JPH0347881B2 - - Google Patents

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Publication number
JPH0347881B2
JPH0347881B2 JP62218055A JP21805587A JPH0347881B2 JP H0347881 B2 JPH0347881 B2 JP H0347881B2 JP 62218055 A JP62218055 A JP 62218055A JP 21805587 A JP21805587 A JP 21805587A JP H0347881 B2 JPH0347881 B2 JP H0347881B2
Authority
JP
Japan
Prior art keywords
oil
water
settling tank
waste oil
collector bowl
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 - Lifetime
Application number
JP62218055A
Other languages
Japanese (ja)
Other versions
JPS6463006A (en
Inventor
Hisayoshi Nakajima
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.)
SANNETSU KK
Original Assignee
SANNETSU KK
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 SANNETSU KK filed Critical SANNETSU KK
Priority to JP21805587A priority Critical patent/JPS6463006A/en
Publication of JPS6463006A publication Critical patent/JPS6463006A/en
Publication of JPH0347881B2 publication Critical patent/JPH0347881B2/ja
Granted legal-status Critical Current

Links

Description

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

(発明の目的) この発明は、金属加工における切削油、各種機
械の潤滑油等の廃油を精製して再生する際の水分
および固形夾雑物の静置による沈降分離手段に関
するもので、沈降分離能率を増進するとともに、
沈降分離に引続く濾過等による精製作業を容易に
し、廃油再生の経済性を向上することがその目的
である。 前記のような廃油の再生作業には精製の経済性
を確保するため、当初に沈降分離作業が行われ
る。この沈降分離は廃油に混入している水分や金
属くず、作業手袋やウエスのような繊維品のくず
などの夾雑物を油分から比重差により分離するた
め、廃油をセツトリングタンクに収容し、加温に
よる緩和な対流により沈降分離を促進し、沈澱し
た水分、夾雑物を適時タンクの底から抜き取るの
である。このような沈降分離処理には相当の時間
が必要であつて、この処理を急げば処理後の油分
の純度が低下する。そして処理後の油分の純度が
低いと、引続き行われる濾過作業に困難を来し、
または吸着助剤等の副資材を多量に消費するとと
もに精製油の収率を低下させ、あるいは大型の濾
過装置が必要になるなど、廃油再生作業の経済性
を著しく低下させるのである。 従つて、この発明は、受入れた廃油の沈降分離
処理の能率を増進すること、すなわち、処理時間
の短縮とともに処理済の油分の良好な純度が確保
できる手段を提供し、かくして引続く濾過等の精
製作業の容易化をはかり、最終的に廃油再生の経
済性を向上するのがその目的である。 (発明の構成) この発明にかかる廃油再生用沈降分離装置は、
セツトリングタンク1の底端を閉鎖型のコレクタ
ーボウル2に接続するとともに、バイパス管3を
介してコレクターボウル2の頂部をセツトリング
タンク1の胴部に接続してなるものである。ただ
し、セツトリングタンク1は廃油の供給を受けて
これを静置し、これに含まれる固形夾雑物を沈降
させるのに使用されるタンクである。 この発明の構成は上記した通りであるが、その
理解の便のため、まず、一実施を示した第1図を
参照してこの発明を説明すれば、1はセツトリン
グタンクで、ドラム缶その他適宜な手段により供
給を受けた廃油を静置し、これに含まれる水や固
形物等の夾雑物を沈降させるのに使用する。この
セツトリングタンク1は、図示を省略するが、ヒ
ートコイル、電気ヒーター等を使用し、収容され
た廃油を加温してその粘度低下をはかることが普
通行われる。 セツトリングタンク1の底端は閉鎖型のコレク
ターボウル2に接続されている一方、コレクター
ボウル2の頂部はバイパス管3を介してセツトリ
ングタンク1の胴部に接続されている。特にこの
実施例によればコレクターボウル2には内部の定
水位を検知して動作する水位センサー4が設けて
あり、ドレン管21には水位センサーに応動する
電磁弁5が介挿されている。 なお、図示した実施例の手動開閉弁V1,V2
ドレン管6の吐出口を開閉するためである。ま
た、セツトリングタンク1とコレクターボウル2
との接続部の手動開閉弁V3およびバイパス管3
の手動開閉弁V4は後述のように必要の際、セツ
トリングタンク1の液をコレクターボウル2から
切離すためである。なお、手動開閉弁V5はセツ
トリングタンク1に廃油原液を収容したままでコ
レクターボウル2を空虚にする場合の給気弁であ
る。また、セツトリングタンク1およびコレクタ
ーボウル2の器壁にはそれらの内部の点検や補修
作業のため適当なマンホールを設けるのがよい。
もちろん、図示の装置は地上に設置する場合、図
示を省略した適当な架台で支持する必要があるの
はいうまでもない。 ここで前記した実施例装置の使用法を説明すれ
ば、まず、沈降分離の対象物である廃油原液をセ
ツトリングタンク1に注入収容する。注入の際、
手動開閉弁V3,V4を全閉しておき、注入終了時
にこれらの手動開閉弁V3,V4を徐々に全開した
方がよい。 注入して暫時の後には廃油原液の動揺が収ま
り、混入物である水、金属粉、繊維屑などの沈降
がはじまり、コレクターボウル2内の水位が上昇
するのと同時に、水を含んだ繊維くずや金属粉な
ど比重の大きい固形物がコレクターボウル2の底
部に沈澱する。この間、沈降が不充分で油中に分
散している微細な固形物や水の粒子はコレクター
ボウル2内の液の上層に存在しており、これら微
細な粒子を含む油分は自然対流によりバイパス管
3中を上昇し、セツトリングタンク1に戻され、
その戻された粒子はセツトリングタンク1内でた
がいに付着しあつて油分から分離沈降しやすくな
り、セツトリングタンク1の底から再びコレクタ
ーボウル2に降下して沈澱する。このようにして
コレクターボウル2内の水位が一定水準に高まれ
ば、水位センサー4がこれを検知し、その検知信
号により電磁弁5が開き、従つてコレクターボウ
ル2における水その他の沈澱物が排出される。電
磁弁5の開弁期間は、水位センサー4に付設した
タイマーにより、または適当な水位の変化によつ
て電磁弁5の閉鎖信号を発生する水位センサー4
を選択することにより、これを最適に制御するこ
とができる。かくして、電磁弁5を介してドレン
管21から排出された排出物を目視して水分、夾
雑物が僅少となり、有意の油分が混入してきたと
き、処理作業を終了し、後続する濾過等の精製工
程に移管する。 以下、第1図に示す実施例を使用した沈降分離
の処理成績を従来装置例による処理成績と対比し
て掲げる。実施例装置の寸度、容積はつぎの通り
であり、従来装置例は実施例装置からコレクター
ボウル2およびバイパス管3を除去したセツトリ
ングタンク1である。 セツトリングタンク1 内径D=900mm 高さH=1110mm 容積=401 コレクターボウル2 内径d=450mm 高さh=550mm 容積=87 バイパス管3 内径=27.6mm 落差K=450mm 第1表に、上記した実施例装置および従来例装
置を使用した処理例における条件を示す。ただ
し、処理例1および処理例2はいずれも前記実施
例装置に関するもの、対照例は従来例装置に関す
るもので、被処理廃油原液は圧延用ギヤーオイル
(シエル・オラマ#220)の廃油で主な混入物は
水、金属粉、および繊維くずであると認められ
た。
(Object of the invention) The present invention relates to a sedimentation separation means by leaving water and solid impurities still when refining and regenerating waste oil such as cutting oil in metal processing and lubricating oil for various machines, and improves sedimentation separation efficiency. In addition to promoting
The purpose is to facilitate refining operations such as filtration following sedimentation separation, and to improve the economic efficiency of waste oil regeneration. In the waste oil regeneration work as described above, sedimentation separation work is initially performed in order to ensure the economic efficiency of refining. In this sedimentation separation, waste oil is stored in a settling tank and processed in order to separate impurities such as water, metal scraps, and scraps of textiles such as work gloves and rags from the oil based on the difference in specific gravity. The gentle convection caused by the temperature promotes sedimentation and separation, and the precipitated moisture and impurities are removed from the bottom of the tank in a timely manner. Such sedimentation separation treatment requires a considerable amount of time, and if this treatment is rushed, the purity of the oil after treatment will be reduced. If the purity of the oil after treatment is low, it will be difficult to carry out the subsequent filtration work.
Alternatively, a large amount of auxiliary materials such as adsorption aids are consumed, the yield of refined oil is reduced, or a large filtration device is required, which significantly reduces the economic efficiency of waste oil regeneration work. Accordingly, the present invention provides a means for increasing the efficiency of the sedimentation separation treatment of incoming waste oil, i.e., by shortening the treatment time and ensuring good purity of the treated oil, thus reducing the need for subsequent filtration, etc. The purpose is to facilitate refining operations and ultimately improve the economic efficiency of waste oil recycling. (Structure of the Invention) The sedimentation separator for waste oil regeneration according to the present invention includes:
The bottom end of the settling tank 1 is connected to a closed collector bowl 2, and the top of the collector bowl 2 is connected to the body of the settling tank 1 via a bypass pipe 3. However, the settling tank 1 is a tank used to receive a supply of waste oil, leave it stationary, and settle solid impurities contained therein. The structure of the present invention is as described above, but for ease of understanding, the present invention will first be explained with reference to FIG. 1 showing one implementation. It is used to leave waste oil supplied by suitable means to settle out impurities such as water and solids contained therein. Although not shown in the drawings, this settling tank 1 typically uses a heat coil, an electric heater, etc. to heat the contained waste oil to reduce its viscosity. The bottom end of the settling tank 1 is connected to a closed collector bowl 2, while the top of the collector bowl 2 is connected to the body of the settling tank 1 via a bypass pipe 3. In particular, according to this embodiment, the collector bowl 2 is provided with a water level sensor 4 that operates by detecting a constant water level inside, and the drain pipe 21 is fitted with an electromagnetic valve 5 that responds to the water level sensor. The manual on-off valves V 1 and V 2 in the illustrated embodiment are for opening and closing the discharge port of the drain pipe 6. In addition, settling tank 1 and collector bowl 2
Manual on-off valve V 3 and bypass pipe 3 at the connection with
The manual on-off valve V4 is for separating the liquid in the settling tank 1 from the collector bowl 2 when necessary, as will be described later. The manual on-off valve V5 is an air supply valve used when the collector bowl 2 is emptied while the settling tank 1 still contains the waste oil concentrate. Further, it is preferable to provide suitable manholes in the walls of the settling tank 1 and the collector bowl 2 for inspection and repair work inside them.
Of course, when the illustrated apparatus is installed on the ground, it goes without saying that it needs to be supported by a suitable pedestal (not shown). To explain how to use the apparatus of the above embodiment, first, a waste oil stock solution, which is the object of sedimentation separation, is injected into the settling tank 1 and stored therein. During injection,
It is better to keep the manual on-off valves V 3 and V 4 fully closed, and then gradually fully open these manual on-off valves V 3 and V 4 at the end of injection. After a while after injection, the agitation of the waste oil stock solution subsides, and contaminants such as water, metal powder, and fiber waste begin to settle.At the same time, the water level in the collector bowl 2 rises, and the water-containing fiber waste begins to settle. Solids with high specific gravity, such as metal powder and metal powder, settle at the bottom of the collector bowl 2. During this time, fine solid matter and water particles that have not settled sufficiently and are dispersed in the oil are present in the upper layer of the liquid in the collector bowl 2, and the oil containing these fine particles is moved through the bypass pipe by natural convection. 3 and returned to settling tank 1.
The returned particles adhere to each other in the settling tank 1 and are easily separated from the oil and settle, and then descend from the bottom of the settling tank 1 to the collector bowl 2 again and settle. When the water level in the collector bowl 2 rises to a certain level in this way, the water level sensor 4 detects this, and the detection signal opens the solenoid valve 5, so that water and other sediments in the collector bowl 2 are discharged. Ru. The opening period of the electromagnetic valve 5 is determined by a timer attached to the water level sensor 4, or by the water level sensor 4, which generates a closing signal for the electromagnetic valve 5 according to an appropriate change in the water level.
This can be optimally controlled by selecting . In this way, when the waste discharged from the drain pipe 21 via the solenoid valve 5 is visually inspected and water and impurities are found to be minimal and significant oil has been mixed in, the treatment operation is completed and subsequent purification such as filtration is performed. Transfer to process. The treatment results of sedimentation separation using the example shown in FIG. 1 will be listed below in comparison with the treatment results of the conventional apparatus example. The dimensions and volume of the apparatus of the embodiment are as follows, and the example of the conventional apparatus is a settling tank 1 obtained by removing the collector bowl 2 and bypass pipe 3 from the apparatus of the embodiment. Settling tank 1 Inner diameter D = 900mm Height H = 1110mm Volume = 401 Collector bowl 2 Inner diameter d = 450mm Height h = 550mm Volume = 87 Bypass pipe 3 Inner diameter = 27.6mm Head K = 450mm Table 1 shows the implementation described above. Conditions in a processing example using an example device and a conventional example device are shown. However, both Treatment Example 1 and Treatment Example 2 are related to the above-mentioned example device, and the control example is related to the conventional example device, and the waste oil stock solution to be treated is mainly waste oil from rolling gear oil (Ciel Orama #220). Contaminants were found to be water, metal powder, and textile debris.

【表】 第2表に、前記処理の結果を示す。ただし検査
は処理終了時のセツトリングタンク1中の残液で
ある処理済の液を対象とした。
[Table] Table 2 shows the results of the above treatment. However, the test targeted the treated liquid, which is the residual liquid in the settling tank 1 at the end of the treatment.

【表】 上掲の成績から、この発明にかかる装置によれ
ば、従来装置による処理と較べ、静置分離処理後
の廃油中に残留する固形物および水分がかなり少
量になつており、しかも、処理の所要時間が短か
いことがわかる。実施例装置における水分その他
の沈澱物の排出は水位センサー4に応動する電磁
弁5によつて自動的に高能率に行われるのに対
し、従来例の使用においては、手動開閉弁V3
操作を手動で行い、しかも、水の分離が良好でな
いので、単位時間における弁の操作回数が少くな
り、従つて、排出された沈澱物の外見が実施例装
置による場合と同程度と認められるまで弁操作を
行うと長時間を要するためである。 以上、前記した実施例による廃油処理成績を記
載したのであるが、コレクターボウル2内の水位
センサー4と吐出用の電磁弁5の組合せは、沈澱
物の排出能率の向上には役立つても、水分、夾雑
物の分離沈降の促進に役立つわけではない。 ところで、この発明は前記のようにしてなり、
コレクターボウル2の頂部のセツトリングタンク
1の胴部を接続するバイパス管3の前記分離沈降
促進への影響をしらべるため、つぎの卓上試験を
行つた。なお、水分、夾雑物の油分からの分離促
進が顕著であればそれにより再生油の性状が向上
し、あわせて最終的に廃油処理時間の短縮化に好
ましい影響を与えるのはいうまでもない。試験に
使用した装置の一方は前記した実施例装置に対応
する構造で、透明プラスチツクからなる小型のも
の(第2図)である。他方は前記した従来例装置
に対応する構造で、やはり透明プラスチツクから
なる小型のもの(第3図)である。セツトリング
タンク1の容量は5、コレクターボウル2の容
量は1である。ただし、コレクターボウル2に
は水位センサーを設けない。被処理廃油はつぎの
4種類である。 ステンレス鋼粉末を含む90cstの切削油(切
削油2種17号) 銅粉末を含むと同種の切削油 ステンレス鋼粉末を含む40cstの切削油(切
削油2種16号) 銅粉末を含むと同種の切削油 ただし、各上記廃油はいずれも水およびウエ
ス、作業手袋等の素材と思われる繊維くずを含ん
でおり、金属粉末についてはほとんどが50メツシ
ユふるいを通過した。 上掲4種類の廃油試料につき本発明装置(第2
図)および従来装置(第3図)を用いて沈降分離
処理を行つた結果は第3表ないし第6表に示す通
りである。ただし、試験方法は下記の通りであ
る。 (1) 試料は入手した同一の廃油原液を充分に撹拌
し、本発明装置および従来装置にそれぞれ4
づつ仕込んだ。 (2) 静置時間はいずれも24時間とし、その間本発
明装置では弁v1,v5は閉鎖、弁v3,v4は全開と
する。 (3) 静置時間における試料の温度は、試料,
は20℃、試料,は40℃に保存する。 (4) 静置時間経過時における排出物の抜取りは本
発明装置では弁v1から、従来装置では弁v3から
それぞれ行い、排出物に有意の油分が含まれて
いると認められたとき抜取りを終る。 (5) 排出物は10μ瀘紙で濾過し、濾滓を加温乾燥
し、揮発油により脱油乾燥後秤量し、さらに焼
灼後秤量し、この秤量を金属粉末の重量とし、
焼灼減量は繊維類の重量とする。
[Table] From the above results, it can be seen that with the apparatus of the present invention, the amount of solid matter and water remaining in the waste oil after static separation treatment is considerably smaller than that with the conventional apparatus. It can be seen that the time required for processing is short. In the device of the embodiment, the discharge of moisture and other precipitates is automatically and efficiently carried out by the solenoid valve 5 that responds to the water level sensor 4, whereas in the use of the conventional example, the discharge of moisture and other precipitates is performed manually by operating the on-off valve V3 . is carried out manually, and since the water separation is not good, the number of valve operations per unit time is reduced. This is because it takes a long time to perform the operation. The results of waste oil treatment according to the above embodiments have been described above. Although the combination of the water level sensor 4 in the collector bowl 2 and the discharge solenoid valve 5 is useful for improving the efficiency of discharging sediment, , it does not help promote the separation and sedimentation of impurities. By the way, this invention is made as described above,
In order to examine the effect of the bypass pipe 3 connecting the body of the settling tank 1 at the top of the collector bowl 2 on the promotion of separation and sedimentation, the following tabletop test was conducted. It goes without saying that if the separation of water and impurities from the oil is significantly promoted, the properties of the recycled oil will be improved, and this will ultimately have a favorable effect on shortening the waste oil treatment time. One of the devices used in the test was a small device made of transparent plastic (FIG. 2), and had a structure corresponding to the device of the embodiment described above. The other device has a structure corresponding to the conventional device described above, and is also a small device made of transparent plastic (FIG. 3). The capacity of the settling tank 1 is 5, and the capacity of the collector bowl 2 is 1. However, the collector bowl 2 is not provided with a water level sensor. There are four types of waste oil to be treated: 90 cst cutting oil containing stainless steel powder (cutting oil type 2 No. 17) Similar cutting oil containing copper powder 40 cst cutting oil containing stainless steel powder (cutting oil type 2 No. 16) Similar cutting oil containing copper powder Cutting oil However, all of the above waste oils contained water and fiber waste, which was thought to be the material of rags, work gloves, etc., and most of the metal powder passed through a 50-mesh sieve. The device of the present invention (second
Tables 3 to 6 show the results of sedimentation separation using the conventional apparatus (Fig. 3) and the conventional apparatus (Fig. 3). However, the test method is as follows. (1) For the sample, the same waste oil stock solution obtained was thoroughly stirred, and the sample was placed in the device of the present invention and the conventional device at 40°C.
I prepared it one by one. (2) The standing time is 24 hours, during which time valves v 1 and v 5 are closed and valves v 3 and v 4 are fully opened in the device of the present invention. (3) The temperature of the sample during the standing time is
Store at 20℃ and samples at 40℃. (4) After the standing time has elapsed, the discharged material is extracted from valve v 1 in the device of the present invention, and from valve v 3 in the conventional device, and is removed when it is recognized that the discharged material contains significant oil. end. (5) The discharged material is filtered through 10 μ filter paper, the filter cake is heated and dried, deoiled with volatile oil, dried and weighed, and further weighed after cauterization, and this weighed amount is taken as the weight of the metal powder.
The loss due to cauterization is the weight of the fibers.

【表】【table】

【表】【table】

【表】【table】

【表】 さらに、この発明装置による沈降分離処理が油
中水分の除去にどのような効果があるのかを確認
するため、つぎの卓上試験を行つた。試験方法は
つぎの通りである。 (1) 試料として前記した金属粉等を含む前掲試料
およびにそれぞれ酸性白土を加えて撹拌濾
過することにより水分および固形物をほぼ完全
に除いたものをとり、それぞれに水道水を6%
添加し、強力に撹拌して水をよく分散させたも
のをそれぞれ試料および試料とする。 (2) まず、前記した卓上試験用の本発明装置(第
2図)および従来装置(第3図)に試料をそ
れぞれ4づつ仕込み、20℃に保持しつつ24時
間静置する。静置時間における弁v1,v3,v4
v5の開閉は前記した試料ないしについての
卓上試験に準ずる。 (3) 静置時間終了時において、本発明装置では弁
v1、従来装置では弁v3をそれぞれ開き、沈澱水
を若干の油分とともにメスシリンダーに受け、
そのまま24時間静置した後水層を計量する。 (4) つぎに、試料についても上掲(2)、(3)と同様
の処理を行う。ただし、装置内の試料の温度は
40℃に保持する。 第7表は以上の卓上試験による油水分離成績で
ある。
[Table] Furthermore, in order to confirm what kind of effect the sedimentation separation process using this invention apparatus has on removing water in oil, the following tabletop test was conducted. The test method is as follows. (1) Take the above-mentioned sample containing metal powder, etc. as a sample, add acid clay to each sample, stir and filtrate to remove water and solids almost completely, and add 6% tap water to each sample.
Add the water and stir vigorously to thoroughly disperse the water, and use these as the sample and sample, respectively. (2) First, four samples each were placed in the apparatus of the present invention (FIG. 2) and the conventional apparatus (FIG. 3) for the above-mentioned tabletop test, and were left standing at 20° C. for 24 hours. Valves v 1 , v 3 , v 4 during standing time,
v Opening and closing of 5 is in accordance with the tabletop test for the sample described above. (3) At the end of the standing time, the device of the present invention closes the valve.
In the conventional device, valves V 1 and V 3 are opened, and the precipitated water is received into the graduated cylinder along with some oil.
After allowing it to stand for 24 hours, weigh the aqueous layer. (4) Next, the sample is treated in the same manner as in (2) and (3) above. However, the temperature of the sample inside the device is
Hold at 40°C. Table 7 shows the oil/water separation results from the above tabletop test.

【表】 すなわち、上記試験により、前記したバイパス
管3の存在は、水分、夾雑物の油分からの分離沈
降作用に顕著な影響を与えることが確認できた。 (発明の効果) 前掲の各試験成績から明らかなように、この発
明装置は、被処理廃油の粘度が比較的高い場合、
または低い場合にかかわらず、また室温付近で処
理が行われる場合でも、加温処理の場合でも、従
来装置と較べて油分からの水分、夾雑物の分離沈
降性能が著しく高い。すなわち、この発明によれ
ば、廃油原液からの水分、夾雑物の沈降分離がこ
のように高能率に行われるので、静置分離処理に
引続いて廃油再生に必要な濾過工程における吸着
用助剤の消費を著しく減少できるとともに、濾過
装置その他の設備の小型化、精製時間の短縮など
に伴う所要エネルギー減少の効果をもたらし、廃
油再生処理のコスト低減に寄与するところがすこ
ぶる顕著である。
[Table] That is, the above test confirmed that the presence of the bypass pipe 3 had a significant effect on the separation and sedimentation of water and impurities from oil. (Effects of the Invention) As is clear from the test results listed above, the device of the present invention is effective when the viscosity of the waste oil to be treated is relatively high.
Regardless of whether the temperature is low, whether the treatment is performed near room temperature, or the treatment is heated, the separation and sedimentation performance of water and impurities from oil is significantly higher than that of conventional equipment. That is, according to the present invention, since the sedimentation separation of water and impurities from the waste oil stock solution is performed with high efficiency, the adsorption aid in the filtration process necessary for waste oil regeneration following the static separation treatment is In addition to significantly reducing the consumption of oil, it also has the effect of reducing the energy required by downsizing filtration equipment and other equipment, shortening refining time, etc., and significantly contributes to reducing the cost of waste oil recycling processing.

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

第1図は本発明の一実施例の縦断骨格図、第2
図は卓上試験における本発明装置の縦断骨格図、
第3図は第2図に対応する従来装置の縦断骨格図
である。 1はセツトリングタンク、2はコレクターボウ
ル、3はバイパス管、4は水位センサー、5は電
磁弁、6はドレン管、V1,V2,V3,V4,V5
v1,v3,v4,v5は手動開閉弁である。
Fig. 1 is a longitudinal sectional view of one embodiment of the present invention;
The figure is a longitudinal skeletal diagram of the device of the present invention in a tabletop test.
FIG. 3 is a longitudinal sectional view of the conventional device corresponding to FIG. 2. 1 is a settling tank, 2 is a collector bowl, 3 is a bypass pipe, 4 is a water level sensor, 5 is a solenoid valve, 6 is a drain pipe, V 1 , V 2 , V 3 , V 4 , V 5 ,
v 1 , v 3 , v 4 , and v 5 are manual on-off valves.

Claims (1)

【特許請求の範囲】[Claims] 1 廃油の供給を受けてこれを静置し、これに含
まれる水および固形夾雑物を沈降させるセツトリ
ングタンク1の底端を閉鎖型のコレクターボウル
2に接続するとともに、バイパス管3を介してコ
レクターボウル2の頂部をセツトリングタンク1
の胴部に接続してなる廃油再生用沈降分離装置。
1. The bottom end of the settling tank 1, which receives waste oil and allows it to settle and settles the water and solid impurities contained therein, is connected to a closed collector bowl 2, and is also Place the top of the collector bowl 2 into the settling tank 1.
Sedimentation separator for waste oil regeneration connected to the body of.
JP21805587A 1987-09-02 1987-09-02 Precipitator for waste oil regeneration Granted JPS6463006A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP21805587A JPS6463006A (en) 1987-09-02 1987-09-02 Precipitator for waste oil regeneration

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP21805587A JPS6463006A (en) 1987-09-02 1987-09-02 Precipitator for waste oil regeneration

Publications (2)

Publication Number Publication Date
JPS6463006A JPS6463006A (en) 1989-03-09
JPH0347881B2 true JPH0347881B2 (en) 1991-07-22

Family

ID=16713944

Family Applications (1)

Application Number Title Priority Date Filing Date
JP21805587A Granted JPS6463006A (en) 1987-09-02 1987-09-02 Precipitator for waste oil regeneration

Country Status (1)

Country Link
JP (1) JPS6463006A (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5246734A (en) * 1975-10-11 1977-04-13 Hitachi Ltd Reader circuit of magnetic bubble storage
JPS5652007B2 (en) * 1972-06-05 1981-12-09

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5652007U (en) * 1979-09-25 1981-05-08

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5652007B2 (en) * 1972-06-05 1981-12-09
JPS5246734A (en) * 1975-10-11 1977-04-13 Hitachi Ltd Reader circuit of magnetic bubble storage

Also Published As

Publication number Publication date
JPS6463006A (en) 1989-03-09

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