JPS5935675B2 - Sludge separation and collection method using water film eddy current coating booth - Google Patents
Sludge separation and collection method using water film eddy current coating boothInfo
- Publication number
- JPS5935675B2 JPS5935675B2 JP8885877A JP8885877A JPS5935675B2 JP S5935675 B2 JPS5935675 B2 JP S5935675B2 JP 8885877 A JP8885877 A JP 8885877A JP 8885877 A JP8885877 A JP 8885877A JP S5935675 B2 JPS5935675 B2 JP S5935675B2
- Authority
- JP
- Japan
- Prior art keywords
- water
- sludge
- booth
- eddy current
- water film
- 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
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims description 99
- 239000010802 sludge Substances 0.000 title claims description 54
- 239000011248 coating agent Substances 0.000 title claims description 11
- 238000000576 coating method Methods 0.000 title claims description 11
- 238000000034 method Methods 0.000 title claims description 5
- 238000000926 separation method Methods 0.000 title description 4
- 239000003595 mist Substances 0.000 claims description 10
- 230000003311 flocculating effect Effects 0.000 claims description 5
- 150000004679 hydroxides Chemical class 0.000 claims description 3
- 238000010422 painting Methods 0.000 claims description 2
- 230000004888 barrier function Effects 0.000 claims 1
- 238000004140 cleaning Methods 0.000 description 19
- 239000003973 paint Substances 0.000 description 11
- 239000003795 chemical substances by application Substances 0.000 description 8
- 239000007787 solid Substances 0.000 description 6
- -1 alkali metal carboxylate Chemical class 0.000 description 4
- 229910052783 alkali metal Inorganic materials 0.000 description 3
- 230000018044 dehydration Effects 0.000 description 3
- 238000006297 dehydration reaction Methods 0.000 description 3
- 239000002736 nonionic surfactant Substances 0.000 description 3
- 239000007921 spray Substances 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 229920000877 Melamine resin Polymers 0.000 description 2
- 150000001340 alkali metals Chemical class 0.000 description 2
- 229920000180 alkyd Polymers 0.000 description 2
- 239000002518 antifoaming agent Substances 0.000 description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 2
- 239000000920 calcium hydroxide Substances 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000008394 flocculating agent Substances 0.000 description 2
- 238000005187 foaming Methods 0.000 description 2
- 238000005192 partition Methods 0.000 description 2
- 230000000737 periodic effect Effects 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 229920001296 polysiloxane Polymers 0.000 description 2
- 239000004925 Acrylic resin Substances 0.000 description 1
- 229920000178 Acrylic resin Polymers 0.000 description 1
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- 235000013162 Cocos nucifera Nutrition 0.000 description 1
- 244000060011 Cocos nucifera Species 0.000 description 1
- 239000005909 Kieselgur Substances 0.000 description 1
- 239000004640 Melamine resin Substances 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 150000001298 alcohols Chemical class 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 description 1
- RQPZNWPYLFFXCP-UHFFFAOYSA-L barium dihydroxide Chemical compound [OH-].[OH-].[Ba+2] RQPZNWPYLFFXCP-UHFFFAOYSA-L 0.000 description 1
- 229910001863 barium hydroxide Inorganic materials 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 239000000701 coagulant Substances 0.000 description 1
- 230000001112 coagulating effect Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 239000011790 ferrous sulphate Substances 0.000 description 1
- 235000003891 ferrous sulphate Nutrition 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 238000005188 flotation Methods 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 description 1
- 229910000359 iron(II) sulfate Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- JDSHMPZPIAZGSV-UHFFFAOYSA-N melamine Chemical compound NC1=NC(N)=NC(N)=N1 JDSHMPZPIAZGSV-UHFFFAOYSA-N 0.000 description 1
- 239000002480 mineral oil Substances 0.000 description 1
- 235000010446 mineral oil Nutrition 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 229920000620 organic polymer Polymers 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
Landscapes
- Treatment Of Sludge (AREA)
- Coating Apparatus (AREA)
- Separation Of Particles Using Liquids (AREA)
- Physical Water Treatments (AREA)
Description
【発明の詳細な説明】
本発明は、水膜渦流式塗装ブース(水の循環と排気洗浄
とを排風機によって行い、ポンプを使用しない型の塗装
ブース)のスラッジ分離捕集方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a sludge separation and collection method for a water film eddy current coating booth (a type of coating booth in which water circulation and exhaust cleaning are performed by an exhaust fan and no pump is used). .
従来、水膜渦流式塗装ブースのオーバースプレーミスト
を処理する場合には、循環水にアルカリ金属を含む水処
理剤を加えて水槽中に沈殿させて除去していた。Conventionally, when treating overspray mist from a water film eddy current painting booth, a water treatment agent containing an alkali metal was added to the circulating water and removed by precipitation in a water tank.
しかし、沈殿したスラッジは粘着性があり、除去するに
はかなりの労力を要していた。However, the settled sludge was sticky and required considerable effort to remove.
また、無公害、省資源塗料として多用されるようになっ
た水系塗料が使用された場合には、水系塗料用樹脂がア
ルカリ金属のカルボン酸塩となって溶解するために、粘
度上昇、起泡、排気洗浄部へのスラッジの蓄積などの問
題のため、循環水を有効に利用できない欠点があった。In addition, when water-based paints, which are now widely used as non-polluting and resource-saving paints, are used, the resin for water-based paints becomes an alkali metal carboxylate and dissolves, resulting in increased viscosity and foaming. However, due to problems such as the accumulation of sludge in the exhaust cleaning section, there was a drawback that circulating water could not be used effectively.
本発明は、以上の現状に鑑み、上記欠点のないオーバー
スプレーミスト処理について種々研究の結果なされたも
のであって、水膜渦流式塗装ブースの循環水に、元素周
期表第na族元素の水酸化物および/または酸化物を主
成分とする凝集浮上剤を加えてオーバースプレーミスト
をスラッジとして循環水より分離させ、ついでその分離
したスラッジを導水路またはブース水槽に設けた阻流板
またはスラッジ吸込口により捕集することを特徴とする
水膜渦流式塗装ブースのスラッジ分離捕集方法である。In view of the above-mentioned current situation, the present invention has been made as a result of various studies on overspray mist treatment that does not have the above-mentioned drawbacks. The overspray mist is separated from the circulating water as sludge by adding an oxide and/or a flocculating agent mainly composed of oxides, and then the separated sludge is transferred to a baffle plate or sludge suction installed in the headrace or booth water tank. This is a method for separating and collecting sludge in a water film vortex coating booth, which is characterized by collecting the sludge through a spout.
本発明において使用される水処理剤は、循環水にそれを
加えた場合、スラッジが凝集し浮上するもの、すなわち
、凝集浮上剤であり、元素周期表第1Ia族元素の水酸
化物および/または酸化物を必須成分とし、これにスラ
ッジの粘着性、含水率、凝集性、浮上性、濾過性、装置
への付着性、循環水の起泡性などを改良する目的で、硫
酸アルミニウム、ポリ塩化アルミニウム、塩化カルシウ
ム、硫酸第一鉄のような凝結剤、ノニオン系界面活性剤
、ケイソウ土、活性白土、活性炭のような吸着剤、有機
高分子化合物のような凝集剤、シリコーンのような消泡
剤、そのほか高沸点アルコール類、鉱物油などを必要に
応じて添加したものである。The water treatment agent used in the present invention is one in which sludge coagulates and floats when added to circulating water, that is, a flocculating floatant, which contains hydroxides and/or hydroxides of Group Ia elements of the periodic table. Oxide is an essential component, and aluminum sulfate, polychloride, etc. are added to improve the sludge's stickiness, water content, cohesiveness, flotation, filtration, adhesion to equipment, foaming of circulating water, etc. Aluminum, calcium chloride, coagulants such as ferrous sulfate, nonionic surfactants, adsorbents such as diatomaceous earth, activated clay, activated carbon, flocculants such as organic polymer compounds, antifoaming agents such as silicone. In addition, high boiling point alcohols, mineral oil, etc. are added as necessary.
そして、循環水に元素周期表第11a族元素の水酸化物
および/または酸化物として0.01%以上溶解してP
Hを9以上に保った状態でスプレ一作業を行うとオーバ
ースプレーミストは、水処理剤と反応して凝結し、気泡
を含んだスラッジとなって浮上する。Then, 0.01% or more of P is dissolved in the circulating water as a hydroxide and/or oxide of Group 11a elements of the periodic table.
When a spray operation is performed with H maintained at 9 or more, the overspray mist reacts with the water treatment agent, condenses, and floats up as sludge containing air bubbles.
浮上したスラッジは付着性、粘着性が少なく、含水率も
きわめて低いので、スラッジの脱水は簡単な装置で容易
に行うことができ、スラッジを自動的に除去することも
容易である。The floated sludge has little adhesion and stickiness, and has an extremely low water content, so the sludge can be easily dehydrated using a simple device, and the sludge can be easily removed automatically.
導水路とは、排気洗浄部から排出される循環水をブース
水槽にもどすほめの水路であり、排気洗浄部の後部およ
び側部に設けられる。The headrace is a waterway that returns circulating water discharged from the exhaust cleaning section to the booth water tank, and is provided at the rear and side portions of the exhaust cleaning section.
阻流板とは、導水路の循環水面に、またはブース水槽の
水面に凝集浮上しているスラッジを捕集するために、導
水路またはブース水槽に取りつげられるものである。A baffle plate is attached to a water conduit or a booth water tank in order to collect sludge that has coagulated and floated on the circulating water surface of the water channel or the water surface of the booth water tank.
なお、阻流板のかわりにラッパ状をしたスラッジ吸込口
を取りつげてもよい。Note that a trumpet-shaped sludge suction port may be installed instead of the baffle plate.
本発明においては、水処理剤として従来の沈殿剤にかえ
て凝集浮上剤を使用することにより、オーバースプレー
ミストば、スラッジとして循環水より分離され、そして
、その分離されたスラッジは、導水路またはブース水槽
に設けられた阻流板またはスラッジ吸込口により捕集さ
れるので、かつ、水槽壁にスラッジが付着することが少
なく、循環水は常に清浄である。In the present invention, by using a flocculant instead of a conventional precipitating agent as a water treatment agent, overspray mist is separated from circulating water as sludge, and the separated sludge can be used in a water conduit or Since the sludge is collected by the baffle plate or sludge suction port provided in the booth tank, there is little sludge adhering to the tank wall, and the circulating water is always clean.
導水路を設けたことにより、循環水がそこを通過する間
には、循環水中のスラッジ、が浮上するので、その分離
が完全になり、凝集浮上剤の作用によって、スラッジの
粘着性低下が進むので、その含水率が下がる。By providing a water conduit, the sludge in the circulating water floats to the surface while the circulating water passes through it, resulting in complete separation and the action of the coagulating floatation agent, which further reduces the stickiness of the sludge. Therefore, its moisture content decreases.
か(して、粘着性と含水率とが少なく、かつ、高濃度と
なったスラッジは、阻流板またはスラッジ吸込口によっ
て、1カ所に集めることができるので、分離槽、濃縮槽
を要することもなく、きわめて容易に除去することがで
きる。(As a result, sludge with low stickiness and water content and high concentration can be collected in one place by a baffle plate or sludge suction port, so a separation tank and a concentration tank are not required. It can be removed very easily.
本発明の方法によって、水面に浮上したスラッジを短時
間のうちに容易に捕集し回収することができるので、回
収したスラッジにはゴミなどの異物の混入が少なく、こ
れを高分子化合物として再利用する場合にも有利である
。By the method of the present invention, sludge floating on the water surface can be easily collected and recovered in a short time, so the collected sludge contains less foreign matter such as dust and can be recycled as a polymer compound. It is also advantageous when used.
つぎに、図面(第1図)によって、水膜渦流式塗装ブー
スについての従来方法を説明する。Next, a conventional method for a water film vortex type coating booth will be explained with reference to a drawing (FIG. 1).
1はブース水槽、2は洗浄室、3は渦巻板、4は鋸刃状
板である。1 is a booth water tank, 2 is a cleaning chamber, 3 is a spiral plate, and 4 is a sawtooth plate.
被塗物にスプレーした場合のオーバースプレーミスしは
、洗浄室2の上部に設げられている排風機6の作用によ
る空気流のために、ブース水槽1の水の表面がはぎとら
れて、水が渦巻板3にそってのぼり、エリミネータ5に
あたって飛散する霧の中に包含される。Mistakes in overspray when spraying onto the object to be coated can occur because the surface of the water in the booth water tank 1 is stripped off due to the air flow produced by the exhaust fan 6 installed at the top of the cleaning chamber 2, causing the water to overspray. The mist climbs along the swirl plate 3 and hits the eliminator 5, and is included in the scattered mist.
しかして、霧がブース水槽1に落下するとき、オーバー
スプレーミストは、ブース水槽1の水中に含まれている
アルカリ金属を含む水処理剤によって水中にスラッジと
なって沈殿する。Therefore, when the mist falls into the booth water tank 1, the overspray mist is precipitated as sludge in the water by the water treatment agent containing the alkali metal contained in the water in the booth water tank 1.
そのスラッジは、逐次、戻り水路7に集積する。The sludge gradually accumulates in the return waterway 7.
なお、8は洗浄室前板、9は洗浄室後板である。Note that 8 is a front plate of the cleaning chamber, and 9 is a rear plate of the cleaning chamber.
つぎに、図示(第2図〜第5図)実施例について本発明
を説明する。The invention will now be described with reference to the illustrated embodiments (FIGS. 2 to 5).
’Ilaは、後部導水路であり、洗浄室後板の下端を適
宜に切りとるか、穴をあけるかして(9aがその洗浄室
後板の切取り部を示す)ブース水槽1の循環水をこの中
に導く水路である。'Ila is the rear water conduit, and the circulating water of the booth water tank 1 can be routed through this by cutting off the lower end of the rear plate of the cleaning chamber or making a hole (9a shows the cutout part of the rear plate of the cleaning chamber). It is a waterway that leads inside.
11bは、側部導水路であり、後部導水路11aと連続
している。11b is a side water conduit, which is continuous with the rear water conduit 11a.
したがって、循環水はブース水槽1から後部導水路11
a、側部導水路11bを通ってブース水槽1にもどるこ
とになる。Therefore, circulating water flows from the booth water tank 1 to the rear water conduit 11.
a, it returns to the booth water tank 1 through the side water conduit 11b.
この導水路の幅などは、循環水の水量、スプレーする塗
料の使用量などを考慮して適宜法めればよい。The width of this conduit can be determined as appropriate, taking into consideration the amount of circulating water, the amount of paint to be sprayed, and the like.
後部導水路11aに後部阻流板12aを設けるか、また
は側部導水路11bに側部阻流板12bを設けるか、あ
るいはブース水槽1に水槽内阻流板12cを設げるかす
る。Either a rear baffle plate 12a is provided in the rear water conduit 11a, a side baffle plate 12b is provided in the side water conduit 11b, or an in-tank baffle plate 12c is provided in the booth water tank 1.
これらの阻流板12a。12b、12cは、いずれか1
カ所のみに設ければ十分である(第2図、第3図におい
ては、これらの阻流板を、便宜上、同一図面上に記載し
たものである)。These baffle plates 12a. 12b and 12c are either 1
It is sufficient to provide the baffle plates only at a few locations (in FIGS. 2 and 3, these baffle plates are shown on the same drawing for convenience).
これらの阻流板を設けるかわりに、それと同様な位置に
ラッパ状をしたスラッジ吸込口13を設けることができ
る。Instead of providing these baffle plates, a trumpet-shaped sludge suction port 13 can be provided at a similar position.
これらの阻流板12a、12b、’f2c、スラッジ吸
込口13は、循環水の水面下約10cr/l程度、水面
上約5crrL程度あるようにすれば十分であり、それ
らの材質はとくに問わない。It is sufficient for these baffle plates 12a, 12b, 'f2c, and sludge suction port 13 to be approximately 10 cr/l below the water surface of the circulating water and approximately 5 crr/l above the water surface, and their materials are not particularly limited. .
スラッジ吸込口13は、第4図に示したように、進行し
てきた循環水(とくに凝集浮上しているスラッジを含ん
でいる上層部)が、吸込口ラッパ状部13aを通り、つ
いで、吸込口円筒部13bを通るようにしたものであり
、スラッジは、スラッジ吸込口13内に集積するのみで
、吸込口円筒部13bを通らないようにしたものである
。As shown in FIG. 4, the sludge suction port 13 is configured such that circulating water (especially the upper layer containing coagulated and floating sludge) passes through the suction port trumpet-shaped portion 13a, and then passes through the suction port. The sludge is configured so that it passes through the cylindrical portion 13b, and the sludge only accumulates in the sludge suction port 13 and does not pass through the suction port cylindrical portion 13b.
なお、本発明における水流は、洗浄室後板切取り部9a
を通って、後部導水路11aに出るので、戻り水路7は
不要となる。Note that the water flow in the present invention is directed to the cleaning chamber rear plate cutout 9a.
Since the water passes through the water and exits to the rear water conduit 11a, the return water channel 7 becomes unnecessary.
そのため、第2図に示すように、仕切り板14を設ける
。Therefore, as shown in FIG. 2, a partition plate 14 is provided.
つぎに、実施例によって本発明を説明する。Next, the present invention will be explained by examples.
実施例 1
第2図および第3図に示すような水膜渦流式塗装ブース
(ブース幅1.8m、循環水の水量10001)におい
て、側部導水路11bに、循環水の水面上5CIrLで
あって水面下10C7rLである鉄製の阻流板12bを
設げた。Example 1 In a water film eddy current coating booth (booth width 1.8 m, circulating water volume 10001) as shown in Figs. An iron baffle plate 12b was installed at a depth of 10C7rL below the water surface.
ついで循環水に、水酸化カルシウム2kg、プロノン2
04(日本油脂社製のオキシエチレンオキシプロピレン
ブロックポリマー系ノニオン界面活性剤)10kgから
なる凝集浮上剤を溶解し、PHを13,2とした。Next, add 2 kg of calcium hydroxide and 2 kg of pronone to the circulating water.
04 (oxyethylene oxypropylene block polymer nonionic surfactant manufactured by Nippon Oil & Fats Co., Ltd.) 10 kg of a flocculating floatant was dissolved and the pH was adjusted to 13.2.
排風機6を運転した場合の洗浄室2の減圧度は水柱75
7rlr/Lであった。When the exhaust fan 6 is operated, the degree of depressurization in the cleaning chamber 2 is 75 water columns.
It was 7rlr/L.
このように、水膜渦流式塗装ブースを運転しながら、や
し油変性アルキドメラミン樹脂系の白色塗料10kgを
スプレーガンによって、毎分1001の吐出量でスプレ
ーしたところ、側部導水路11bに浮上したスラッジは
、粘着性が少なく取扱いやすい状態を示した。In this way, while operating the water film eddy current coating booth, when 10 kg of white paint made from coconut oil-modified alkyd melamine resin was sprayed with a spray gun at a rate of 100 l/min, it floated to the side water conduit 11b. The sludge was less sticky and easier to handle.
そして、阻流板12bによって捕集されたスラッジは軽
く、その固形分は、スプレーした白色塗料の固形分の9
6%であり、加圧脱水後の含水率は42%であった。The sludge collected by the baffle plate 12b is light, and its solid content is 9% of the solid content of the sprayed white paint.
6%, and the water content after pressure dehydration was 42%.
また、ブース水槽1、洗浄室2の汚れも少なかった。Also, there was less dirt in the booth water tank 1 and the cleaning room 2.
実施例 2
実施例1における阻流板12bの代りに、スラッジ吸込
口13を側部導水路11bに設けた。Example 2 Instead of the baffle plate 12b in Example 1, a sludge suction port 13 was provided in the side water conduit 11b.
ついで、循環水に、実施例1と同様の凝集浮上剤を溶解
し、PHを13.2とした。Next, the same flocculating floatant as in Example 1 was dissolved in the circulating water, and the pH was adjusted to 13.2.
ついで、スラッジ吸込口13を吸引ポンプ(図示せず)
と減圧式のスラッジ脱水装置(図示せず)に接続し、こ
れらの装置と水膜渦流式塗装ブースとを運転しながら、
水溶性アクリル樹脂系の白色塗料10kgをスプレーガ
ンによって、毎分2001の吐出量でスプレーしたとこ
ろ、側部導水路11bに浮上したスラッジは、粘着性が
ほとんどなく、取扱いやすい状態を示した。Next, the sludge suction port 13 is connected to a suction pump (not shown).
and a vacuum-type sludge dewatering device (not shown), and while operating these devices and the water film eddy current coating booth,
When 10 kg of water-soluble acrylic resin-based white paint was sprayed with a spray gun at a discharge rate of 2,001 kg/min, the sludge floating in the side water conduit 11b had almost no stickiness and was easy to handle.
そして、スラッジ吸込口13によって捕集されたスラッ
ジは軽く、その固形分は、スプレーした白色塗料の固形
分の92%であり、加圧脱水後の含水率は36%であっ
た。The sludge collected by the sludge suction port 13 was light, its solid content was 92% of the solid content of the sprayed white paint, and its water content after pressurized dehydration was 36%.
ブース水槽1の水の透視度は20鑵以±であり、塗料成
分の水への溶解が少ないことを示している。The visibility of the water in the booth water tank 1 was 20 mm or higher, indicating that the dissolution of the paint components in the water was low.
また、ブース水槽1、洗浄室2の汚れも少なかった。Also, there was less dirt in the booth water tank 1 and the cleaning room 2.
実施例 3 実施例1と同様にして阻流板12bを設げた。Example 3 A baffle plate 12b was provided in the same manner as in Example 1.
ついで循環水に、水酸化カルシウム2に9、水酸化バリ
ウム20ky、ノニオン0−2(日本油脂社製のポリオ
キシエチレンモノオレエート系ノニオン界面活性剤)I
kg、シリコン消泡剤200グからなる凝集浮上剤を溶
解し、PHを とした。Next, in the circulating water, 2 to 9 calcium hydroxide, 20 ky of barium hydroxide, and 0 to 2 nonionic (polyoxyethylene monooleate type nonionic surfactant manufactured by NOF Corporation) I
kg, a flocculating floatation agent consisting of 200 g of silicone antifoaming agent was dissolved, and the pH was set to .
このように、水膜渦流式塗装ブースを運転しながら、水
溶性アルキッドメラミン白色塗料50kgを実施例1と
同様にしてスプレーしたところ、側部導水路11bに浮
上したスラッジは粘着性がほとんどなく、取扱いやすい
状態を示した。As described above, when 50 kg of water-soluble alkyd melamine white paint was sprayed in the same manner as in Example 1 while operating the water film eddy current coating booth, the sludge that floated to the side water conduit 11b had almost no stickiness. It was in an easy-to-handle condition.
そして、阻流板12bによって捕集されたスラッジは軽
く、その固形分は、スプレーした白色塗料の固形分の9
2%であり、加圧脱水後の含水率は45%であった。The sludge collected by the baffle plate 12b is light, and its solid content is 9% of the solid content of the sprayed white paint.
2%, and the water content after pressure dehydration was 45%.
また、ブース水槽1、洗浄室2の汚れも少なかった。Also, there was less dirt in the booth water tank 1 and the cleaning room 2.
第1図は従来の水膜渦流式塗装ブースを示す説明図、第
2図および第3図は本発明の実施の状態を示す説明図(
第2図は側面図、第3図は平面図)、第4図はスラッジ
吸込口を示す説明図(第4図は側面図、第5図は平面図
)である。
1・・・・・・ブース水槽、2・・・・・・洗浄室、3
・・・・・・渦巻板、4・・・・・・鋸刃状板、5・・
・・・・エリミネータ、6・・・・・・排風機、7・・
・・・・戻り水路、8・・・・・・洗浄室前板、9・・
・・・・洗浄室後板、9a・・・・・・洗浄室後板切取
り部、10・・・・・・ブース水槽側板、11a・・・
・・・後部導水路、11b〜・・・・・側部導水路、1
2a・・・・・・後部阻流板、12b・・・・・・側部
阻流板、12c・・・・・・水槽内阻流板、13・・・
・・・スラッジ吸込口、13a・・・・・・吸込口ラッ
パ状部、13b・・・・・・吸込口円筒部、14・・・
・・・仕切り板。Fig. 1 is an explanatory diagram showing a conventional water film vortex type coating booth, and Figs. 2 and 3 are explanatory diagrams showing the state of implementation of the present invention (
FIG. 2 is a side view, FIG. 3 is a plan view), and FIG. 4 is an explanatory view showing the sludge suction port (FIG. 4 is a side view, and FIG. 5 is a plan view). 1...Booth water tank, 2...Cleaning room, 3
・・・・・・Spiral plate, 4... Serrated plate, 5...
...Eliminator, 6...Exhaust fan, 7...
...Return waterway, 8...Cleaning chamber front plate, 9...
...Cleaning chamber rear plate, 9a...Cleaning chamber rear plate cutout, 10...Booth tank side plate, 11a...
... Rear headrace, 11b - ... Side headrace, 1
2a...Rear baffle plate, 12b...Side baffle plate, 12c...Aquarium baffle plate, 13...
...Sludge suction port, 13a...Suction port trumpet-shaped portion, 13b...Suction port cylindrical portion, 14...
...Partition board.
Claims (1)
Ia族元素の水酸化物および/または酸化物を主成分と
する凝集浮上剤を加えてオーバースプレーミストをスラ
ッジとして循環水より分離させ、ついでその分離したス
ラッジを導水路またはブース水槽に設けた阻流板または
スラッジ吸込口により捕集することを特徴とする水膜渦
流式塗装ブースのスラッジ分離捕集方法。1 In the circulating water of the water film eddy current painting booth,
The overspray mist is separated from the circulating water as sludge by adding a flocculating floatant mainly composed of hydroxides and/or oxides of Group Ia elements, and then the separated sludge is passed through a barrier installed in the water conduit or booth water tank. A method for separating and collecting sludge in a water film eddy current coating booth, characterized in that sludge is collected by a flow plate or a sludge suction port.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP8885877A JPS5935675B2 (en) | 1977-07-26 | 1977-07-26 | Sludge separation and collection method using water film eddy current coating booth |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP8885877A JPS5935675B2 (en) | 1977-07-26 | 1977-07-26 | Sludge separation and collection method using water film eddy current coating booth |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5424271A JPS5424271A (en) | 1979-02-23 |
| JPS5935675B2 true JPS5935675B2 (en) | 1984-08-30 |
Family
ID=13954678
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP8885877A Expired JPS5935675B2 (en) | 1977-07-26 | 1977-07-26 | Sludge separation and collection method using water film eddy current coating booth |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5935675B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4590481B2 (en) * | 2008-04-11 | 2010-12-01 | マックテクニカルシステムズ株式会社 | Floating separation purification method using air bubbles in wet paint booth circulating water |
-
1977
- 1977-07-26 JP JP8885877A patent/JPS5935675B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5424271A (en) | 1979-02-23 |
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