Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPH0757357B2 - Circulation use method of factory treated water - Google Patents
[go: Go Back, main page]

JPH0757357B2 - Circulation use method of factory treated water - Google Patents

Circulation use method of factory treated water

Info

Publication number
JPH0757357B2
JPH0757357B2 JP62092172A JP9217287A JPH0757357B2 JP H0757357 B2 JPH0757357 B2 JP H0757357B2 JP 62092172 A JP62092172 A JP 62092172A JP 9217287 A JP9217287 A JP 9217287A JP H0757357 B2 JPH0757357 B2 JP H0757357B2
Authority
JP
Japan
Prior art keywords
water
treated water
wastewater
liquid
cleaning
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
JP62092172A
Other languages
Japanese (ja)
Other versions
JPS63258698A (en
Inventor
幸夫 茂長
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.)
Kubota Corp
Original Assignee
Kubota Corp
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 Kubota Corp filed Critical Kubota Corp
Priority to JP62092172A priority Critical patent/JPH0757357B2/en
Publication of JPS63258698A publication Critical patent/JPS63258698A/en
Publication of JPH0757357B2 publication Critical patent/JPH0757357B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Landscapes

  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は機械加工品の洗浄廃液や表面処理の為の前処理
用に利用された処理廃水を浄化再生して循環利用する方
法に関し、詳細には切屑や油脂等によって汚染された廃
液を効率良く清浄化して再利用することのできる工場処
理水の循環利用方法に関するものである。
Description: TECHNICAL FIELD The present invention relates to a method for purifying, recycling, and recycling the treated wastewater used for cleaning waste liquid of machined products and pretreatment for surface treatment, and recycling. The present invention relates to a recycling method of factory treated water that can efficiently purify and reuse waste liquid contaminated with chips, oils and fats.

[従来の技術] 自動車やトラクタ等の製造工場では、研削や切削加工さ
れた機械部品に対する洗浄工程が設けられ、又塗装等を
含む各種表面処理を行なう前にも洗浄工程を設けるのが
一般的である。これらのうち例えば上記機械部品を洗浄
する工程に関して、先に本出願人は特公昭59−8434号を
提出し、洗浄後の廃水を浄化して再利用するクローズド
方式の洗浄装置を提出した。第5図は機械加工々程にお
ける洗浄水再利用の概略を示す説明図である。
[Prior Art] In a factory for manufacturing automobiles, tractors, etc., it is common to provide a cleaning process for machine parts that have been ground or cut, and also provide a cleaning process before performing various surface treatments such as painting. Is. Among these, for example, regarding the process of cleaning the above-mentioned machine parts, the present applicant has previously filed Japanese Patent Publication No. 59-8434, and has submitted a closed type cleaning device for purifying and reusing waste water after cleaning. FIG. 5 is an explanatory diagram showing an outline of reuse of cleaning water in the machining process.

第5図において、加工完了後の機械部品は矢印Aに沿っ
て搬送されており、搬送方向に21a,21b,21cの位置を通
過しているものとする。21a〜21cの上方にはノズル22a,
22b,22cが設けられ、それらから洗浄水が噴出される。
洗浄水の清浄度はノズル22a,22b,22cにおいて変りはな
いが、洗浄順の関係から21aの位置より落下する洗浄廃
水がもっとも汚染されており、21b,21cと左へ行くにつ
れて汚染度が少なくなる。そこで洗浄廃水の落下を受け
入れるタンク23には図に示す様な仕切板32を設けて左側
を洗浄廃水希釈室B、右側を洗浄廃水濃縮室Cに分け、
これらの室B,Cは仕切板32の底部で連通させておく。希
釈室B内の比較的きれいな洗浄廃水(以下希釈廃水とい
う)ポンプ4aや加熱装置(図示せず)等を付設した循環
ライン4を経てノズル22a〜22cに循環され、再利用され
る。一方濃縮室C内にある汚染度の高い洗浄廃水(以下
濃縮廃水という)はポンプ5aを設けた引抜ライン5から
カランドリア6へ送給され、スチームライン11から供給
される高温スチームによって加熱される。この加熱によ
って得られる蒸気は清浄度を回復したものであり、デミ
スター等を経て更に浄化された後凝縮器7へ送られ、凝
縮処理水としてタンク9に貯留され、ポンプ16aによっ
てライン16を経て前記循環ライン4中の希釈廃水と合流
させた後、再利用される。他方カランドリア6によって
さらに濃縮された高汚染液(図では濃縮液と記す)は排
出ライン12から燃焼炉14へ送られて焼却処理される。
In FIG. 5, it is assumed that the machine component after processing is conveyed along the arrow A and passes through the positions 21a, 21b, 21c in the conveying direction. Above the 21a to 21c is a nozzle 22a,
22b and 22c are provided, and wash water is jetted from them.
The cleanliness of the wash water does not change at the nozzles 22a, 22b, 22c, but the washing wastewater that drops from the position of 21a is the most polluted due to the order of washing, and the pollution degree decreases toward 21b, 21c and left. Become. Therefore, a partition plate 32 as shown in the figure is provided in the tank 23 that receives the fall of the washing wastewater, and the left side is divided into the washing wastewater diluting chamber B and the right side is divided into the washing wastewater concentrating chamber C,
These chambers B and C are communicated with each other at the bottom of the partition plate 32. It is circulated to the nozzles 22a to 22c through a circulation line 4 provided with a relatively clean cleaning wastewater (hereinafter referred to as “dilution wastewater”) pump 4a, a heating device (not shown) and the like in the dilution chamber B, and is reused. On the other hand, highly contaminated cleaning wastewater (hereinafter referred to as concentrated wastewater) in the concentrating chamber C is sent from the drawing line 5 provided with the pump 5a to the calandria 6 and heated by the high temperature steam supplied from the steam line 11. The steam obtained by this heating has recovered the cleanliness, is further purified through a demister or the like, and is then sent to the condenser 7, stored in the tank 9 as condensed water, and pumped through the line 16 by the pump 16a. After being combined with the diluted wastewater in the circulation line 4, it is reused. On the other hand, the highly polluted liquid (referred to as a concentrated liquid in the figure) further concentrated by the calandria 6 is sent from the discharge line 12 to the combustion furnace 14 and incinerated.

一方第4図は表面処理の前工程における洗浄水の再利用
装置を示す説明図であり、第5図の例と相違する点は次
の通りである。即ち第4図における処理槽群1にはタン
ク3a中の浄化水Dを供給管2aを通して供給し、廃水Eは
排出管2bを介してタンク3b内へ貯留し、該廃水Eは第5
図例と同様カランドリア6に送られる。カランドリア6
によって分離された蒸気は凝縮器7において凝縮液化さ
れた後貯留槽24に貯され、一部はバイパスライン30を経
て処理槽群1に供給され、第5図の場合における21aの
位置に相当する洗浄水として使用される。残部はさらに
ダイヤマルス活性炭吸着塔25及びイオン交換樹脂膜処理
塔26によって一層の浄化処理を受けてからタンク3aへ供
給され、第5図の場合における21b,21cの位置に相当す
る洗浄水として使用される。
On the other hand, FIG. 4 is an explanatory diagram showing the reuse device of the washing water in the pre-process of the surface treatment, and the points different from the example of FIG. 5 are as follows. That is, the purified water D in the tank 3a is supplied to the treatment tank group 1 in FIG. 4 through the supply pipe 2a, and the waste water E is stored in the tank 3b through the discharge pipe 2b.
It is sent to Calandria 6 as in the illustrated example. Calandria 6
The vapor separated by is condensed and liquefied in the condenser 7 and then stored in the storage tank 24, and a part thereof is supplied to the processing tank group 1 through the bypass line 30 and corresponds to the position 21a in the case of FIG. Used as wash water. The remainder is further purified by the Diamals activated carbon adsorption tower 25 and the ion exchange resin membrane processing tower 26 and then supplied to the tank 3a, which is used as washing water corresponding to the positions 21b and 21c in the case of FIG. To be done.

[発明が解決しようとする問題点] 第4図に示したダイヤマルス活性炭吸着塔25及びイオン
交換樹脂膜処理塔26を使う方法では、活性炭やイオン交
換樹脂膜の寿命に限度がある為頻繁に取り換える必要が
生じ、純水製造コストが高くなってしまうという欠点が
あり、低コストで処理できる方法を開発することが望ま
れていた。
[Problems to be Solved by the Invention] The method using the Diamals activated carbon adsorption tower 25 and the ion exchange resin membrane treatment tower 26 shown in FIG. There is a drawback in that it needs to be replaced and the production cost of pure water becomes high, and it has been desired to develop a method capable of treating at low cost.

また第5図に示す凝縮器7によって得られライン16から
供給されてくる処理水は、循環ライン4を流れてくる希
釈廃水に比べて品質の改善されたものとなっているが、
多量の希釈廃水と合流して混合されてしまう為、結局の
ところノズル22a〜22cからは汚れた洗浄液が供給される
ことになり、その結果部品の洗浄効果が低下して後工程
に悪影響を及ぼしたり、或は洗浄水の総入れ換え時期を
早く迎えることになりたいへん不経済である。そのため
処理水及び希釈廃水の品質を何らかの手段で改善する方
法が必要とされていた。
Further, the treated water obtained by the condenser 7 shown in FIG. 5 and supplied from the line 16 has improved quality as compared with the diluted wastewater flowing in the circulation line 4,
Since a large amount of diluted wastewater merges and is mixed, the contaminated cleaning liquid is eventually supplied from the nozzles 22a to 22c, and as a result, the cleaning effect of the parts is reduced and the subsequent processes are adversely affected. Or, it would be very uneconomical to reach the time of total replacement of washing water sooner. Therefore, there has been a need for a method of improving the quality of treated water and diluted wastewater by some means.

[問題点を解決するための手段] 本発明の要旨は、蒸発後の凝縮水を液中燃焼装置で処理
することよって処理水中の低沸点油分を分離除去する工
程を実施する点に要旨があるものであり、これによって
従来の吸着式における諸欠点を解消し得ることとなっ
た。
[Means for Solving the Problems] The gist of the present invention is that the step of separating and removing the low boiling point oil component in the treated water is carried out by treating the condensed water after evaporation with a submerged combustion device. This has made it possible to eliminate various drawbacks in the conventional adsorption system.

[作用及び実施例] 第1図は本発明方法を利用した洗浄水の再利用装置を示
す概略説明図であり、表面処理の前工程として行なわれ
る洗廃水処理の場合を示し、第3図は同じく機械加工々
程における洗浄水再利用の場合を示すものである。但し
本発明方法は上記例示装置を使用する場合に限定され
ず、前・後記の主旨に沿って変更を加えた方法であって
も構わない。
[Operations and Examples] FIG. 1 is a schematic explanatory view showing an apparatus for reusing washing water using the method of the present invention, showing a case of washing wastewater treatment performed as a pre-step of surface treatment, and FIG. Similarly, it shows the case of reuse of cleaning water in the machining process. However, the method of the present invention is not limited to the case of using the above-mentioned exemplified apparatus, and may be a method in which changes are made in accordance with the gist of the preceding and the following.

第1図は、第4図の例におけるダイヤマルス活性炭吸着
塔25及びイオン交換樹脂膜処理塔26を液中燃焼装置15に
変更した点に特徴が存在するものである。該液中燃焼装
置15の詳細は第2図(断面説明図)に示す如く、密閉さ
れた箱体31の内部に液中バーナ17を配設したものであ
り、燃料ガス供給管19及び空気供給管18から夫々供給さ
れる燃料ガス及び空気を燃焼させ、発生する燃焼ガスを
供給管28から導入される未処理液と共に処理液F中へ噴
出するものである。その為処理液Fは上記燃焼ガスの保
有熱によって加熱されると共に撹拌され、処理液中の低
沸点油分やその他有機成分類を飛沫と共に排ガス管20か
ら取り出し、デミスター等によってこれらの飛沫が除去
された後燃焼炉14(第1図参照)によって焼却される。
FIG. 1 is characterized in that the Diamals activated carbon adsorption tower 25 and the ion exchange resin membrane treatment tower 26 in the example of FIG. As shown in FIG. 2 (cross-sectional explanatory view), the details of the submerged combustion device 15 are those in which a submerged burner 17 is provided inside a sealed box body 31, and a fuel gas supply pipe 19 and an air supply are provided. The fuel gas and the air respectively supplied from the pipe 18 are burned, and the generated combustion gas is jetted into the treatment liquid F together with the untreated liquid introduced from the supply pipe 28. Therefore, the treatment liquid F is heated by the heat of the combustion gas and stirred, and the low boiling point oil components and other organic components in the treatment liquid are taken out from the exhaust gas pipe 20 together with the droplets, and these droplets are removed by a demister or the like. After that, it is incinerated by the combustion furnace 14 (see FIG. 1).

従って第1図のカランドリア6[MVR(蒸気圧縮式蒸発
缶)や他の型式の蒸発缶を含む]によって蒸発させられ
更に凝縮器7で凝縮された処理水中に含有される低沸点
油分等は上記液中燃焼装置15によってこれをほぼ完全に
除去することができ、表面処理前工程のカチオン電着隔
膜冷却用水やカチオン電着ディップ水洗水として適用可
能な水質とすることができる。第1表は、廃水Eをカラ
ンドリア6によって濃縮液と処理水に分離し、さらに処
理水を液中燃焼装置15によって浄化した場合の水質変化
を示す。
Therefore, the low boiling point oil component contained in the treated water evaporated by the Calandria 6 [including MVR (vapor compression type evaporator) and other types of evaporators] in FIG. This can be almost completely removed by the submerged combustion device 15, and the water quality can be applied as the water for cooling the cation electrodeposition membrane in the step before the surface treatment or the cation electrodeposition dip washing water. Table 1 shows the water quality change when the waste water E is separated into the concentrated liquid and the treated water by the calandria 6, and the treated water is purified by the submerged combustion device 15.

この様に液中燃焼装置15を使用したときには浄化水中に
おける残留油分が少なくなり、CODも改善されることが
分かった。
Thus, it was found that when the submerged combustion device 15 was used, the residual oil content in the purified water was reduced and the COD was also improved.

第3図は本発明方法を利用した機械加工々程における洗
浄水再利用装置の概略説明図であり、第5図に示す例と
構成上相違する点は次の通りである。即ち処理水用のタ
ンク9の下流側に配管8を介して液中燃焼装置15を設け
ると共に、循環ライン4からバルブ31を介して分岐管27
を分岐し、該分岐管27を配管8に連接した点に特徴があ
る。そして希釈廃水の一部を処理水と混合して上記液中
燃焼装置15へ導入し、この混合水を加熱すると共に該混
合水中の低沸点油分を除去し、ノズル22へ供給される洗
浄水溶液の品質を改善する。こうすることによって希釈
廃水の一部は常に浄化されるので、その交換頻度を低減
でき効率的な廃水再利用がはかれる。
FIG. 3 is a schematic explanatory view of a cleaning water reuse device in a machining process using the method of the present invention, and the points different in configuration from the example shown in FIG. 5 are as follows. That is, the submerged combustion device 15 is provided on the downstream side of the treated water tank 9 via the pipe 8, and the branch pipe 27 from the circulation line 4 via the valve 31.
Is characterized in that the branch pipe 27 is connected to the pipe 8. Then, a part of the diluted waste water is mixed with treated water and introduced into the submerged combustion device 15, and the low boiling point oil component in the mixed water is removed while heating the mixed water, and the cleaning aqueous solution supplied to the nozzle 22 is supplied. Improve quality. By doing so, a part of the diluted wastewater is always purified, so that the frequency of replacement can be reduced and the wastewater can be reused efficiently.

尚第3図に示す例では排出ライン12に他の液中燃焼装置
21を設け、濃縮された液を加熱して液中の成分が凍結又
は結晶化するのを防止し、さらに液中の液体成分を蒸発
させて焼却し易くすることも可能である。
In the example shown in FIG. 3, another in-liquid combustion device is used in the discharge line 12.
It is also possible to provide 21 to prevent the components in the liquid from freezing or crystallizing by heating the concentrated liquid, and further to evaporate the liquid components in the liquid to facilitate incineration.

[発明の効果] 本発明によって蒸発缶等の蒸留装置を経て凝縮された処
理水及び洗浄水の品質を効率的に改善し、廃液の浄化再
利用を低コストで行なうことができるようになった。
[Advantages of the Invention] According to the present invention, the quality of treated water and washing water condensed through a distillation apparatus such as an evaporator can be efficiently improved, and purification and reuse of waste liquid can be performed at low cost. .

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

第1図及び第3図は本発明方法に利用する装置の例を示
す概略説明図、第2図は液中燃焼装置の例を示す断面説
明図、第4,5図は従来方法に用いられる装置の例を示す
概略説明図である。 2a……供給管、2b……排出管 13……蒸気送給ライン
1 and 3 are schematic explanatory views showing an example of an apparatus used in the method of the present invention, FIG. 2 is a sectional explanatory view showing an example of an in-liquid combustion apparatus, and FIGS. 4 and 5 are used in a conventional method. It is a schematic explanatory drawing which shows the example of an apparatus. 2a …… Supply pipe, 2b …… Exhaust pipe 13 …… Steam supply line

フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C02F 9/00 504 B 7446−4D Continuation of front page (51) Int.Cl. 6 Identification code Office reference number FI technical display location C02F 9/00 504 B 7446-4D

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】油性成分含有工場廃水を蒸留処理して蒸気
と濃縮水に分離し、得られた蒸気を凝縮した後、液中燃
焼装置で処理して低沸点油分を分離し、得られた浄化水
を工場処理用水として再利用することを特徴とする工場
処理水の循環利用方法。
1. An industrial wastewater containing an oily component is subjected to a distillation treatment to be separated into steam and concentrated water, and the obtained steam is condensed and then treated in a submerged combustion device to separate a low boiling point oil content. A method for recycling factory treated water, characterized in that purified water is reused as factory treated water.
JP62092172A 1987-04-15 1987-04-15 Circulation use method of factory treated water Expired - Lifetime JPH0757357B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP62092172A JPH0757357B2 (en) 1987-04-15 1987-04-15 Circulation use method of factory treated water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP62092172A JPH0757357B2 (en) 1987-04-15 1987-04-15 Circulation use method of factory treated water

Publications (2)

Publication Number Publication Date
JPS63258698A JPS63258698A (en) 1988-10-26
JPH0757357B2 true JPH0757357B2 (en) 1995-06-21

Family

ID=14047012

Family Applications (1)

Application Number Title Priority Date Filing Date
JP62092172A Expired - Lifetime JPH0757357B2 (en) 1987-04-15 1987-04-15 Circulation use method of factory treated water

Country Status (1)

Country Link
JP (1) JPH0757357B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100246080B1 (en) * 1998-01-22 2000-03-15 설옥덕 A direct-heating waste water condensing system
KR20030084134A (en) * 2002-04-25 2003-11-01 권익 Evaporation concentrator of direct heating type
CN110526480B (en) * 2019-10-11 2020-10-02 清华大学 Combined evaporation device and evaporation control method

Also Published As

Publication number Publication date
JPS63258698A (en) 1988-10-26

Similar Documents

Publication Publication Date Title
US5342482A (en) Leachate evaporation system
US20150014142A1 (en) Method for processing waste water using zero process water discharge
CA2903412C (en) Co2 recovery system and co2 recovery method
KR102169490B1 (en) Non-discharge wastewater treatment using multi-step vacuum decompression evaporation concentration of high concentration wastewater
CN214004100U (en) Contain salt effluent treatment plant
JPH04225875A (en) Method and device for washing object with water washing fluid containing washing agent
KR102056088B1 (en) Apparatus for Processing waste water concentration of wastewater reduction type with low temperature diffusion
US6893556B2 (en) Apparatus for pretreatment prior to painting
CN109534587B (en) Comprehensive treatment system for high-salt degradation-resistant wastewater in printing and dyeing industry
JPH0757357B2 (en) Circulation use method of factory treated water
SE420618B (en) WAY TO REMOVE FUEL OILS
CN1161311C (en) Separation of glycols
JP2005232093A (en) Method for recovering high-purity ethylene glycol
KR102266988B1 (en) Hybrid waste-water disposal system
CA2278163A1 (en) System and method of waste water reduction and product recovery
DE102005049923B4 (en) Method and arrangement for the purification of industrially contaminated waste water / process water by means of a distillation plant
US4834868A (en) Neutralizing oxidation product components in continuous rerefining of used oil stocks
NO142737B (en) PROCEDURE FOR REMOVING SMELLING ORGANIC MATERIALS FROM TABLE OIL.
JPH07112166A (en) Cleaning / drying equipment using solvent
JP2003053328A (en) Waste water treating equipment
JPH09314128A (en) Method for treating regeneration waste liquid of cation exchange resin adsorbed of organic amine
RU2831331C1 (en) Method of recovering physical and chemical properties of glycol solution
JP2003211149A (en) Plating washing waste liquid treatment apparatus and treatment method
CN211311347U (en) System for retrieve DMF and dimethylamine in follow DMF waste liquid
KR20010101436A (en) Process and apparatus for cleaning of waste water