JPH01258791A - Waste water treating device for electrodeposition painting line - Google Patents
Waste water treating device for electrodeposition painting lineInfo
- Publication number
- JPH01258791A JPH01258791A JP8316188A JP8316188A JPH01258791A JP H01258791 A JPH01258791 A JP H01258791A JP 8316188 A JP8316188 A JP 8316188A JP 8316188 A JP8316188 A JP 8316188A JP H01258791 A JPH01258791 A JP H01258791A
- Authority
- JP
- Japan
- Prior art keywords
- tank
- waste water
- rinsing
- rinsing tank
- final
- 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.)
- Pending
Links
- 239000002351 wastewater Substances 0.000 title claims abstract description 19
- 238000004070 electrodeposition Methods 0.000 title claims abstract description 13
- 238000010422 painting Methods 0.000 title abstract 2
- 239000012528 membrane Substances 0.000 claims abstract description 20
- 238000001223 reverse osmosis Methods 0.000 claims abstract description 11
- 239000007788 liquid Substances 0.000 claims abstract description 7
- 238000005406 washing Methods 0.000 claims description 21
- 238000000576 coating method Methods 0.000 claims description 11
- 239000011248 coating agent Substances 0.000 claims description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 11
- 239000000706 filtrate Substances 0.000 abstract description 10
- 239000007787 solid Substances 0.000 abstract description 7
- 229920002647 polyamide Polymers 0.000 abstract description 3
- 239000004952 Polyamide Substances 0.000 abstract 1
- 239000003973 paint Substances 0.000 description 7
- 238000000108 ultra-filtration Methods 0.000 description 6
- 238000001914 filtration Methods 0.000 description 4
- 238000000034 method Methods 0.000 description 4
- 238000004065 wastewater treatment Methods 0.000 description 3
- 125000002091 cationic group Chemical group 0.000 description 2
- SMMIDVLUFMPWFN-UHFFFAOYSA-N 4-nitro-n-[(4-phenyldiazenylphenyl)diazenyl]aniline Chemical compound C1=CC([N+](=O)[O-])=CC=C1NN=NC1=CC=C(N=NC=2C=CC=CC=2)C=C1 SMMIDVLUFMPWFN-UHFFFAOYSA-N 0.000 description 1
- 239000004372 Polyvinyl alcohol Substances 0.000 description 1
- 229920002301 cellulose acetate Polymers 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 239000003792 electrolyte Substances 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 238000011010 flushing procedure Methods 0.000 description 1
- 230000004907 flux Effects 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 125000003367 polycyclic group Chemical group 0.000 description 1
- 229920002451 polyvinyl alcohol Polymers 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 239000008237 rinsing water Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
Description
【発明の詳細な説明】
「産業上の利用分野」
本発明【よ、電着塗装ラインの最終水洗槽からの排水を
処F!!づる装置である。[Detailed Description of the Invention] "Industrial Application Field" The present invention is designed to treat wastewater from the final washing tank of an electrodeposition coating line! ! It is a device that pulls.
「従来の技術」
電着塗装は、自動車ボディー、部品、家N製品の塗装方
法として広く使用されている。特に、自動車車体の下塗
り塗装は、塗膜中に金属イオンを残さないカチオン型電
肴塗装が実施されている。"Prior Art" Electrodeposition coating is widely used as a coating method for automobile bodies, parts, and household products. In particular, cationic electrolyte coating, which does not leave metal ions in the coating film, is used for undercoating automobile bodies.
この装置では、電着塗料の塗布割合の向上と洗浄水の公
害対策の点から、電着槽から持も出された塗料を限界ろ
過装置で分離している。濃縮液は再び電着槽に戻し、透
過液を第2水洗槽に供給している。しかしながら、最終
の純水水洗工程では、第2水洗槽からの塗料の持ら出し
と、水洗シVワーの洗浄水によって固形分0.1%程度
の排水が常にA−バー70−している。In this equipment, the paint removed from the electrodeposition tank is separated using an ultrafiltration device in order to improve the coating rate of the electrodeposition paint and prevent pollution of the washing water. The concentrated liquid is returned to the electrodeposition tank, and the permeated liquid is supplied to the second washing tank. However, in the final pure water rinsing process, the paint is taken out from the second rinsing tank and the rinsing water from the rinsing tank always produces waste water with a solid content of about 0.1%. .
[発明が解決しようと°する課題」
この排水は、BODで4000m’J/eと高濃度でお
る為に、このままでは放流出来ず、排水処理をして放流
している。この排水処理方法として、凝集沈澱後に好気
性生物処理、ドラムドライヤによる蒸発乾燥処理が実施
されている。これらの方法は、大規模で高価な設備と予
信のエネルギーを消費ηる欠点を持っている。[Problems to be Solved by the Invention] This wastewater has a high concentration of BOD of 4000 m'J/e, so it cannot be discharged as it is, so it is treated after being discharged. As a method for treating wastewater, aerobic biological treatment and evaporation drying treatment using a drum dryer are carried out after coagulation and sedimentation. These methods have the disadvantage of large and expensive equipment and considerable energy consumption.
[課題を解決するための手段]
本発明は、安価な設備費とより少ないエネルギーで、最
終水洗槽からの排水を回収する装置に関するしのである
。[Means for Solving the Problems] The present invention relates to an apparatus for recovering wastewater from a final flushing tank with low equipment costs and less energy.
この最終水洗槽からの排水中には、固形分O905%〜
0.2%、BODで2000〜4000mg、/lの4
1機物が含イ1されている1ノれども、電着槽からの塗
料に比較りれぽ、低濃度であるため番こ、限界ろ過膜で
はBODの除去率が低い事が予想されて最終水洗槽から
の排水処理には適用されなかった。逆浸透膜に関しては
、フラックスの急激な低下が予想されて、膜による排水
処理には、適さないと考えられていた。事実、固形分2
0.7%のカヂオン型電看塗利を日東電工(轡製限界ろ
過モジュールNTU2120で分離した場合、固形分0
.6%程度の透過水しか得られなかった。The solid content in the wastewater from this final washing tank is O905%~
0.2%, BOD 2000-4000mg/l 4
However, since the concentration of BOD is low compared to the paint from the electrodeposition tank, it is expected that the removal rate of BOD will be low with the ultrafiltration membrane. It was not applied to wastewater treatment from the final washing tank. As for reverse osmosis membranes, it was thought that they would be unsuitable for wastewater treatment because a rapid drop in flux was expected. In fact, solids content 2
When 0.7% cadion type Dennuri is separated using the ultrafiltration module NTU2120 manufactured by Nitto Denko, the solid content is 0.
.. Only about 6% of permeated water was obtained.
「作 用」
固形分0.05%〜0.2%の最終水洗槽(10)から
の排水を調整槽(20)に導き、循環用高圧ンドンプ(
21)て昇圧し、逆浸透膜モジュール(22)で分21
Iする。濃縮液は、第2水洗槽(12)に供給し、ろ過
液を貯留槽(23)に導く。!!7留槽のろ過液は、水
洗シVワー(24)の水として使用する。貯留槽からオ
ーバーフローした排水はそのまま放流する。"Function" Drainage from the final washing tank (10) with a solid content of 0.05% to 0.2% is led to the adjustment tank (20), and the high-pressure pump for circulation (
21) and increase the pressure for 21 minutes using the reverse osmosis membrane module (22).
I do. The concentrated liquid is supplied to the second washing tank (12), and the filtrate is led to the storage tank (23). ! ! The filtrate from the 7-reservoir tank is used as water for the washing machine (24). The wastewater that overflows from the storage tank will be discharged as is.
逆浸透膜の種類として、酢酸セルロース膜、ポリアミド
系膜、ポリビニルアルコール系膜、複索環す(リマー系
膜いずれでもよいが、特にポリアミド系膜が優れている
。逆浸透膜モジュールとしては、スパイラルモジュール
、中空系モジュール、チューブラ−モジュール、プレー
1〜アンドフレームモジユール、プリーツ−七ジュール
いずれでもよいが、操作性と経済性の点からは、スパイ
ラルモジュールが優れている。Types of reverse osmosis membranes include cellulose acetate membranes, polyamide-based membranes, polyvinyl alcohol-based membranes, and polycyclic (rimer-based membranes), but polyamide-based membranes are particularly excellent.As reverse osmosis membrane modules, spiral Any module may be used, such as a hollow module, a tubular module, a play 1~and frame module, or a pleated 7 joule module, but the spiral module is superior in terms of operability and economy.
固形分0.05%〜0.2%の最終水洗槽(10)から
排水を調整槽(20)に導く際、排水中の有機蒸発成分
を取り除くために、送、I!llAより散気管を通して
、空気を注入しても、BODの低いろ過が(qられる。When introducing the wastewater from the final washing tank (10) with a solid content of 0.05% to 0.2% to the adjustment tank (20), a feed, I! Even if air is injected through the air diffuser from llA, filtration with a low BOD can be achieved (q).
調整槽からの排水を循環用高圧ポンプに導く前に、スト
レナーの代わりに、精密ろ過器、又は限界ろ過膜モジュ
ールを設置しても良い。Before introducing the waste water from the adjustment tank to the circulation high-pressure pump, a microfilter or an ultrafiltration membrane module may be installed instead of the strainer.
「実施例」
[1本ペイント(…製カチオン型電看塗料パワー1〜ツ
ブtJ−500を使用した電着塗装ラインの最終の補水
水洗(aからの排水を調整槽に導く。高圧ポンプにて昇
圧さU/、:後、日東電工■製スパイラル型逆浸透膜N
TR−7197で分離した。逆浸透膜[ジ1−ルの人口
圧力30に’!、/lri、ろ液の透過速度18.ON
、/Tl1−hで運転した時の結果を表−1に示す。"Example" [Final water replenishment washing of an electrodeposition coating line using 1 paint (cationic type electronic paint Power 1 to Tsubutu TJ-500 manufactured by... Boosted U/: After, Nitto Denko's spiral reverse osmosis membrane N
It was separated using TR-7197. Reverse osmosis membrane [Gile's population pressure 30'! , /lri, permeation rate of filtrate18. ON
, /Tl1-h are shown in Table 1.
この工程にて、塗装したリーンプルを焼付乾燥後、上塗
り塗装をしても塗膜の剥離を生じなかった。In this process, after the painted Lean Pull was baked and dried, no peeling of the paint film occurred even when a top coat was applied.
同じ調整槽からの排水をポンプにて日東電工<ti製ス
パイラル型限界ろ過膜モジュールNTU−2120で分
離した。限界ろ過膜モジュールの入口圧力4 K3 、
/ crA、ろ液の透過速度76.34!/ボ・hで運
転した時の結果を表−1に示す。The waste water from the same adjustment tank was separated using a spiral type ultrafiltration membrane module NTU-2120 manufactured by Nitto Denko <ti> using a pump. Inlet pressure of ultrafiltration membrane module 4 K3,
/ crA, filtrate permeation rate 76.34! Table 1 shows the results when operating at /bo/h.
「発明の効果」
」l記のように、最終水洗槽からの排水を逆浸透膜によ
って分離する事によってろ過液のBODを’l0m3.
7f!に下げる事が出来るので、そのまま放WLJる事
が出来る。このろ過液の一部は、最終水洗槽の洗浄水と
して使用する事が出来るので、最終水洗槽で使用する純
水の使用量を低下さける事が出来る。この様にして、本
装置は電着塗装費の低減に貢献出来るしのである。``Effects of the Invention'' As described in section 1, by separating the waste water from the final washing tank using a reverse osmosis membrane, the BOD of the filtrate can be reduced to 10m3.
7f! Since it can be lowered to , it is possible to release WLJ as it is. A part of this filtrate can be used as washing water for the final washing tank, so it is possible to avoid reducing the amount of pure water used in the final washing tank. In this way, this device can contribute to reducing electrodeposition coating costs.
第1図は、本発明の排水処理装置を従来の電着塗装ライ
ンに設置した際の一実施例の70を示す。
11は第1水洗槽、12は第2水洗槽、14は電着塗装
槽、8は限界ろ過装置、9は限界ろ過のろ過液の貯留槽
、10は最終水洗槽、20は排水の調整槽、2]は循環
用高圧ポンプ、22は逆浸透ろ過装置、23はろ過液貯
留槽、24は再刊用水の水洗シャワー、25は精密ろ過
器、26は放流水、27は圧力調整弁、2Bは流量計、
29は最終水洗槽からの排水、30G、を純水水洗。FIG. 1 shows an embodiment 70 in which the wastewater treatment apparatus of the present invention is installed in a conventional electrodeposition coating line. 11 is a first washing tank, 12 is a second washing tank, 14 is an electrodeposition coating tank, 8 is a limit filtration device, 9 is a storage tank for the filtrate of the limit filtration, 10 is a final washing tank, and 20 is a drainage adjustment tank. , 2] is a high-pressure pump for circulation, 22 is a reverse osmosis filtration device, 23 is a filtrate storage tank, 24 is a flush shower with water for reprinting, 25 is a precision filter, 26 is discharge water, 27 is a pressure regulating valve, 2B is Flowmeter,
29 is the waste water from the final washing tank, 30G, which is washed with pure water.
Claims (1)
透膜によつて分離し、濃縮液を第一水洗槽(11)、第
二水洗槽(12)のいずれかに供給し、ろ過液を最終水
洗槽の水洗として供給する装置。The wastewater from the final washing tank (10) of the electrodeposition coating line is separated by a reverse osmosis membrane, and the concentrated liquid is supplied to either the first washing tank (11) or the second washing tank (12), where it is filtered. A device that supplies liquid as a final flush to the final flush tank.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP8316188A JPH01258791A (en) | 1988-04-06 | 1988-04-06 | Waste water treating device for electrodeposition painting line |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP8316188A JPH01258791A (en) | 1988-04-06 | 1988-04-06 | Waste water treating device for electrodeposition painting line |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH01258791A true JPH01258791A (en) | 1989-10-16 |
Family
ID=13794531
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP8316188A Pending JPH01258791A (en) | 1988-04-06 | 1988-04-06 | Waste water treating device for electrodeposition painting line |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH01258791A (en) |
-
1988
- 1988-04-06 JP JP8316188A patent/JPH01258791A/en active Pending
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