JPH024898A - Re-treatment of waste lubricating oil - Google Patents
Re-treatment of waste lubricating oilInfo
- Publication number
- JPH024898A JPH024898A JP15546388A JP15546388A JPH024898A JP H024898 A JPH024898 A JP H024898A JP 15546388 A JP15546388 A JP 15546388A JP 15546388 A JP15546388 A JP 15546388A JP H024898 A JPH024898 A JP H024898A
- Authority
- JP
- Japan
- Prior art keywords
- oil
- diatomaceous earth
- waste
- admixtures
- lubricating oil
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000002699 waste material Substances 0.000 title claims abstract description 41
- 239000010687 lubricating oil Substances 0.000 title claims abstract description 20
- 239000003921 oil Substances 0.000 claims abstract description 100
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 33
- 239000005909 Kieselgur Substances 0.000 claims abstract description 31
- 238000010438 heat treatment Methods 0.000 claims abstract description 25
- 239000004927 clay Substances 0.000 claims abstract description 15
- 238000001914 filtration Methods 0.000 claims abstract description 11
- 239000003518 caustics Substances 0.000 claims abstract description 9
- 239000007864 aqueous solution Substances 0.000 claims abstract description 6
- 238000000034 method Methods 0.000 claims description 31
- 239000012535 impurity Substances 0.000 claims description 29
- 238000006243 chemical reaction Methods 0.000 claims description 16
- 238000000926 separation method Methods 0.000 claims description 16
- 230000001050 lubricating effect Effects 0.000 claims description 11
- 238000004064 recycling Methods 0.000 claims description 4
- 239000010419 fine particle Substances 0.000 abstract description 9
- 229910019142 PO4 Inorganic materials 0.000 abstract description 6
- 239000003513 alkali Substances 0.000 abstract description 5
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 abstract description 5
- 239000010452 phosphate Substances 0.000 abstract description 5
- 239000011248 coating agent Substances 0.000 abstract description 4
- 238000000576 coating method Methods 0.000 abstract description 4
- 238000011084 recovery Methods 0.000 abstract description 3
- 239000011541 reaction mixture Substances 0.000 abstract 1
- 238000005482 strain hardening Methods 0.000 abstract 1
- 230000008929 regeneration Effects 0.000 description 11
- 238000011069 regeneration method Methods 0.000 description 11
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 9
- 238000005119 centrifugation Methods 0.000 description 8
- 238000010273 cold forging Methods 0.000 description 8
- 230000000052 comparative effect Effects 0.000 description 6
- 239000000203 mixture Substances 0.000 description 6
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 5
- 239000000356 contaminant Substances 0.000 description 5
- 238000007796 conventional method Methods 0.000 description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 5
- 229910052725 zinc Inorganic materials 0.000 description 5
- 239000011701 zinc Substances 0.000 description 5
- 239000000463 material Substances 0.000 description 4
- 238000002156 mixing Methods 0.000 description 4
- 239000010802 sludge Substances 0.000 description 4
- LRXTYHSAJDENHV-UHFFFAOYSA-H zinc phosphate Chemical compound [Zn+2].[Zn+2].[Zn+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O LRXTYHSAJDENHV-UHFFFAOYSA-H 0.000 description 4
- 229910000165 zinc phosphate Inorganic materials 0.000 description 4
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 3
- 238000004458 analytical method Methods 0.000 description 3
- 230000003247 decreasing effect Effects 0.000 description 3
- 230000018044 dehydration Effects 0.000 description 3
- 238000006297 dehydration reaction Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 239000011148 porous material Substances 0.000 description 3
- 239000002244 precipitate Substances 0.000 description 3
- 238000012545 processing Methods 0.000 description 3
- 239000002002 slurry Substances 0.000 description 3
- 235000011121 sodium hydroxide Nutrition 0.000 description 3
- 239000000243 solution Substances 0.000 description 3
- 238000003756 stirring Methods 0.000 description 3
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- 239000011362 coarse particle Substances 0.000 description 2
- 239000000314 lubricant Substances 0.000 description 2
- 230000001172 regenerating effect Effects 0.000 description 2
- 239000000344 soap Substances 0.000 description 2
- UGZADUVQMDAIAO-UHFFFAOYSA-L zinc hydroxide Chemical compound [OH-].[OH-].[Zn+2] UGZADUVQMDAIAO-UHFFFAOYSA-L 0.000 description 2
- 229940007718 zinc hydroxide Drugs 0.000 description 2
- 229910021511 zinc hydroxide Inorganic materials 0.000 description 2
- 241000206761 Bacillariophyta Species 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000007123 defense Effects 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 238000007667 floating Methods 0.000 description 1
- 238000005242 forging Methods 0.000 description 1
- 238000007689 inspection Methods 0.000 description 1
- 235000014413 iron hydroxide Nutrition 0.000 description 1
- NCNCGGDMXMBVIA-UHFFFAOYSA-L iron(ii) hydroxide Chemical compound [OH-].[OH-].[Fe+2] NCNCGGDMXMBVIA-UHFFFAOYSA-L 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- GQPLMRYTRLFLPF-UHFFFAOYSA-N nitrous oxide Inorganic materials [O-][N+]#N GQPLMRYTRLFLPF-UHFFFAOYSA-N 0.000 description 1
- 235000011118 potassium hydroxide Nutrition 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 238000012958 reprocessing Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Landscapes
- Lubricants (AREA)
Abstract
Description
【発明の詳細な説明】
産業上の利用分野
この発明は、冷間鍛造加工に使用した型潤滑油等の廃油
を再生使用するための潤滑廃油の再生処理方法に関する
ものである。DETAILED DESCRIPTION OF THE INVENTION Field of Industrial Application This invention relates to a method for recycling waste lubricating oil, such as die lubricating oil used in cold forging.
従来の技術
金型を用いる冷間鍛造加工は、型通りの形状の部品が素
材から直接製造できるので生産性が高く、また無駄にな
る材料の発生が少なく省資源の面でも優れているため、
自動車製造等において盛んに利用されている加工法であ
る。Cold forging using conventional technology molds is highly productive because parts with the shape of the mold can be manufactured directly from the raw material, and it is also excellent in terms of resource conservation as there is less wasted material.
This is a processing method that is widely used in automobile manufacturing and other industries.
冷間鍛造加工は常温で行われるので、熱間S造加工と比
べ金型と素材間に大きな摩擦力がかかり、金型に型潤滑
油を塗布しただけでは、油膜の形成不全と耐熱性不足と
で焼付が起りやすい。そのため冷間鍛造加工においては
、加工用素材に予めリン酸塩被膜処理を施し、素材表面
に潤滑性、耐摩耗性に優れる被膜を形成してから加工し
ている。Since cold forging is performed at room temperature, there is a greater frictional force between the mold and the material than in hot steel forging, and simply applying mold lubricating oil to the mold may result in insufficient oil film formation and insufficient heat resistance. Burning is likely to occur. Therefore, in cold forging processing, the material to be processed is subjected to a phosphate coating treatment in advance to form a coating with excellent lubricity and wear resistance on the surface of the material before processing.
このため、油タンクと冷間若造はとの間を循環させなが
ら使用している型潤滑油には、リン酸塩粕(通称:ボン
デ粕)の混入が避けられず、スラッジ(沈澱物)、スカ
ム(浮遊物)分が多くなるにつれてマシントラブルが発
生しやすくなる。したがって、型潤滑油は所定期間使用
された後、新油と交、換され、その周期は使用状態で異
なるが2〜4力月が一般的である。For this reason, the mold lubricating oil that is used while being circulated between the oil tank and the cold water tank is unavoidably contaminated with phosphate sludge (commonly known as Bonde sludge), sludge (sediment), As the amount of scum (floating matter) increases, machine troubles are more likely to occur. Therefore, after the mold lubricating oil has been used for a predetermined period of time, it is replaced with new oil, and although the cycle varies depending on the state of use, it is generally 2 to 4 months.
交換された使用済の型潤滑油、すなわち夾雑物を多く含
んでいる廃油には、他の廃液(例えば特開昭61−12
3639号公報参照)にみられるような適切な処分方法
が見い出せなかったため、このような冷間鍛造型潤滑油
の廃油は、多くの場合、再生使用されることなく焼却処
分されていた。The used mold lubricating oil that has been replaced, that is, the waste oil that contains a lot of contaminants, is mixed with other waste liquids (for example, JP-A-61-12
In many cases, such waste oil from cold forging mold lubricating oil was incinerated without being recycled, as no suitable disposal method could be found as seen in Publication No. 3639).
このように、冷間鍛造型潤滑油の廃油の再生使用があま
り行われていないのは、廃油中に夾雑物が3%以上と多
く、かつ粘度が初期の高い粘度75 cstから更に1
00cst以上へとより高くなっていることから、夾雑
物の分離排除が困難なためであり、従来の一般的な廃油
の再生処理方法、例えば、廃油を加熱して粘度を下げ、
夾雑物を静置分離または遠心分離する方法で処理した場
合には、夾雑物除去率は30〜60%が限界であり、し
かも−船釣な加熱温度(80℃)よりも20%増の10
0’C前後まで加熱しなければならなかった。As described above, the reason why waste oil used for cold forging lubricating oil is not often recycled is that the waste oil contains a large amount of impurities (more than 3%), and the viscosity has increased from the initial high viscosity of 75 cst to 1.
This is because it is difficult to separate and eliminate impurities as the oil temperature is higher than 00 cst. Conventional conventional waste oil recycling methods, such as heating the waste oil to lower its viscosity, are difficult.
When contaminants are treated by static separation or centrifugal separation, the contaminant removal rate is limited to 30 to 60%, and moreover, the contaminant removal rate is 20% higher than the heating temperature (80°C) used in boat fishing.
It had to be heated to around 0'C.
また、濾過助剤や吸着剤として珪藻土や活性白土を廃油
に加えて再生処理する方法も試みられている。例えば第
2図は、珪藻土を用いる従来の潤滑廃油の再生処理プラ
ントのプロセスフローシートを示すもので、容器1に回
収された使用済みの潤滑廃油は、1jロ熱タンク2に送
油され、80℃以上に加熱して粘度を下げられた後、遠
心分離機3にかけられる。遠心分離n3により分離され
た夾雑物は分離軸として分離軸タンク4に回収され、ま
た分離軸が除かれた分離油は分離油タンク5に回収され
る。回収された分離油は、加熱脱水タンク6に送油され
て100〜120℃に加熱され、水分は水蒸気として排
出される。水分を除去された処理油は、珪藻土混合タン
ク7に送油され、処理油に含まれる夾雑物量に応じた量
(例えば3.0〜7.0%)の珪藻土が添加され、均一
に分散するように攪拌混合される。そして、珪藻土混合
油は、フィルターブレス8に送油されて濾過され、濾過
残漬は濾過残漬パレット9に回収され、濾過された処理
油は、再生油として再生油タンク10に回収され、ドラ
ム缶等の容器11に詰められ、型yJ潤滑油し再使用さ
れる。Additionally, attempts have been made to recycle waste oil by adding diatomaceous earth or activated clay as a filter aid or adsorbent. For example, Fig. 2 shows a process flow sheet of a conventional lubricating waste oil regeneration treatment plant using diatomaceous earth. After being heated to a temperature above .degree. C. to lower the viscosity, it is passed through a centrifuge 3. The impurities separated by the centrifugation n3 are collected as separation shafts in the separation shaft tank 4, and the separated oil from which the separation shafts have been removed is collected in the separation oil tank 5. The recovered separated oil is sent to a heating dehydration tank 6 and heated to 100 to 120°C, and the moisture is discharged as steam. The treated oil from which water has been removed is sent to the diatomaceous earth mixing tank 7, where diatomaceous earth is added in an amount (for example, 3.0 to 7.0%) according to the amount of impurities contained in the treated oil, and is uniformly dispersed. Stir and mix as shown. Then, the diatomaceous earth mixed oil is sent to the filter breath 8 and filtered, the filtered residue is collected in the filtered residue pallet 9, and the filtered treated oil is collected as recycled oil in the recycled oil tank 10, and the filtered oil is collected in the recycled oil tank 10 as recycled oil. It is packed in a container 11 such as a type yJ lubricant and reused.
発明が解決しようとする課題
しかし、前記した従来の再生処理方法においては、例え
ば珪藻土の添加量が不足していると、フィルタープレス
の濾過目詰りが早く、処理不能等の処理トラブルが発生
しやすかった。この濾過目詰りの原因としては、直径1
〜30μ程度のボンデ粕の微粒子が、珪藻土の細孔を閉
塞するためと推定され、その対応策として濾布の洗浄等
を頻繁に実施して再生処理を行なう必要があった。Problems to be Solved by the Invention However, in the conventional regeneration treatment method described above, for example, if the amount of diatomaceous earth added is insufficient, the filtration of the filter press will quickly become clogged, which tends to cause treatment troubles such as inability to process. Ta. The cause of this filter clogging is the diameter 1
It is presumed that the fine particles of Bonde lees of about 30 microns block the pores of the diatomaceous earth, and as a countermeasure, it was necessary to perform regeneration treatment by frequently washing the filter cloth.
また、上記した従来の方法で再生処理した場合には、再
生油の夾雑物含有!(83値)が0.2〜1.0%の範
囲で、直径1μ以下のボンデ粕の微粒子が残存している
。そのため、この再生油を潤滑油としそのまま再使用す
ると、再生油の油寿命が非常に短くなってしまうことか
ら、再生処理した潤滑油に、型潤滑油の新油を50%程
度混合して使用しなければならない等の問題点があった
。In addition, when recycled oil is recycled using the conventional method described above, the recycled oil contains impurities! (83 value) is in the range of 0.2 to 1.0%, and fine particles of bondage residue with a diameter of 1 μm or less remain. Therefore, if this recycled oil is reused as a lubricating oil, the lifespan of the recycled oil will be extremely shortened, so the recycled lubricating oil should be mixed with about 50% new mold lubricating oil. There were problems such as having to do so.
この発明は上記した技術的背景の下になされたもので、
夾雑物の除去率を向上させかつ濾過トラブルの発生を防
止するとともに、再生油の回収率の高い、1!I滑廃油
の再生処理方法の提供を目的としている。This invention was made against the above-mentioned technical background.
1! Improves the removal rate of impurities, prevents filtration troubles, and has a high recovery rate of recycled oil! The purpose is to provide a method for recycling waste oil.
課題を解決するための手段
上記課題を解決するための手段としてこの発明の潤滑廃
油の再生処理方法は、潤滑廃油に苛性アルカリ水溶液を
添加して100℃以上に加熱し、夾雑物を沈澱させて除
去する加熱反応処理工程と、珪藻土と活性白土とを添加
して均一に分散させ、潤滑廃油中に残留する夾雑物と共
に遠心分離鵬により分離除去する遠心分離処理工程と、
珪藻土等の濾過助剤を添加し、濾過してa!I滑廃油中
の夾雑物を除去する濾過処理工程とを行うことを特徴と
している。Means for Solving the Problems As a means for solving the above problems, the method for regenerating lubricating waste oil of the present invention includes adding a caustic alkaline aqueous solution to lubricating waste oil and heating it to 100°C or higher to precipitate impurities. a heating reaction treatment step for removing diatomaceous earth and activated clay; a centrifugation treatment step for adding and uniformly dispersing diatomaceous earth and activated clay, and separating and removing the impurities remaining in the lubricating waste oil using a centrifugal separator;
Add a filter aid such as diatomaceous earth, filter and a! It is characterized by performing a filtration treatment step to remove impurities from the waste oil.
作 用
上記の方法によれば、先ず、加熱反応処理工程が行われ
、夾雑物を含む8!I澗廃油に苛性アルカリ水溶液が添
加されかつ100℃以上に加熱されると、夾雑物中に含
まれるリン酸亜鉛等のリン11 塩被膜粕の微粒子が化
学変化して粗粒化される。Effect According to the above method, first, a heating reaction treatment step is performed, and 8! When an aqueous caustic alkali solution is added to the waste oil and heated to 100° C. or higher, the fine particles of the phosphorus-11 salt-coated residue, such as zinc phosphate, contained in the impurities undergo a chemical change and become coarse particles.
例えば、難溶性リン酸亜鉛は、亜鉛水酸化物、亜鉛石鹸
等の化合物となって沈澱し、水分も同時に除去される。For example, sparingly soluble zinc phosphate becomes a compound such as zinc hydroxide or zinc soap and precipitates, and water is also removed at the same time.
[主な化学反応式]
2rr3 (PO4)2 +6NaOH+2RCOOH
(fl溶性リン酸亜鉛)(苛性ソーダ)2rb (P
O4)2+4H20+2RCOOHまた、遠心分離処理
工程では、分離助剤として珪藻土と活性白土の混合物を
添加し、夾雑物中の微粒子を珪藻土および活性白土の細
孔中に吸着させて遠心分離はにかけると、夾雑物が珪藻
土および活性白土と共に効率的に分離除去される。[Main chemical reaction formula] 2rr3 (PO4)2 +6NaOH+2RCOOH
(fl-soluble zinc phosphate) (caustic soda) 2rb (P
O4)2+4H20+2RCOOHAlso, in the centrifugation process, a mixture of diatomaceous earth and activated clay is added as a separation aid, and the fine particles in the impurities are adsorbed into the pores of the diatomaceous earth and activated clay, and then centrifugation is performed. Impurities are efficiently separated and removed together with diatomaceous earth and activated clay.
そして濾過工程では、例えば珪藻上等の濾過助剤を添加
してフィルタープレス等により濾過すると、潤滑間油中
の夾雑物が濾過助剤とともに除去される。In the filtration step, when a filter aid such as diatom is added and filtered using a filter press or the like, impurities in the lubricating oil are removed together with the filter aid.
したがって、夾雑物中のリン酸塩被膜の微粒子は、加熱
反応処理工程で粗粒化され沈澱して除去されるとともに
、遠心分離処理工程で、珪藻土等に吸着して分離除去さ
れているため、濾過工程においては珪藻上等が濾過目詰
まりすることなく、効率良く濾過される。Therefore, the fine particles of the phosphate coating in the contaminants are coarsened and precipitated in the heating reaction treatment process and removed, and in the centrifugation treatment process they are adsorbed to diatomaceous earth and separated and removed. In the filtration step, the diatoms and the like are efficiently filtered without clogging the filter.
実施例
以下、この発明の潤滑廃油の再生処理方法の一実施例を
第1図に示す再生処理のプロセスフローシートを参照し
て説明する。EXAMPLE Hereinafter, an example of the method for regenerating lubricating waste oil of the present invention will be described with reference to the regeneration process flow sheet shown in FIG.
冷間鍛造加工に使用された型潤滑油の廃油には、多量の
ボンデ粕等の夾雑物が含まれ、これらの夾雑物は、常温
では廃油の粘度が高いため沈澱せずに廃油中に分散して
いる。夾雑物の組成としては、水分、鉄酸化物、鉄水酸
化物、リン酸亜1(ボンデ粕)、シリカ(塵埃)等で、
この廃油は、ドラム缶等の容器11より先ず加熱反応タ
ンク12へ送油されて、濃度0.1%程度の苛性ソーダ
あるいは苛性カリ等の苛性アルカリ水溶液が添加される
。この苛性アルカリ水溶液の添加量は、廃油の吊の2〜
5%程度で、添加後は加熱反応タンク12内に配設した
スチームヒータによって100℃以上に加熱される。苛
性アルカリ水溶液を添加されるとともにh0熱された廃
油は、特にリン酸亜鉛の微粒子が亜鉛水酸化物や亜鉛石
鹸に化学変化し、粗粒化するとともに沈澱してスラリー
化する。この加熱反応時間は、30〜60分程度で程度
する。The waste oil from mold lubricating oil used in cold forging processing contains a large amount of impurities such as bonding scum, and these impurities are dispersed in the waste oil without settling because the viscosity of the waste oil is high at room temperature. are doing. The composition of impurities includes moisture, iron oxide, iron hydroxide, nitrous phosphate (bonde lees), silica (dust), etc.
This waste oil is first sent to a heating reaction tank 12 from a container 11 such as a drum, and an aqueous caustic alkali solution such as caustic soda or caustic potash having a concentration of about 0.1% is added thereto. The amount of this caustic alkaline aqueous solution added is between 2 and 3 times the amount of waste oil.
It is about 5%, and after addition, it is heated to 100° C. or higher by a steam heater installed in the heating reaction tank 12. In waste oil to which an aqueous caustic alkali solution is added and heated to h0, fine particles of zinc phosphate in particular chemically change into zinc hydroxide and zinc soap, become coarse particles, and precipitate to form a slurry. The heating reaction time is about 30 to 60 minutes.
そして、加熱反応タンク12内に沈澱した夾雑物のスラ
リーは、下部のドレンより排出されてスラリータンク1
3に回収される。Then, the slurry of impurities precipitated in the heating reaction tank 12 is discharged from the drain at the bottom and becomes the slurry tank 1.
It will be collected on 3rd.
一方、加熱反応タンク12に残った処理油は、加熱タン
ク14に送油され、活性白土と珪藻土とを2.5%程度
投入されて攪拌混合される。そして、混合鷺浬油は、ス
チームヒータで100℃以上にノjO熱され、活性白土
と珪藻土の細孔中に含まれている水分を追い出し、代り
に処理油中の夾雑物の微粒子を前記細孔内に吸着させる
。この吸着に要する時間は30−60分程度である。次
に遠心分離握15にかけられ、夾雑物を吸着した活性白
土および珪藻土は、分離粕として分離粕タンク16に回
収され、分離油は、分離油タンク17に回収される。On the other hand, the treated oil remaining in the heating reaction tank 12 is sent to the heating tank 14, where about 2.5% of activated clay and diatomaceous earth are added and mixed by stirring. The mixed Sagiho oil is then heated to over 100°C with a steam heater to drive out the moisture contained in the pores of the activated clay and diatomaceous earth, and instead remove the fine particles of impurities in the treated oil. Adsorb into the hole. The time required for this adsorption is about 30-60 minutes. Next, the activated clay and diatomaceous earth that have been subjected to centrifugal separation 15 and have adsorbed impurities are collected as separated lees in a separated lees tank 16, and the separated oil is collected in a separated oil tank 17.
そして、分離油タンク17に回収された分離油は、加熱
脱水タンク18に送油され、スチームヒータで110℃
以上に加熱して、水分を水蒸気として除去される。The separated oil collected in the separated oil tank 17 is sent to a heated dehydration tank 18 and heated to 110°C using a steam heater.
By heating to a higher temperature, water is removed as water vapor.
さらに、水分除去油は、珪藻土混合タンク19に送油さ
れるとともに、油量の1〜3%程度の珪藻土が投入され
るとともに、100℃以上に加熱されて攪拌混合される
。30分程度撹拌混合した後、フィルタープレス20に
送られて濾過され、濾過残渣は濾過残漬パレット21に
回収され、直径1μ以上の夾雑物は殆ど除去されて、再
生油タンク22に回収され、再生油は、品質検査を行な
った後、ドラム缶等の容器23に詰められ、型潤滑油と
して使用に供される。Further, the water-removed oil is sent to the diatomaceous earth mixing tank 19, and about 1 to 3% of the oil amount of diatomaceous earth is added thereto, heated to 100° C. or higher, and stirred and mixed. After stirring and mixing for about 30 minutes, it is sent to a filter press 20 and filtered, and the filtration residue is collected in a filter residue pallet 21, and most of the impurities with a diameter of 1 μ or more are removed and collected in a recycled oil tank 22. After quality inspection, the recycled oil is packed into a container 23 such as a drum and used as mold lubricating oil.
次に、この実施例の潤滑廃油の再生処理方法によって実
際に再生処理を行った実施例1と、加熱反応処理工程の
効果を見るために実施例1における加熱反応処理工程を
省略して再生処理を行なった参考例1と、従来法により
再生処理を行なった比較例について説明する。Next, we will discuss Example 1 in which regeneration treatment was actually performed using the regeneration treatment method for lubricating waste oil of this example, and regeneration treatment in which the heating reaction treatment step in Example 1 was omitted in order to see the effect of the heating reaction treatment step. Reference Example 1 in which the regeneration process was performed and a comparative example in which the regeneration process was performed using the conventional method will be described.
[比較例1]
供試油は、冷間鍛造型潤滑剤(協同油脂(体製・サルク
ラットY−50A)の廃油で、その性状は第1表に示す
通りである。[Comparative Example 1] The sample oil was a waste oil of a cold forging lubricant (Kyodo Yushi Co., Ltd., manufactured by Taisei, Sarkurat Y-50A), and its properties are as shown in Table 1.
第2a
単位: ppm
第1表
第38
単位: ppm
5S値=0.8μミリポアフイルタを通過できない懸濁
固形物(5uspended sol id)の廃油中
の存在量を百分率で表したもの。Unit 2a: ppm Table 1, No. 38 Unit: ppm 5S value = 0.8μ The amount of suspended solids that cannot pass through a Millipore filter in waste oil, expressed as a percentage.
上記供試油を、第2図にプロセスフローシートを示す従
来の再生処理方法で処理を行ない、その遠心分離処理油
と再生油のそれぞれの性状とス比較用に新油の性状とを
第2表に示す。なお、珪藻土は処理油量に対して約6.
0%添加した。The above sample oil was processed using the conventional reprocessing method shown in the process flow sheet in Figure 2, and the properties of the centrifuged oil and recycled oil were compared with the properties of the new oil in a second test. Shown in the table. In addition, diatomaceous earth has a ratio of about 6% to the amount of oil processed.
Added 0%.
そして、供試油、遠心分離処理油、再生油の三者の油中
金属元素をICP分析装置(ICPとは、Tnduct
ively Coupled Plaslaの略)で分
析した結果を第3表に示す。Then, the metal elements in the oil of the sample oil, centrifuged oil, and recycled oil were analyzed using an ICP analyzer (ICP is Tnduct).
Table 3 shows the results of the analysis using ively Coupled Plasla.
その結果、例えば供試油に含有される亜鉛の邑が、比較
例1では8655 ppnから7487ppnまで減少
し、約13%除去されている。As a result, for example, the amount of zinc contained in the sample oil decreased from 8,655 ppn to 7,487 ppn in Comparative Example 1, and was removed by about 13%.
[実施例11
比較例で用いた供試油と同等の廃油を、第1図に示す本
11明の方法のプロセスフローシートにしたがって再生
処理した。但し、処理油に対する添加量は、苛性ソーダ
が3.0%、分離助剤としての珪藻土および活性白土の
混合物が2,5%、濾過助剤としての珪藻土が1,0%
である。[Example 11 Waste oil equivalent to the test oil used in the comparative example was recycled according to the process flow sheet of the method of the present invention shown in FIG. However, the amount added to the treated oil is 3.0% caustic soda, 2.5% mixture of diatomaceous earth and activated clay as a separation aid, and 1.0% diatomaceous earth as a filter aid.
It is.
そして、供試油の性状および遠心分離処理油の性状、再
生油の性状をそれぞれ第4表に示す。また、各処理段階
における油中金属元素の分析結果を第5表に示す。Table 4 shows the properties of the sample oil, the centrifuged oil, and the recycled oil. Furthermore, Table 5 shows the analysis results of metal elements in the oil at each treatment stage.
第4表
単位:p−
第5表
その結果、例えば供試油に含有される亜鉛の里が、実施
例1では7217ppImから4487pρ1まで減少
し、約38%除去されている。Table 4 Unit: p- Table 5 As a result, for example, the amount of zinc contained in the sample oil decreased from 7217 ppIm to 4487 ppI in Example 1, and was removed by about 38%.
なお、遠心分離処理工程でIIJ滑廃油中に添加する分
離助剤は、珪藻土と活性白土とを1:1のと]合で混合
しものを用い、その添加量は、廃油中の夾雑物の吊(S
S値)に応じて適宜決定される。The separation aid added to the IIJ waste oil in the centrifugation process is a 1:1 mixture of diatomaceous earth and activated clay. Hanging (S
S value) is determined as appropriate.
r参考例1ノ
実施例1と同等な廃油を、第1図のプロセスフローシー
トに示す方法のうち加熱反応処理工程を省略して再生処
理した。なお、処理油に対する添加量は、分離助剤とし
の珪藻土と活性白土との混合物が3.0%、濾過助剤と
しての珪藻上が2゜5%である。rReference Example 1 Waste oil equivalent to Example 1 was regenerated by the method shown in the process flow sheet of FIG. 1 by omitting the heating reaction treatment step. The amount added to the treated oil was 3.0% of a mixture of diatomaceous earth and activated clay as a separation aid, and 2.5% of diatom as a filter aid.
そして、供試油の性状および遠心分離処理油の性状、再
生油の性状をそれぞ第6表に示す。また、油中金属元素
の分析結果を第7表に示す。Table 6 shows the properties of the sample oil, the properties of the centrifuged oil, and the properties of the recycled oil. Table 7 also shows the analysis results of metal elements in the oil.
第6表
単位: pDI
第7表
その結果、例えば供試油に含有される亜鉛の吊が、参考
例1では6755 ppnから5160ppiまで減少
し、約23%除去されている。Table 6 Unit: pDI Table 7 As a result, for example, the concentration of zinc contained in the sample oil decreased from 6755 ppn to 5160 ppi in Reference Example 1, which was about 23% removed.
また、比較例1と実施例1と参考例1とを、それぞれの
処理方法で得られた再生油のSS値で比較すると、従来
法による比較例1で処理された再生単位: ppm
油が0.6%、実施例1で処理された再生油では0.0
4%、加熱反応処理工程を行わなかった参考例1では0
.41%であった。Furthermore, when Comparative Example 1, Example 1, and Reference Example 1 are compared in terms of SS values of the recycled oil obtained by each treatment method, the recycled unit treated in Comparative Example 1 using the conventional method: ppm oil is 0. .6% and 0.0 for recycled oil treated in Example 1.
4%, and 0 in Reference Example 1 where no heating reaction treatment step was performed.
.. It was 41%.
発明の詳細
な説明したようにこの発明の方法によれば、加熱反応処
理工程において、潤滑廃油に苛性アルノノリ水溶液を添
加して100°C以上に加熱し、夾雑物を化学変化させ
、沈澱させて除去するとともに、遠心分離処理工程にお
いて、分離助剤として珪藻土と活性白土とを添加し、夾
雑物と共に遠心分離機により分離除去し、さらに、濾過
処理工程において、珪藻土等の濾過助剤を添加し、濾過
して潤滑廃油中の夾雑物を除去するようにしたので、加
熱反応処理工程において夾雑物の微粒子が粗粒化され、
沈澱して除去されるとともに、遠心分離処理工程での夾
雑物の分離性が向上する結果、濾過!I!!lL理工程
における濾過目詰りによるトラブルの弁士がなくなり、
夾雑物の除去率が従来法の場合の40%から70%に向
上した。Detailed Description of the Invention According to the method of the present invention, in the heating reaction treatment step, a caustic arunonol aqueous solution is added to the lubricating waste oil and heated to 100°C or higher to chemically change and precipitate impurities. At the same time, in the centrifugation process, diatomaceous earth and activated clay are added as separation aids, and the impurities are separated and removed by a centrifuge, and further, in the filtration process, a filter aid such as diatomaceous earth is added. Since the impurities in the lubricating waste oil are removed by filtration, the fine particles of the impurities are coarsened in the heating reaction treatment process.
In addition to being precipitated and removed, the separation of impurities during the centrifugation process is improved, resulting in filtration! I! ! Eliminates troubles caused by clogging of filters in the LL process,
The removal rate of impurities was improved from 40% in the conventional method to 70%.
また、従来法の場合には、0.1〜1.0%程度であっ
た再生油のSS値を、0.1%以下に清澄化でき、膨潤
滑油として100%再生油のみで使用できるようになり
、新油の使用量を低減することができる。In addition, in the case of conventional methods, the SS value of recycled oil, which was about 0.1 to 1.0%, can be clarified to 0.1% or less, and only 100% recycled oil can be used as expanded lubricating oil. This makes it possible to reduce the amount of new oil used.
さらに、濾過目詰り等のトラブルの発生が減り、生じる
分離粕等も減少するため、従来法の場合には30〜50
%であった再生油の回収率を65%以上に向上できる等
の効果を有する。In addition, the occurrence of troubles such as filter clogging is reduced, and the amount of separated sludge that is generated is also reduced.
This has the effect of increasing the recovery rate of recycled oil from 1.5% to 65% or more.
第1図はこの弁明の方法の一実施例を示す再生処理設備
のプロセスフローシート、第2図は従来の再生12!l
t哩設備のプロセスフローシートである。
12・・・加熱反応タンク、 14・・・加熱タンク、
15・・・遠心分離芸、 17・・・分離油タンク、
128・・・加熱脱水タンク、 19・・・珪藻土混合
タンク、20・・・フィルタープレス、 22・・・
再生油タンク、23・・・ドラム缶等の容器。Fig. 1 is a process flow sheet of a regeneration treatment facility showing an example of this defense method, and Fig. 2 is a process flow sheet of a conventional regeneration 12! l
This is a process flow sheet for the 100-meter facility. 12... Heating reaction tank, 14... Heating tank,
15... Centrifugal separation art, 17... Separation oil tank,
128... Heating dehydration tank, 19... Diatomaceous earth mixing tank, 20... Filter press, 22...
Recycled oil tank, 23... Container such as a drum can.
Claims (1)
に加熱し、夾雑物を沈澱させて除去する加熱反応処理工
程と、珪藻土と活性白土とを添加して均一に分散させ、
潤滑廃油中に残留する夾雑物と共に遠心分離機により分
離除去する遠心分離処理工程と、珪藻土等の濾過助剤を
添加し、濾過して潤滑廃油中の夾雑物を除去する濾過処
理工程とを行うことを特徴とする潤滑廃油の再生処理方
法。A heating reaction treatment step in which a caustic alkaline aqueous solution is added to lubricating waste oil and heated to 100°C or higher to precipitate and remove impurities, and diatomaceous earth and activated clay are added and dispersed uniformly.
A centrifugal separation process in which impurities remaining in the lubricating waste oil are separated and removed using a centrifuge, and a filtration process in which a filter aid such as diatomaceous earth is added and filtered to remove impurities in the lubricating waste oil are performed. A method for recycling waste lubricating oil, characterized by:
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63155463A JP2619264B2 (en) | 1988-06-23 | 1988-06-23 | Reprocessing of lubricating waste oil |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63155463A JP2619264B2 (en) | 1988-06-23 | 1988-06-23 | Reprocessing of lubricating waste oil |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH024898A true JPH024898A (en) | 1990-01-09 |
JP2619264B2 JP2619264B2 (en) | 1997-06-11 |
Family
ID=15606601
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP63155463A Expired - Lifetime JP2619264B2 (en) | 1988-06-23 | 1988-06-23 | Reprocessing of lubricating waste oil |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2619264B2 (en) |
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06509604A (en) * | 1992-05-19 | 1994-10-27 | モホーク カナダ リミテッド | Waste lubricating oil disposal method |
JP2003082382A (en) * | 2001-09-14 | 2003-03-19 | Japan Atom Energy Res Inst | Method for purifying waste lubricating oil by water addition centrifugation |
WO2003044141A3 (en) * | 2001-11-20 | 2003-07-17 | Jozsef Koszta | Process for the purification of contaminated oils |
KR20030069367A (en) * | 2002-02-20 | 2003-08-27 | 대양대체에너지 주식회사 | Method for extracting an emulsion type fuel oil from all sorts of defective oil and apparatus for the same |
JP2011218426A (en) * | 2010-04-13 | 2011-11-04 | Sumitomo Metal Ind Ltd | Lubricating oil cleaning device and drawing bench equipped therewith, as well as cleaning method of lubricating oil, and drawing method using thereof |
WO2012009749A1 (en) * | 2010-07-19 | 2012-01-26 | Loyal Asset Development Limited | Process for treating used oil |
US8299001B1 (en) | 2006-09-18 | 2012-10-30 | Martin De Julian Pablo | Process for recovering used lubricating oils using clay and centrifugation |
CN107569901A (en) * | 2017-10-10 | 2018-01-12 | 杨继新 | Reduce oil product carbon residue device |
US10164651B2 (en) | 2015-10-22 | 2018-12-25 | Socionext Inc. | A/D converter, A/D conversion method, and semiconductor integrated circuit |
CN113604810A (en) * | 2021-09-07 | 2021-11-05 | 鹰普机械(宜兴)有限公司 | Sand casting cleaning method |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5112801A (en) * | 1974-07-23 | 1976-01-31 | Toa Nenryo Kogyo Kk | Junkatsuyuhaiyuno saiseiho |
JPS54142206A (en) * | 1978-04-27 | 1979-11-06 | Degussa | Regeneration of used lubricant |
-
1988
- 1988-06-23 JP JP63155463A patent/JP2619264B2/en not_active Expired - Lifetime
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5112801A (en) * | 1974-07-23 | 1976-01-31 | Toa Nenryo Kogyo Kk | Junkatsuyuhaiyuno saiseiho |
JPS54142206A (en) * | 1978-04-27 | 1979-11-06 | Degussa | Regeneration of used lubricant |
Cited By (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06509604A (en) * | 1992-05-19 | 1994-10-27 | モホーク カナダ リミテッド | Waste lubricating oil disposal method |
JP2003082382A (en) * | 2001-09-14 | 2003-03-19 | Japan Atom Energy Res Inst | Method for purifying waste lubricating oil by water addition centrifugation |
WO2003044141A3 (en) * | 2001-11-20 | 2003-07-17 | Jozsef Koszta | Process for the purification of contaminated oils |
KR20030069367A (en) * | 2002-02-20 | 2003-08-27 | 대양대체에너지 주식회사 | Method for extracting an emulsion type fuel oil from all sorts of defective oil and apparatus for the same |
US8299001B1 (en) | 2006-09-18 | 2012-10-30 | Martin De Julian Pablo | Process for recovering used lubricating oils using clay and centrifugation |
JP2011218426A (en) * | 2010-04-13 | 2011-11-04 | Sumitomo Metal Ind Ltd | Lubricating oil cleaning device and drawing bench equipped therewith, as well as cleaning method of lubricating oil, and drawing method using thereof |
WO2012009749A1 (en) * | 2010-07-19 | 2012-01-26 | Loyal Asset Development Limited | Process for treating used oil |
US10164651B2 (en) | 2015-10-22 | 2018-12-25 | Socionext Inc. | A/D converter, A/D conversion method, and semiconductor integrated circuit |
CN107569901A (en) * | 2017-10-10 | 2018-01-12 | 杨继新 | Reduce oil product carbon residue device |
CN107569901B (en) * | 2017-10-10 | 2023-01-06 | 杨继新 | Reduce oil carbon residue device |
CN113604810A (en) * | 2021-09-07 | 2021-11-05 | 鹰普机械(宜兴)有限公司 | Sand casting cleaning method |
Also Published As
Publication number | Publication date |
---|---|
JP2619264B2 (en) | 1997-06-11 |
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