第4級アン
モニウム塩を含む水層とに分離する。次に水層を
逆浸透や蒸発等の操作に賦することにより前記第
4級アンモニウム塩を回収し、再使用することが
できる。 以下に本発明を実施例で説明する。 実施例 1 使用済みの清掃用含油繊維製品(ダストコント
ロール製品)を、工業用パラフイン油でクリーニ
ングした際に回収し、ケイソウ土過した洗浄油
を汚油試料とした。 この洗浄油は、工業用パラフインを主体とし、
ノニオン系界面活性剤7重量%、酸化防止剤0.35
重量%、防カビ剤1.0重量%、抗菌剤0.15重量
%、及び動植物油脂、ワツクス、グリース、微細
な土砂等を数%含有している。 汚染液に凝集剤としてテトラ−n−ブチルアン
モニウムクロライドを3重量%加え80℃に加温撹
拌し、凝集剤が均一分散した後、加温撹拌を停止
し、1時間程静置放冷した。その上澄液について
評価を表−1に示す。 【表】
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for regenerating and recovering high-boiling point polluted oil, and more specifically, the present invention relates to a method for regenerating and recovering high-boiling point polluted oil, and more specifically, to remove pollutant components and nonionic interfaces obtained by washing used oil-impregnated cleaning fiber products with a dust-adsorbing oil agent as a cleaning liquid. The following formula is applied to a high boiling point dirty oil containing an activator in the substantial absence of phase-separated water. In the formula, each of R 1 , R 2 , and R 3 is an alkyl group having 2 to 5 carbon atoms, and R 4 is an alkyl group having 2 to 5 carbon atoms or an aralkyl group whose alkyl moiety has 2 or more carbon atoms. A quaternary ammonium salt represented by X is a nonion is added in an amount of 0.5 to 10% by weight, heated and stirred at a temperature of 50 to 95°C, and left to coagulate and precipitate the pollutants. This invention relates to a method for recycling and recovering high-boiling point dirty oil, which is characterized by separating clear oil. Used oil-impregnated fiber cleaning materials contain a combination of cationic, nonionic, or amphoteric surfactants as dust adsorbents and nonvolatile mineral oils or synthetic oils, and also contain large amounts of dirt, dust, Other inorganic or organic dirt, mold, bacteria, etc. are attached. Thus, the wastewater discharged during the recycling and cleaning of cleaning materials contains an extremely high concentration of emulsified oil, and also contains pollutants such as COD and SS at a high concentration, making it difficult to treat the wastewater. Wastewater treatment requires many steps such as primary treatment and secondary treatment, and the cost of the treatment is also quite high. In order to eliminate these drawbacks, after cleaning used dirty cleaning oil-impregnated fiber products using the dust-absorbing oil agent itself, which is used to adsorb dust to the fibers, the amount of the remaining oil agent is removed to an appropriate level. It has already been proposed to perform both the cleaning and oil impregnation processes consistently by adjusting the adjustment within a certain range (Japanese Patent Publication No. 53).
-37471). As mentioned above, this method is superior in that both the cleaning and oil impregnation steps are performed consistently and does not require wastewater treatment after cleaning, but as the cleaning operation is repeated, it becomes contaminated. A problem arises in that components accumulate in the oil agent and it is difficult to remove these contaminating components. The oil agent for dust adsorption has a high boiling point, as is clear from the fact that it is non-volatile under normal conditions, and is difficult to purify by distillation using simple means such as the case with ordinary dry cleaning solvents. Furthermore, this oil has a high viscosity and is relatively difficult to purify by filtration, and even if it were to be filtrated, it is virtually impossible to sufficiently remove the contaminant components contained therein. Furthermore, even if a method of decolorizing the contaminated oil by adding an adsorbent polymer substance or activated carbon is applied to this contaminated oil, in addition to the above-mentioned problem of difficulty in filtration, it is easy to regenerate the adsorbed polymer substance or activated carbon. However, there are disadvantages in terms of economic efficiency. The present inventors added and mixed a specific quaternary ammonium salt to high-boiling point oil containing polluting components and surfactants, such as contaminated oil obtained by washing used oil-impregnated cleaning textile products, Add this mixture to 50 to 95
It has been found that when heated to a temperature of 0.degree. C., polluted components are very effectively coagulated and precipitated and separated, and the purified oil component is effectively recovered as a supernatant. The present invention shows that when a short-chain alkyl group-containing quaternary ammonium salt is added to high-boiling point foul oil containing polluting components and nonionic surfactants and the mixture is heated and stirred, even in the absence of water, the high-boiling point foul oil can be dissolved. This is based on the novel idea that pollutant components selectively coagulate and precipitate. Oil-impregnated fibers for cleaning contain water in proportion to the moisture absorption rate of the fibers, and even if this water were to migrate into the oil, this water would remain dissolved in the oil. It does not exist in a phase-separated form from the oil. This water content is at most 5%
within In the present invention, although the reason why contaminant components coagulate and settle in oil is not fully clear, the above-mentioned short-chain alkyl group-containing quaternary ammonium salt combines with negatively charged contaminant components in oil. It is thought that the oil coagulates and settles due to the action of the nonionic surfactant present in the oil. This estimation is based on high boiling point oil that does not contain nonionic surfactants.
This agrees well with the fact that even when a short-chain alkyl group-containing quaternary ammonium salt is added, no flocculation and sedimentation of pollutant components occurs. According to the present invention, the fourth
Grade ammonium salt is extracted by extracting the sedimentary pollutant components with water.
If necessary, it can be easily recovered in a reusable form by applying a concentration method known per se. The high-boiling point oil targeted in the present invention includes mineral oil, synthetic lubricating oil, or a mixture thereof, and any oil that is suitable as an oil agent for dust adsorption can be used. These oils can be used under normal conditions (20℃, 1
It is non-volatile (non-drying) at atmospheric pressure) and has a viscosity of 8 to 100 cP, preferably 10 to 90 cP, measured at 100 m. Suitably, the oil has an aniline point of 20 to 80, preferably 40 to 60, an ignition point of at least 130°C, a boiling point of at least 280°C, and a temperature of less than 15 mmHg measured at 70°C. It also has a low vapor pressure. The mineral oil may consist of paraffinic hydrocarbons, naphthenic hydrocarbons, aromatic hydrocarbons or mixtures thereof, suitable examples of which are liquid paraffin, spindle oil, machine oil, refrigeration oil and others. It is a petroleum-based lubricant. Synthetic lubricating oils include polyolefin oil (α-olefin oil), polyglycol oil, polybutene oil,
Examples include alkylbenzene oil, diester oil, polyol ester oil, polyphenyl ether oil, and isoparaffin oil. In the case of oil-impregnated fiber products for cleaning, in addition to the above-mentioned oil agents, a cationic surfactant may be added to the oil agent for the purpose of imparting dust adsorption properties or further imparting self-emulsifying and self-exhausting properties. A combination with a nonionic surfactant, or an amphoteric surfactant having a cationic active group such as a quaternary ammonium group or an amino group and an anionic active group such as a carboxylic acid or sulfonic acid group, or the above cation. Amphoteric surfactants containing active groups and nonionic active groups such as polyethylene oxide groups are included. Furthermore, oil-impregnated fiber products for cleaning contain antioxidants to prevent deterioration of the oil agent, antifungal agents to prevent the growth of mold and bacteria, and antibacterial agents. During the cleaning and deoiling treatment described later, a portion of the oil is transferred into the oil agent which is the cleaning medium. Dirt on used oil-impregnated fibers is a complex mixture of the various types of stains mentioned above that adhere to or are adsorbed to the fibers, and even become stuck to the fibers after long-term use or neglect. There are some. Therefore, when cleaning oil-impregnated fiber products for cleaning using the oil itself as a cleaning medium, it is necessary to use a nonionic surfactant, especially a nonionic surfactant made of an ethylene oxide adduct of nonylphenol or a higher alcohol, to enhance the cleaning power. The average added mole of ionic surfactant, especially ethylene oxide is 1 to 1.
Add 10 moles. The amount added is preferably in the range of 3 to 20% by weight based on the oil agent as the cleaning medium. As the washing machine, a commercially available rotary washer may be used, but a washer capable of washing and deoiling (adjusting the amount of oil retained), such as Floatair manufactured by Washex, USA, is preferred. Cleaning is preferably carried out at room temperature, but in some cases it may be heated at 60 to 80°C.
It can be done for 30 minutes to 1 hour. The amount of oil left on the fibers varies depending on the type of fiber base material, but
12 to 30% by weight, especially 18 to 23% based on the fiber weight
A range of weight percent is suitable. After washing, the recovered oil is first separated through a wire mesh to remove coarse fiber waste and dirt, and then, if necessary, is filtered using a supercharging agent such as acid clay or diatomaceous earth, and then subjected to the recycling treatment of the present invention. do. In the present invention, adding a quaternary ammonium salt of general formula () to the above-mentioned contaminated oil in an amount of 0.5 to 10% by weight, particularly preferably 1 to 3% by weight, effectively coagulates and sediments the pollutant components. It is important to do so. First, the alkyl group in the molecule of the quaternary ammonium salt used must have 2 to 5 carbon atoms. Quaternary surfactants with long chain alkyl groups commonly used as cationic surfactants
Class ammonium salts such as cetylpyridium chloride, trioctylmethylammonium chloride, dimethyldimyristylbenzylammonium chloride, dimethyldistearylammonium chloride, dimethylalkylbenzylammonium chloride, and dimethyldialkyl ammonium chloride are all pollutant components in contaminated oil. It does not have the ability to coagulate and precipitate. That is, contaminated oil obtained by washing used oil-impregnated fiber products is stained brown to black, and its absorbance is generally 2.0 or more. When a quaternary ammonium salt having a long-chain alkyl group as exemplified above is added to this contaminated oil, no sedimentation of these contaminating components occurs, and the absorbance of the treated liquid remains that of the contaminated oil. On the other hand, according to the present invention, when a quaternary ammonium salt whose alkyl group has carbon atoms in the range of 2 to 5 is added, the contaminant components are significantly flocculated and sedimented, and this fact is clear from the examples described below. Probably. In the quaternary ammonium salt used in the present invention, only one of the four alkyl groups may be substituted with an aralkyl group such as a benzyl group. The anion of the quaternary ammonium salt is preferably a halide ion, particularly a chloride ion.
Suitable examples thereof are tetraethylammonium chloride, tetra-n-propylammonium chloride, tetra-n-butylammonium chloride, tetra-n-pentylammonium chloride, tetra-n-butylammonium bromide, tetra-n-butylammonium iodide, These include benzyltri-n-butylammonium chloride, and these may be used alone or in combination of two or more. Most preferred is tetra-n-butylammonium chloride. The mixture with the addition of quaternary ammonium salt is 50
Heating and stirring at a temperature of 60 to 80°C, particularly 60 to 80°C,
Uniformly disperse the quaternary ammonium salt. When this liquid is then allowed to stand and cool, the polluted components coagulate and settle, and a clear, almost transparent oil component is separated in the upper layer. This separation is completed within an hour, especially within 30 minutes. However, it is of course also possible to perform a centrifugation operation to facilitate separation. Further, according to the present invention, the quaternary ammonium salt used as a flocculant and sedimentation agent is prepared by diluting the pollutant layer separated by flocculation and sedimentation with water 5 to 10 times.
Heat to 95℃ and leave for a while, or 5 to 10 minutes.
After dilution, a clear aqueous solution of the quaternary ammonium salt is obtained by adding an inorganic salt such as common salt or mirabilite to a concentration of 2 to 10% based on the amount of diluted water. This aqueous solution can be reused by extracting it with an organic solvent or by evaporating and concentrating it. The present invention will be explained below with reference to FIG. 1, which shows one embodiment of the method of the present invention. Contaminated oil A and flocculant precipitant B in an amount of 1.5 to 10% by weight based on contaminated oil A are heated at 50 to 95°C in stirring tank 1.
Heat and stir at a temperature of . Next, this mixed liquid C is transferred to the flocculation sedimentation tank 3, where it is left to cool and stand. After standing for a while, a clear, almost colorless oil layer D from which contaminant components have been removed is obtained as the upper layer. Transfer this recycled oil layer D to the stirring layer 4, add activated clay G, mix and stir,
This is subjected to a pre-coating process to obtain recycled oil. Further, the contaminant component (tar component) E condensed and precipitated in the condensation sedimentation tank is diluted 5 to 10 times with water F, and mixed and stirred in the stirring tank 6 at 50 to 90°C. If necessary, add inorganic salts such as table salt or mirabilite.
By adding 3 to 10% by weight to the amount of diluted water, mixing and leaving it for a while in the next settling tank 7, an oil layer containing pollutant components (tar content) and an aqueous layer containing the quaternary ammonium salt are formed. Separate into Next, the quaternary ammonium salt can be recovered and reused by subjecting the aqueous layer to operations such as reverse osmosis and evaporation. The present invention will be explained below using examples. Example 1 A used cleaning oil-impregnated fiber product (dust control product) was collected after cleaning with industrial paraffin oil, and the cleaning oil filtered through diatomaceous earth was used as a dirty oil sample. This cleaning oil is mainly made of industrial paraffin.
Nonionic surfactant 7% by weight, antioxidant 0.35
% by weight, 1.0% by weight of antifungal agent, 0.15% by weight of antibacterial agent, and several % of animal and vegetable oils, wax, grease, fine earth and sand, etc. 3% by weight of tetra-n-butylammonium chloride was added as a flocculant to the contaminated liquid, and the mixture was heated and stirred at 80°C. After the flocculant was uniformly dispersed, the heating and stirring was stopped, and the mixture was allowed to stand for about 1 hour to cool. The evaluation of the supernatant liquid is shown in Table 1. 【table】

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

第1図は、本発明の再生回収法の行程を示す図
であり、引照数字1は撹拌層、2は凝集沈殿、4
及び5は撹拌層、6は沈殿層であり、Aは汚染
油、Bは凝集沈降剤、Dは再生油層、Hはプレコ
ート過、Iは再生油、Jは逆浸透又は蒸発等の
操作、Kは再生された凝集沈降剤をそれぞれ示
す。
FIG. 1 is a diagram showing the process of the regeneration and recovery method of the present invention, where reference number 1 is a stirring layer, 2 is a coagulation sedimentation layer, 4 is a
and 5 is a stirring layer, 6 is a sedimentation layer, A is contaminated oil, B is a coagulation sedimentation agent, D is a recycled oil layer, H is a pre-coat filter, I is a recycled oil, J is an operation such as reverse osmosis or evaporation, K indicate regenerated flocculation and sedimentation agents, respectively.

Claims (1)

【特許請求の範囲】 1 使用済清掃用含油繊維製品をダスト吸着用油
剤を洗浄液として洗浄して得られる汚濁成分及び
ノニオン界面活性を含有する高沸点汚油に、相分
離した水の実質上非存在下に、 下記式 式中、R1,R2,R3の各々は炭素数2乃至5の
アルキル基であり、R4は炭素数2乃至5のアル
キル基若しくはアルキル部分の炭素数が2以下で
あるアラールキル基であり、Xはアニオンであ
る、 で表わされる第4級アンモニウム塩を0.5乃至10
重量%の量で添加し、50乃至95℃の温度で加熱撹
拌し、放置して汚濁物質を凝集沈殿させ、上澄清
浄油を分取することを特徴とする高沸点汚油の再
生回収法。 2 前記式()で表わされる第4級アンモニウ
ム塩がテトラ−n−ブチルアンモニウムクロライ
ドである特許請求の範囲第1項記載の再生回収
法。 3 凝集沈殿した汚濁物質を水性媒体による抽出
操作に賦して第4級アンモニウム塩を回収し、回
収された第4級アンモニウム塩を凝集剤として再
利用する特許請求の範囲第1項記載の再生回収
法。
[Scope of Claims] 1. A high boiling point dirty oil containing polluting components and nonionic surfactants obtained by washing used oil-impregnated cleaning fiber products with a dust adsorption oil agent as a cleaning liquid is mixed with substantially non-containing phase-separated water. In the presence of the following formula In the formula, each of R 1 , R 2 , and R 3 is an alkyl group having 2 to 5 carbon atoms, and R 4 is an alkyl group having 2 to 5 carbon atoms or an aralkyl group whose alkyl moiety has 2 or less carbon atoms. 0.5 to 10 of the quaternary ammonium salt represented by
A method for regenerating and recovering high-boiling point dirty oil, which is characterized in that it is added in an amount of % by weight, heated and stirred at a temperature of 50 to 95°C, allowed to stand to coagulate and precipitate the pollutants, and then separate the supernatant clean oil. . 2. The regeneration and recovery method according to claim 1, wherein the quaternary ammonium salt represented by the formula () is tetra-n-butylammonium chloride. 3. Regeneration according to claim 1, in which the coagulated and precipitated pollutants are subjected to an extraction operation using an aqueous medium to recover quaternary ammonium salts, and the recovered quaternary ammonium salts are reused as a flocculant. Collection method.
JP13239579A 1979-10-16 1979-10-16 Regeneration recovery of high boiling point used oil Granted JPS5657899A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13239579A JPS5657899A (en) 1979-10-16 1979-10-16 Regeneration recovery of high boiling point used oil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13239579A JPS5657899A (en) 1979-10-16 1979-10-16 Regeneration recovery of high boiling point used oil

Publications (2)

Publication Number Publication Date
JPS5657899A JPS5657899A (en) 1981-05-20
JPS6146033B2 true JPS6146033B2 (en) 1986-10-11

Family

ID=15080379

Family Applications (1)

Application Number Title Priority Date Filing Date
JP13239579A Granted JPS5657899A (en) 1979-10-16 1979-10-16 Regeneration recovery of high boiling point used oil

Country Status (1)

Country Link
JP (1) JPS5657899A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2609648B1 (en) * 1987-01-16 1990-12-14 Total France DESEMULSIFYING AND ANTI-FOULING AGENT CAPABLE OF SEPARATING WATER-HYDROCARBON MIXTURES, WHETHER EMULSIFIED, AND APPLICATIONS THEREOF
EP2363290A1 (en) * 2010-03-05 2011-09-07 KBA-NotaSys SA Installation and process for recycling wiping solution of one or more intaglio printing presses
JP2014071025A (en) * 2012-09-28 2014-04-21 Toshiba Corp Solid-liquid separation method and solid-liquid separation device
CN104818153B (en) * 2015-04-10 2017-09-29 阚立东 A kind of method that utilization gutter oil manufactures soap powder

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4911901A (en) * 1972-05-15 1974-02-01
JPS54102305A (en) * 1978-01-18 1979-08-11 Nippon Steel Chem Co Ltd Treatment of water-containing tar waste oil

Also Published As

Publication number Publication date
JPS5657899A (en) 1981-05-20

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