JP3864447B2 - Wastewater treatment method and wastewater treatment equipment for alkaline waste liquid - Google Patents

Wastewater treatment method and wastewater treatment equipment for alkaline waste liquid Download PDF

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Publication number
JP3864447B2
JP3864447B2 JP7270596A JP7270596A JP3864447B2 JP 3864447 B2 JP3864447 B2 JP 3864447B2 JP 7270596 A JP7270596 A JP 7270596A JP 7270596 A JP7270596 A JP 7270596A JP 3864447 B2 JP3864447 B2 JP 3864447B2
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Japan
Prior art keywords
waste liquid
temperature
alkaline waste
wastewater treatment
tank
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Expired - Fee Related
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JP7270596A
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Japanese (ja)
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JPH09262589A (en
Inventor
正明 森光
昌郎 大住
一郎 西川
茂利 原
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Panasonic Corp
Panasonic Holdings Corp
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Panasonic Corp
Matsushita Electric Industrial Co Ltd
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  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は例えばプリント配線板の製造過程で発生するエッチングレジストのような樹脂成分を含有したアルカリ廃液の廃水処理方法とその廃水処理装置に関するものである。
【0002】
【従来の技術】
近年、地球環境の保護としての取組みが強化される中で、各種製造において発生する廃液の処理においても様々な工夫がなされ、また種々の規制が制定されてきている。
【0003】
プリント配線板の製造過程においても種々の廃液が発生するが、その中でもエッチングレジストとして使用する感光性フィルム(通称ドライフィルム)や印刷インキをアルカリ溶液で除去したときに生じる樹脂系アルカリ廃液の処理が大きな問題となっていた。
【0004】
そこで従来は樹脂成分を含有したアルカリ廃液に酸性薬液を添加し、加温して凝集反応をさせ、上澄み液を除去した後、残留した樹脂系スラッジ含有廃液を分離装置で樹脂系スラッジと処理水とに分離するようにしていた。
【0005】
【発明が解決しようとする課題】
上記分離装置で分離された樹脂系スラッジは廃棄処理業者に委託処理することとなるのであるが、含水率が高いヘドロ状のため産業廃棄物量がきわめて多量となり、処理費用が多くかかるという問題があった。
【0006】
勿論、分離装置でさらにその含水率を低くすることが考えられるが、凝集反応した樹脂系スラッジは内部に水分を取込んだ状態となっているので、分離装置によっても水分を簡単には分離できず、その結果として上述のごとく産業処理業者に委託する産業廃棄物量がきわめて多くなってしまうのであった。
【0007】
そこで本発明は樹脂系スラッジ内の含水率を下げることによって産業処理業者に委託する産業廃棄物量を減少させることを目的とする。
【0008】
【課題を解決するための手段】
この目的を達成するために本発明は、樹脂成分を含有したアルカリ廃液に酸性薬液を添加し、第1の温度に加温して凝集反応させ、次に前記第1の温度より高温の第2の温度に加温して凝集反応をさせ、その後、分離装置で樹脂系スラッジと処理水に分離し、これによって所期の目的を達成するものである。
【0009】
【発明の実施の形態】
本発明の請求項1に記載の発明は、凝集反応を第1の温度と、それより高温の第2の温度で行わせることとしたものであり、加熱温度を低温から高温への段階的に行うことにより、凝集するスラッジが従来のように一度に大粒化することによって水分を大量に取込むことはなくなり、この結果として以後の分離装置で水分をきわめて分離しやすくなり、これにより産業処理業者に委託する産業廃棄物量がきわめて少なくなり、処理コストを低減化することができる。
【0010】
本発明の請求項2に記載の発明は、アルカリ廃液に酸性薬液を添加し、30〜50℃に加温し、凝集沈殿後の上澄み液を除去したのち残留した樹脂系スラッジ含有廃液を55〜70℃に加温することを特徴とする請求項1記載のアルカリ廃液の廃水処理方法としたものであり、第1の温度を30〜50℃として次への搬送性を高め、第2の温度を55〜70℃として分離性を高めている。
【0011】
本発明の請求項3に記載の発明は、第2の温度に加温した樹脂系スラッジ含有廃液を移送する際に、一旦降温することを特徴とする請求項1または2に記載のアルカリ廃液の廃水処理方法としたものであり、凝集反応物を搬送性に適した温度まで降温するものである。
【0012】
本発明の請求項4に記載の発明は、20〜40℃まで降温することを特徴とする請求項3記載のアルカリ廃液の廃水処理方法としたものであり、搬送性に優れた温度まで降温するという作用を有する。
【0013】
本発明の請求項5に記載の発明は、酸性領域で凝集反応を行うことを特徴とする請求項1記載のアルカリ廃液の廃水処理方法としたものであり、PHにより凝集沈殿物の分離性、流動性に差があり、酸性領域で生成した凝集沈殿物は廃水処理に適している。
【0014】
本発明の請求項6に記載の発明は、酸性領域のPH値を2〜4とすることを特徴とする請求項5記載のアルカリ廃液の廃水処理方法としたものであり、酸性領域のなかでもPH2〜4の範囲で生成した凝集沈殿物が特に廃水処理に優れている。
【0015】
本発明の請求項7に記載の発明は、攪拌器、第1の加熱器を備えた反応槽と、この反応槽へ薬液槽から薬液を滴下する定量ポンプと、前記反応槽の廃液を昇温槽へ移送するポンプと、前記昇温槽に設けた第2の加熱器と、前記昇温槽の廃液を分離装置へ移送するポンプとを備え、第2の加熱器による加熱温度を第1の加熱器による加熱温度よりも高温とすることにより請求項1の作用を奏するものとする。
【0016】
以下本発明の一実施の形態について図面を用いて説明する。
図1は本発明のアルカリ廃液の廃水処理方法を示す装置の概略構成図である。図1において1はエッチングレジストの樹脂成分を含むアルカリ廃液、2,2aは樹脂系スラッジ、3は貯水槽、4は反応槽、5は加温器、6は攪拌器、7a〜7eは移送ポンプ、8は定量ポンプ、9は昇温槽、10は分離装置、11a〜11fは移送管、12はバルブ、13は薬液槽、14は酸性薬剤、15は温度計、16はPH計測器、17a,17bは処理廃水である。
【0017】
プリント配線板の製造過程において、現像および剥離能力が劣化したアルカリ廃液1は、図1に示すように移送管11aを経由して廃水処理施設の貯水槽3に送られる。アルカリ廃液1中の比較的大きな樹脂系スラッジ2や異物は貯水槽3の底に堆積する。貯水槽3の上澄み部分のアルカリ廃液1aは移送管11bを介して移送ポンプ7aで反応槽4に送り、貯水槽3の底に堆積した樹脂系スラッジ2や異物は定期的にバルブ12を開き除去したのち産業廃棄物として産業処理業者へ委託処理する。
【0018】
反応槽4のアルカリ廃液1aを攪拌器6で攪拌するとともに加温器5で加温しながら薬液槽13の酸性薬剤14として60vol%の硫酸を定量ポンプ8で反応槽4に滴下する。反応槽4に備えたPH計測器16でPH値が3〜4の時点で酸性薬剤14の滴下を停止し、温度計15の計測値が30〜50℃の時点で加温を終了し、約10〜20分間経過したのち攪拌器6を停止する。その後反応槽4内で生成した凝集反応物は約10〜12時間静置することにより反応槽4の底に樹脂系スラッジ2aとして堆積する。反応槽4内の約70%にあたる上澄みの処理廃水17aは移送管11cを介して移送ポンプ7Bで原水槽(図示せず)に送り、PH調整等を行い一般廃水として放流する。
【0019】
残りの約30%にあたる樹脂系スラッジ2aを含有したアルカリ廃液1bは移送管11dを介して移送ポンプ7cで昇温槽9に送る。アルカリ廃液1bは30〜50℃での凝集反応物であるため含水率が高く分離性も良くないが流動性に富みポンプ搬送性は優れている。昇温槽9内のアルカリ廃液1bを攪拌器6で攪拌しながら加温器5で55〜70℃まで昇温し攪拌を停止する。このときの樹脂系スラッジ2aは含水率が低いアルカリ廃液1cとなる。その後、55〜70℃まで加温したアルカリ廃液1cを流動性および搬送性を向上させるため自然放置等により20〜40℃まで降温し、移送管11eを介して移送ポンプ7dで分離装置10に送る。20〜40℃の沈殿物は粘土状で搬送性に優れている。
【0020】
次に分離装置10の遠心分離のろ過器を用いて樹脂系スラッジ2bと処理水(ろ液)を分離し、処理廃水17bを移送管11fを介して移送ポンプ7eで原水槽へ送りPH調整等を行い、一般廃水として放流する。このとき残留した樹脂系スラッジ2bは含水率がきわめて低く、産業廃棄物の減量化を図ることができる。
【0021】
【発明の効果】
以上のように本発明は、凝集反応を第1の温度と、それより高温の第2の温度で行わせることとしたものであり、加熱温度を低温から高温への段階的に行うことにより、凝集するスラッジが従来のように一度に大粒化することによって水分を大量に取り込むことはなくなり、この結果として以後の分離装置で水分をきわめて分離しやすくなり、これにより産業処理業者に委託する産業廃棄物量がきわめて少なくなり、処理コストを低減化することができる。
【図面の簡単な説明】
【図1】本発明のアルカリ廃液の廃水処理装置の概略構成図
【符号の説明】
1 アルカリ廃液
2,2a,2b 樹脂系スラッジ
3 貯水槽
4 反応槽
5 加温器
6 攪拌器
7a〜7e 移送ポンプ
8 定量ポンプ
9 昇温槽
10 分離装置
11a〜11f 移送管
12 バルブ
13 薬液槽
14 酸性薬剤
15 温度計
16 PH計測器
17a,17b 処理廃水
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a wastewater treatment method for an alkaline waste liquid containing a resin component such as an etching resist generated in the manufacturing process of a printed wiring board, and a wastewater treatment apparatus therefor.
[0002]
[Prior art]
In recent years, as efforts to protect the global environment have been strengthened, various ideas have been made in the treatment of waste liquid generated in various productions, and various regulations have been established.
[0003]
Various waste liquids are also generated in the manufacturing process of printed wiring boards. Among them, resin-based alkaline waste liquids produced when photosensitive films (commonly called dry films) and printing inks used as etching resists are removed with alkaline solutions. It was a big problem.
[0004]
Therefore, conventionally, an acidic chemical solution is added to an alkaline waste liquid containing a resin component, heated to cause a coagulation reaction, and the supernatant liquid is removed. Then, the residual waste liquid containing resin sludge is treated with resin sludge and treated water using a separator. And was to be separated.
[0005]
[Problems to be solved by the invention]
The resin sludge separated by the separation device is entrusted to a waste disposal contractor. However, there is a problem that the amount of industrial waste becomes very large due to the sludge shape with a high water content, resulting in high processing costs. It was.
[0006]
Of course, it is conceivable to further reduce the water content with a separator, but the resin sludge that has undergone agglomeration is in a state where moisture has been taken into the interior, so moisture can be easily separated even with a separator. As a result, as described above, the amount of industrial waste entrusted to an industrial processor is extremely large.
[0007]
Accordingly, an object of the present invention is to reduce the amount of industrial waste entrusted to an industrial processor by lowering the water content in the resin sludge.
[0008]
[Means for Solving the Problems]
In order to achieve this object, the present invention adds an acidic chemical solution to an alkaline waste solution containing a resin component, warms it to a first temperature, causes an agglomeration reaction, and then performs a second reaction at a temperature higher than the first temperature. The agglomeration reaction is carried out by heating to a temperature of 1, and then the resin sludge and treated water are separated by a separation device, thereby achieving the intended purpose.
[0009]
DETAILED DESCRIPTION OF THE INVENTION
According to the first aspect of the present invention, the aggregation reaction is performed at the first temperature and the second temperature higher than the first temperature, and the heating temperature is gradually changed from low to high. By doing so, the sludge that agglomerates becomes large at once, so that a large amount of moisture is not taken in, and as a result, it becomes very easy to separate the moisture in the subsequent separation apparatus, thereby allowing the industrial processor to The amount of industrial waste entrusted to the company is extremely small, and the processing cost can be reduced.
[0010]
In the invention according to claim 2 of the present invention, an acidic chemical solution is added to an alkaline waste solution, heated to 30 to 50 ° C., and the residual sludge containing resin sludge is removed after removing the supernatant solution after coagulation precipitation. The method according to claim 1, wherein the temperature is raised to 70 ° C, wherein the first temperature is set to 30 to 50 ° C to improve the transportability to the next, and the second temperature. Is set to 55 to 70 ° C. to improve the separability.
[0011]
The invention according to claim 3 of the present invention is characterized in that the temperature of the alkaline waste liquid according to claim 1 or 2 is temporarily lowered when the resin sludge containing waste liquid heated to the second temperature is transferred. This is a wastewater treatment method in which the agglomerated reaction product is cooled to a temperature suitable for transportability.
[0012]
Invention of Claim 4 of this invention is set as the wastewater treatment method of the alkaline waste liquid of Claim 3 characterized by temperature-falling to 20-40 degreeC, and temperature-falls to the temperature excellent in the conveyance property. It has the action.
[0013]
The invention described in claim 5 of the present invention is the wastewater treatment method for alkaline waste liquid according to claim 1, wherein the coagulation reaction is performed in an acidic region. There is a difference in fluidity, and the aggregated precipitate generated in the acidic region is suitable for wastewater treatment.
[0014]
The invention according to claim 6 of the present invention is the wastewater treatment method for alkaline waste liquid according to claim 5, characterized in that the pH value of the acidic region is 2 to 4, and among the acidic region, Aggregated precipitates generated in the range of PH2-4 are particularly excellent in wastewater treatment.
[0015]
The invention according to claim 7 of the present invention includes a reaction vessel provided with a stirrer and a first heater, a metering pump for dropping a chemical solution from the chemical solution tank to the reaction vessel, and raising the temperature of the waste liquid in the reaction vessel. A pump for transferring to the tank; a second heater provided in the temperature raising tank; and a pump for transferring waste liquid from the temperature raising tank to the separation device, wherein the heating temperature by the second heater is the first temperature. The effect of claim 1 is achieved by setting the temperature higher than the heating temperature by the heater.
[0016]
Hereinafter, an embodiment of the present invention will be described with reference to the drawings.
FIG. 1 is a schematic configuration diagram of an apparatus showing a method for treating wastewater of alkaline waste liquid according to the present invention. In FIG. 1, 1 is an alkaline waste solution containing a resin component of an etching resist, 2, 2a is a resin sludge, 3 is a water storage tank, 4 is a reaction tank, 5 is a heater, 6 is a stirrer, and 7a to 7e are transfer pumps. , 8 is a metering pump, 9 is a temperature raising tank, 10 is a separation device, 11a to 11f are transfer pipes, 12 is a valve, 13 is a chemical solution tank, 14 is an acidic drug, 15 is a thermometer, 16 is a PH meter, 17a , 17b is treated wastewater.
[0017]
In the manufacturing process of the printed wiring board, the alkaline waste liquid 1 having a deteriorated developing and peeling ability is sent to the water storage tank 3 of the wastewater treatment facility via the transfer pipe 11a as shown in FIG. Relatively large resin sludge 2 and foreign matters in the alkaline waste liquid 1 accumulate on the bottom of the water storage tank 3. The alkaline waste liquid 1a in the supernatant of the water storage tank 3 is sent to the reaction tank 4 by the transfer pump 7a through the transfer pipe 11b, and the resin sludge 2 and foreign matter deposited on the bottom of the water storage tank 3 are periodically removed by opening the valve 12. After that, it is consigned to an industrial processor as industrial waste.
[0018]
While stirring the alkaline waste liquid 1a in the reaction tank 4 with the stirrer 6 and heating it with the warmer 5, 60 vol% sulfuric acid is dropped into the reaction tank 4 with the metering pump 8 as the acidic chemical 14 in the chemical liquid tank 13. The pH meter 16 provided in the reaction tank 4 stops dropping the acidic drug 14 when the PH value is 3 to 4, and the heating is finished when the measured value of the thermometer 15 is 30 to 50 ° C. After 10 to 20 minutes, the agitator 6 is stopped. Thereafter, the agglomerated reaction product generated in the reaction tank 4 is allowed to stand for about 10 to 12 hours, and is deposited on the bottom of the reaction tank 4 as a resin-based sludge 2a. About 70% of the supernatant processing waste water 17a in the reaction tank 4 is sent to the raw water tank (not shown) by the transfer pump 7B via the transfer pipe 11c, and is discharged as general waste water by adjusting the pH.
[0019]
The remaining alkaline waste liquid 1b containing the resin sludge 2a corresponding to the remaining 30% is sent to the heating tank 9 by the transfer pump 7c through the transfer pipe 11d. Since the alkaline waste liquid 1b is an agglomerated reaction product at 30 to 50 ° C., the water content is high and the separability is not good, but the fluidity is high and the pumpability is excellent. While stirring the alkaline waste liquid 1b in the temperature raising tank 9 with the stirrer 6, the temperature is raised to 55 to 70 ° C. with the heater 5 and the stirring is stopped. The resin sludge 2a at this time becomes an alkaline waste liquid 1c having a low water content. Thereafter, the alkaline waste liquid 1c heated to 55 to 70 ° C. is cooled to 20 to 40 ° C. by natural standing or the like in order to improve fluidity and transportability, and sent to the separation device 10 by the transfer pump 7d through the transfer pipe 11e. . A precipitate at 20 to 40 ° C. is clay-like and has excellent transportability.
[0020]
Next, the resin sludge 2b and the treated water (filtrate) are separated using the centrifugal separator of the separation device 10, and the treated wastewater 17b is sent to the raw water tank by the transfer pump 7e through the transfer pipe 11f. To discharge as general wastewater. The residual resin sludge 2b at this time has a very low moisture content, and can reduce the amount of industrial waste.
[0021]
【The invention's effect】
As described above, according to the present invention, the aggregation reaction is performed at the first temperature and the second temperature higher than the first temperature. By performing the heating temperature stepwise from a low temperature to a high temperature, Aggregating sludge does not take in a large amount of moisture when it becomes large at once as a conventional method, and as a result, it becomes very easy to separate moisture in the subsequent separation equipment, thereby industrial waste entrusted to industrial processors The amount of material is extremely reduced, and the processing cost can be reduced.
[Brief description of the drawings]
FIG. 1 is a schematic configuration diagram of an alkaline waste liquid wastewater treatment apparatus according to the present invention.
DESCRIPTION OF SYMBOLS 1 Alkaline waste liquid 2,2a, 2b Resin system sludge 3 Water storage tank 4 Reaction tank 5 Heater 6 Stirrer 7a-7e Transfer pump 8 Metering pump 9 Temperature rising tank 10 Separation apparatus 11a-11f Transfer pipe 12 Valve 13 Chemical solution tank 14 Acidic medicine 15 Thermometer 16 PH meter 17a, 17b Treatment wastewater

Claims (7)

樹脂成分を含有したアルカリ廃液に酸性薬液を添加し、第1の温度に加温して凝集反応をさせ、次に前記第1の温度より高温の第2の温度に加温して凝集反応をさせ、その後分離装置で樹脂系スラッジと処理水に分離するアルカリ廃液の廃水処理方法。An acidic chemical solution is added to an alkaline waste liquid containing a resin component, heated to a first temperature to cause an agglomeration reaction, and then heated to a second temperature higher than the first temperature to cause an agglomeration reaction. Waste water treatment method for alkaline waste liquid, which is then separated into resin sludge and treated water by a separation device. アルカリ廃液に酸性薬液を添加し、30〜50℃に加温し、凝集沈殿後の上澄み液を除去した後、残留した樹脂系スラッジ含有廃液を55〜70℃に加温することを特徴とする請求項1に記載のアルカリ廃液の廃水処理方法。An acidic chemical solution is added to the alkaline waste liquid, heated to 30 to 50 ° C., the supernatant liquid after coagulation precipitation is removed, and the remaining resin sludge-containing waste liquid is heated to 55 to 70 ° C. The wastewater treatment method of the alkaline waste liquid according to claim 1. 第2の温度に加温した樹脂系スラッジ含有廃液を分離装置へ移送する際に、一旦降温することを特徴とする請求項1または2に記載のアルカリ廃液の廃水処理方法。The wastewater treatment method for alkaline waste liquid according to claim 1 or 2, wherein the temperature is temporarily lowered when the resin sludge-containing waste liquid heated to the second temperature is transferred to the separation device. 20〜40℃まで降温することを特徴とする請求項3に記載のアルカリ廃液の廃水処理方法。The method for treating wastewater of an alkaline waste liquid according to claim 3, wherein the temperature is lowered to 20 to 40 ° C. 酸性領域で凝集反応を行わせることを特徴とする請求項1に記載のアルカリ廃液の廃水処理方法。The wastewater treatment method for alkaline waste liquid according to claim 1, wherein the coagulation reaction is performed in an acidic region. 酸性領域のPH値を2〜4とすることを特徴とする請求項5に記載のアルカリ廃液の廃水処理方法。6. The method for treating wastewater of an alkaline waste liquid according to claim 5, wherein the pH value of the acidic region is 2 to 4. 攪拌器、第1の加熱器を備えた反応槽と、この反応槽へ薬液槽から薬液を滴下する定量ポンプと、前記反応槽の廃液を昇温槽へ移送するポンプと、前記昇温槽に設けた第2の加熱器と、前記昇温槽の廃液を分離装置へ移送するポンプとを備え、第2の加熱器による加熱温度を、第1の加熱器による加熱温度よりも高温としたアルカリ廃液の廃水処理装置。A reactor equipped with a stirrer, a first heater, a metering pump for dropping a chemical solution from the chemical solution tank into the reaction vessel, a pump for transferring the waste solution of the reaction vessel to the temperature raising tank, and the temperature raising tank An alkali having a second heater provided and a pump for transferring the waste liquid from the heating tank to the separation device, wherein the heating temperature by the second heater is higher than the heating temperature by the first heater; Wastewater treatment equipment for waste liquid.
JP7270596A 1996-03-27 1996-03-27 Wastewater treatment method and wastewater treatment equipment for alkaline waste liquid Expired - Fee Related JP3864447B2 (en)

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