JP6690197B2 - Method and system for treating wastewater containing organic matter - Google Patents

Method and system for treating wastewater containing organic matter Download PDF

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JP6690197B2
JP6690197B2 JP2015223042A JP2015223042A JP6690197B2 JP 6690197 B2 JP6690197 B2 JP 6690197B2 JP 2015223042 A JP2015223042 A JP 2015223042A JP 2015223042 A JP2015223042 A JP 2015223042A JP 6690197 B2 JP6690197 B2 JP 6690197B2
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organic matter
membrane
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separation
wastewater
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JP2016112559A (en
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藤井 渉
渉 藤井
勝郎 石森
勝郎 石森
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Mitsubishi Chemical Corp
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • C02F3/1236Particular type of activated sludge installations
    • C02F3/1268Membrane bioreactor systems
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/441Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/442Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by nanofiltration
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Description

本発明は、有機物を含む廃水の処理方法及び処理システムに関する。   The present invention relates to a method and a system for treating wastewater containing organic matter.

工業廃水や生活廃水は、廃水中に含まれる懸濁物質や有機物等を取り除く処理が施されてから、工業用水として再利用されたり、河川等に放流される。
工業廃水等の処理方法として、例えば特許文献1には、工業廃水を、逆浸透膜を使用した逆浸透膜(RO膜)モジュールに供給して、その透過水と非透過水とに分離し、前記非透過水をさらに蒸発濃縮装置に供給して濃縮処理する廃水の濃縮処理方法が開示されている。
しかしながら、特許文献1の処理方法では、有機物を含む廃水(特に、高濃度有機物を含む廃水)を処理すると、廃水中に含まれる有機物が、逆浸透膜に目詰まりを生じさせたり、逆浸透膜を溶解する等の問題があった。
Industrial wastewater and domestic wastewater are reused as industrial water or discharged to rivers, etc., after being subjected to a treatment to remove suspended substances, organic substances, etc. contained in the wastewater.
As a method for treating industrial wastewater and the like, for example, in Patent Document 1, industrial wastewater is supplied to a reverse osmosis membrane (RO membrane) module using a reverse osmosis membrane and separated into permeated water and non-permeated water, There is disclosed a method for concentrating waste water by further supplying the non-permeated water to an evaporative concentrator to condense it.
However, in the treatment method of Patent Document 1, when wastewater containing organic matter (in particular, wastewater containing high-concentration organic matter) is treated, the organic matter contained in the wastewater causes clogging of the reverse osmosis membrane or the reverse osmosis membrane. There was a problem such as melting.

特開2007−789号公報JP, 2007-789, A

有機物を含む廃水の処理方法として、活性汚泥中の微生物の作用により有機物を生物分解する生物処理と、分離膜により固液分離し分離膜を透過した処理水を得る膜処理とを組み合わせた膜分離活性汚泥処理(MBR)法がある。
MBR法は、有機物を含む廃水の処理方法として有効な手段であるが、高濃度有機物を含む廃水を処理する場合には以下のような問題があった。
すなわち、有機物を生物分解する生物処理に要する時間は、廃水に含まれる有機物の濃度が高い程、長くなる。そのため高濃度有機物を含む廃水をMBR法で処理するには、活性汚泥中に前記廃水を長時間滞留させて生物処理を行う必要がある。一方、工場や家庭からは、逐次新たな廃水が排出される。そのため、MBR工程の活性汚泥中に廃水を長時間滞留させて生物処理を行うと、その間、MBR工程に新たな廃水を供給できず、工場や家庭から排出される廃水の排出量と、MBR法により処理される廃水の処理量とのバランスが保てなくなる。
これを避けるためには、MBR工程において生物処理が行われる活性汚泥槽を大きく形成して、単位時間あたりの生物処理を増やすことが考えられるが、この場合、廃水処理システムをコンパクトに構築できなくなる。
As a method for treating wastewater containing organic matter, membrane separation that combines biological treatment that biodegrades organic matter by the action of microorganisms in activated sludge and membrane treatment that obtains treated water that has undergone solid-liquid separation by a separation membrane and permeates the separation membrane There is an activated sludge treatment (MBR) method.
The MBR method is an effective means for treating wastewater containing organic matter, but has the following problems when treating wastewater containing high-concentration organic matter.
That is, the higher the concentration of the organic matter contained in the wastewater, the longer the time required for the biological treatment for biodegrading the organic matter. Therefore, in order to treat wastewater containing high-concentration organic matter by the MBR method, it is necessary to retain the wastewater in activated sludge for a long time and perform biological treatment. On the other hand, new wastewater is sequentially discharged from factories and households. Therefore, when wastewater is retained in activated sludge in the MBR process for a long time for biological treatment, new wastewater cannot be supplied to the MBR process during that time, and the amount of wastewater discharged from factories and households and the MBR method Therefore, the balance with the amount of waste water treated cannot be maintained.
In order to avoid this, it is conceivable to form a large activated sludge tank for biological treatment in the MBR process to increase biological treatment per unit time, but in this case, the wastewater treatment system cannot be constructed compactly. .

本発明は、上記事情に鑑みてなされたものであり、有機物を含む廃水(特に、高濃度有機物を含む廃水)をMBR法によりバランスよく処理できる廃水の処理方法及び処理システムを提供することを目的とする。   The present invention has been made in view of the above circumstances, and an object of the present invention is to provide a wastewater treatment method and a treatment system capable of treating wastewater containing organic matter (in particular, wastewater containing high-concentration organic matter) in a well-balanced manner by the MBR method. And

本発明は以下の態様を有する。
[1]有機物を含む廃水を、蒸発濃縮処理又は蒸留処理し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する蒸発分離工程と、前記溶液Bを、膜分離活性汚泥処理法により処理して処理水を得る膜分離活性汚泥処理工程と、を含むことを特徴とする、有機物を含む廃水の処理方法。
[2]常圧下での沸点が100℃以上である有機物を含む廃水を、蒸発濃縮処理し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する蒸発分離工程と、前記溶液Bを、膜分離活性汚泥処理法により処理して処理水を得る膜分離活性汚泥処理工程と、を含むことを特徴とする、有機物を含む廃水の処理方法。
[3]常圧下での沸点が100℃未満である有機物を含む廃水を、蒸留処理し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する蒸発分離工程と、前記溶液Bを、膜分離活性汚泥処理法により処理して処理水を得る膜分離活性汚泥処理工程と、を含むことを特徴とする、有機物を含む廃水の処理方法。
[4]前記処理水を再利用することを特徴とする、[1]〜[3]のいずれかに記載の有機物を含む廃水の処理方法。
[5]さらに、前記処理水を、逆浸透膜又はナノろ過膜によってろ過処理し、前記逆浸透膜又はナノろ過膜を透過したろ液と、逆浸透膜又はナノろ過膜を透過しない濃縮水とに分離するろ過分離工程を含むことを特徴とする、[1]〜[3]のいずれかに記載の有機物を含む廃水の処理方法。
[6]前記ろ液を再利用することを特徴とする、[5]に記載の有機物を含む廃水の処理方法。
[7]さらに、前記濃縮水を、前記の蒸発分離工程に返送することを特徴とする、[5]又は[6]に記載の有機物を含む廃水の処理方法。
[8]前記有機物を含む廃水の全有機炭素(TOC)濃度が、2,000〜50,000mg/Lであることを特徴とする、[1]〜[7]のいずれかに記載の有機物を含む廃水の処理方法。
[9]前記有機物を含む廃水に含まれる有機物が、N,N−ジメチルアセトアミド、N−メチル−2−ピロリドン及びN,N−ジメチルホルムアミドから選ばれる1種以上の化合物を含むことを特徴とする、[1]〜[8]のいずれかに記載の有機物を含む廃水の処理方法。
[10]有機物を含む廃水を、蒸発濃縮処理又は蒸留処理し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する蒸発分離装置と、前記溶液Bを、膜分離活性汚泥処理法により処理して処理水を得る膜分離活性汚泥処理装置と、を備えることを特徴とする、有機物を含む廃水の処理システム。
[11]前記処理水を再利用するための処理水流路を備えることを特徴とする、[10]に記載の有機物を含む廃水の処理システム。
[12]さらに、前記処理水を、逆浸透膜又はナノろ過膜によってろ過処理し、前記逆浸透膜又はナノろ過膜を透過したろ液と、逆浸透膜又はナノろ過膜を透過しない濃縮水とに分離するろ過分離装置を備えることを特徴とする、[10]に記載の有機物を含む廃水の処理システム。
[13]前記ろ液を再利用するためのろ液流路を備えることを特徴とする、[12]に記載の有機物を含む廃水の処理システム。
[14]さらに、前記濃縮水を、前記の蒸発分離装置に返送するための濃縮水返送路を備えることを特徴とする、[12]又は[13]に記載の有機物を含む廃水の処理システム。
[15]前記有機物を含む廃水の全有機炭素(TOC)濃度が、2,000〜50,000mg/Lであることを特徴とする、[10]〜[14]のいずれかに記載の有機物を含む廃水の処理システム。
[16]前記有機物を含む廃水に含まれる有機物が、N,N−ジメチルアセトアミド、N−メチル−2−ピロリドン及びN,N−ジメチルホルムアミドから選ばれる1種以上の化合物を含むことを特徴とする、[10]〜[15]のいずれかに記載の有機物を含む廃水の処理システム。
The present invention has the following aspects.
[1] Evaporative separation step of subjecting wastewater containing organic matter to evaporative concentration treatment or distillation treatment to separate the solution A in which the organic matter is concentrated and the solution B in which the concentration of the organic matter is reduced, and the solution B. And a membrane separation activated sludge treatment step for obtaining treated water by treatment by a membrane separation activated sludge treatment method.
[2] Evaporation of wastewater containing an organic substance having a boiling point of 100 ° C. or higher under normal pressure by evaporative concentration to separate a solution A in which the organic substance is concentrated and a solution B in which the concentration of the organic substance is reduced. A method for treating wastewater containing organic matter, comprising: a separation step; and a membrane separation activated sludge treatment step of treating the solution B by a membrane separation activated sludge treatment method to obtain treated water.
[3] Evaporative separation in which wastewater containing an organic substance having a boiling point under atmospheric pressure of less than 100 ° C. is subjected to a distillation treatment to separate a solution A in which the organic substance is concentrated and a solution B in which the concentration of the organic substance is reduced. A method for treating wastewater containing organic matter, comprising: a step; and a step of treating the solution B by a membrane separation activated sludge treatment method to obtain treated water.
[4] The method for treating wastewater containing organic matter according to any one of [1] to [3], wherein the treated water is reused.
[5] Further, the treated water is filtered through a reverse osmosis membrane or a nanofiltration membrane, and a filtrate that has passed through the reverse osmosis membrane or the nanofiltration membrane and concentrated water that does not pass through the reverse osmosis membrane or the nanofiltration membrane. The method for treating wastewater containing organic matter according to any one of [1] to [3], which comprises a filtration separation step of separating into.
[6] The method for treating wastewater containing organic matter according to [5], wherein the filtrate is reused.
[7] The method for treating wastewater containing organic matter according to [5] or [6], characterized in that the concentrated water is returned to the evaporative separation step.
[8] The organic matter according to any one of [1] to [7], wherein the wastewater containing the organic matter has a total organic carbon (TOC) concentration of 2,000 to 50,000 mg / L. Waste water treatment method including.
[9] The organic matter contained in the wastewater containing the organic matter contains at least one compound selected from N, N-dimethylacetamide, N-methyl-2-pyrrolidone and N, N-dimethylformamide. The method for treating wastewater containing the organic substance according to any one of [1] to [8].
[10] An evaporative separator that evaporates and concentrates wastewater containing organic matter to separate it into a solution A in which the organic matter is concentrated and a solution B in which the concentration of the organic matter is reduced, and the solution B. And a membrane separation activated sludge treatment device for obtaining treated water by treating by a membrane separation activated sludge treatment method.
[11] The treatment system for wastewater containing organic matter according to [10], further comprising a treated water flow path for reusing the treated water.
[12] Furthermore, the treated water is filtered through a reverse osmosis membrane or a nanofiltration membrane, and a filtrate that has passed through the reverse osmosis membrane or the nanofiltration membrane and concentrated water that does not pass through the reverse osmosis membrane or the nanofiltration membrane. The wastewater treatment system containing an organic matter according to [10], characterized in that the wastewater treatment system is equipped with a filtration separation device.
[13] The wastewater treatment system containing an organic matter according to [12], further comprising a filtrate flow path for reusing the filtrate.
[14] The treatment system for wastewater containing organic matter according to [12] or [13], further comprising a concentrated water return passage for returning the concentrated water to the evaporation / separation device.
[15] The organic matter according to any one of [10] to [14], wherein the wastewater containing the organic matter has a total organic carbon (TOC) concentration of 2,000 to 50,000 mg / L. Wastewater treatment system including.
[16] The organic matter contained in the wastewater containing the organic matter contains at least one compound selected from N, N-dimethylacetamide, N-methyl-2-pyrrolidone and N, N-dimethylformamide. , [10] to [15] a wastewater treatment system containing the organic matter.

本発明の廃水の処理方法及び処理システムによれば、有機物を含む廃水をMBR法によりバランスよく処理できる。特に、高濃度有機物を含む廃水の処理方法及び処理方法として、最適に用いることができる。   According to the wastewater treatment method and treatment system of the present invention, wastewater containing organic matter can be treated in a well-balanced manner by the MBR method. In particular, it can be optimally used as a method and a method for treating wastewater containing high-concentration organic matter.

本発明の廃水の処理システムの一実施形態を示す概略構成図である。1 is a schematic configuration diagram showing an embodiment of a wastewater treatment system of the present invention. 本発明の廃水の処理システムの他の実施形態を示す概略構成図である。It is a schematic block diagram which shows other embodiment of the waste water treatment system of this invention. 本発明の廃水の処理システムの他の実施形態を示す概略構成図である。It is a schematic block diagram which shows other embodiment of the waste water treatment system of this invention.

以下、本発明の廃水の処理方法について、実施形態例を示して説明する。ただし、本発明は以下の実施形態に限定されない。   Hereinafter, the wastewater treatment method of the present invention will be described with reference to exemplary embodiments. However, the present invention is not limited to the following embodiments.

<第一実施形態>
図1は、本発明の第一実施形態の有機物を含む廃水の処理方法に用いる処理システム1の概略構成図である。
処理システム1は、有機物を含む廃水を、蒸発濃縮処理又は蒸留処理し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する蒸発分離装置10と、前記溶液B水を、膜分離活性汚泥処理(MBR)法により処理して処理水を得る膜分離活性汚泥処理装置20と、を備える。
<First embodiment>
FIG. 1 is a schematic configuration diagram of a treatment system 1 used in a method for treating wastewater containing organic matter according to the first embodiment of the present invention.
The treatment system 1 evaporates and concentrates waste water containing an organic substance to separate it into a solution A in which the organic substance is concentrated and a solution B in which the concentration of the organic substance has been reduced, and A membrane-separated activated sludge treatment device 20 that obtains treated water by treating the solution B water by a membrane-separated activated sludge treatment (MBR) method.

(蒸発分離装置10)
蒸発分離装置10は、蒸発分離器11を備える。
蒸発分離装置10には、有機物を含む廃水が貯留された原水槽41からの廃水が供給される廃水流路12と、蒸発分離器11から前記有機物が濃縮された溶液Aを排出する溶液A流路13と、該分離器11から前記有機物の濃度が低減された溶液Bを排出する溶液B流路14とが接続されている。
(Evaporation separator 10)
The evaporative separator 10 includes an evaporative separator 11.
The evaporative separator 10 is supplied with wastewater from a raw water tank 41 in which wastewater containing organic matter is stored, and a solution A flow for discharging the solution A in which the organic matter is concentrated from the evaporative separator 11. The path 13 and the solution B flow path 14 for discharging the solution B having the reduced concentration of the organic substance from the separator 11 are connected to each other.

蒸発分離器11は、有機物を含む廃水を蒸発し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離できる形態であればよく、特に限定されない。
蒸発分離器11としては、例えば、単効用又は多重効用方式、自己蒸気圧縮方式、多段フラッシュ方式、液膜流下方式等が挙げられる。
The evaporative separator 11 is not particularly limited as long as it is capable of evaporating wastewater containing an organic substance and separating it into a solution A in which the organic substance is concentrated and a solution B in which the concentration of the organic substance is reduced.
Examples of the evaporative separator 11 include a single-effect or multiple-effect method, a self-vapor compression method, a multi-stage flash method, and a liquid film flow-down method.

(膜分離活性汚泥処理装置20)
膜分離活性汚泥処理装置20は、活性汚泥槽21と、活性汚泥槽21内の底部近傍に配置された散気管22と、活性汚泥槽21内かつ散気管22の上方に配置された分離膜モジュール25と、を備える。膜分離活性汚泥処理装置20には、該装置20からの処理水を排出する処理水流路26と、該装置20からの余剰汚泥を排出する余剰汚泥流路28とが接続されている。
上記散気管22には、散気管22にエアを供給するブロア23と、散気管22とブロア23とを接続するエア導入管24が接続されている。
上記処理水流路26には、その流路の途中に吸引ポンプ27が設けられている。前記吸引ポンプ27により、分離膜モジュール25内を減圧にすることができ、活性汚泥と処理水(透過水)とが固液分離される。さらに前記処理水が、処理水流路26を経て、活性汚泥槽21の外へ排出される。
(Membrane separation activated sludge treatment device 20)
The membrane separation activated sludge treatment device 20 includes an activated sludge tank 21, an air diffusing pipe 22 arranged near the bottom of the activated sludge tank 21, and a separation membrane module arranged in the activated sludge tank 21 and above the air diffusing pipe 22. 25, and. The membrane separation activated sludge treatment device 20 is connected to a treated water flow passage 26 for discharging treated water from the device 20 and an excess sludge flow passage 28 for discharging excess sludge from the device 20.
A blower 23 that supplies air to the air diffuser 22 and an air introduction pipe 24 that connects the air diffuser 22 and the blower 23 are connected to the air diffuser 22.
A suction pump 27 is provided in the treated water channel 26 in the middle of the channel. The suction pump 27 can reduce the pressure in the separation membrane module 25, and the activated sludge and the treated water (permeate) are separated into solid and liquid. Further, the treated water is discharged to the outside of the activated sludge tank 21 through the treated water channel 26.

分離膜モジュール25としては、公知の分離膜(ろ過膜)を備えた公知の分離膜モジュールを用いることができる。
分離膜の種類としては、精密ろ過膜(MF膜)又は限外ろ過膜(UF膜)が好ましい。
分離膜の形状としては、中空糸膜、平膜、管状膜、袋状膜等が挙げられる。これらのうち、容積ベースで比較した場合に膜面積の高度集積が可能であることから、中空糸膜が好ましい。
As the separation membrane module 25, a known separation membrane module including a known separation membrane (filtration membrane) can be used.
As the type of separation membrane, a microfiltration membrane (MF membrane) or an ultrafiltration membrane (UF membrane) is preferable.
Examples of the shape of the separation membrane include a hollow fiber membrane, a flat membrane, a tubular membrane, and a bag-shaped membrane. Of these, hollow fiber membranes are preferred because they allow a high degree of integration of the membrane area when compared on a volume basis.

分離膜の材質としては、有機材料(セルロース、ポリオレフィン、ポリスルフォン、ポリビニルアルコール、ポリメチルメタクリレート、ポリフッ化ビニリデン、ポリ4フッ化エチレン等)、金属(ステンレス等)、無機材料(セラミック等)が挙げられる。分離膜の材質は、有機物を含む廃水の性状等に応じて適宜選択される。   Examples of the material of the separation membrane include organic materials (cellulose, polyolefin, polysulfone, polyvinyl alcohol, polymethylmethacrylate, polyvinylidene fluoride, polytetrafluoroethylene, etc.), metals (stainless steel, etc.), inorganic materials (ceramics, etc.). To be The material of the separation membrane is appropriately selected according to the properties of wastewater containing organic substances.

分離膜の孔径は、処理の目的に応じて適宜選択すればよい。膜分離活性汚泥処理法において、分離膜の孔径は、0.001〜3μmが好ましい。孔径が0.001μm未満では、膜の抵抗が大きくなりやすい。孔径が3μmを超えると、活性汚泥を完全に分離することができないため、処理水(透過水)の水質が悪化するおそれがある。分離膜の孔径は、精密ろ過膜の範囲とされる0.04〜1.0μmがより好ましい。
分離膜モジュール25は、活性汚泥槽21内に1つ配置されてもよいし複数配置されてもよい。
The pore size of the separation membrane may be appropriately selected according to the purpose of treatment. In the membrane separation activated sludge treatment method, the pore size of the separation membrane is preferably 0.001 to 3 μm. If the pore size is less than 0.001 μm, the resistance of the film tends to increase. If the pore size exceeds 3 μm, the activated sludge cannot be completely separated, and the water quality of the treated water (permeate) may deteriorate. The pore diameter of the separation membrane is more preferably 0.04 to 1.0 μm in the range of the microfiltration membrane.
One separation membrane module 25 may be arranged in the activated sludge tank 21, or a plurality of separation membrane modules 25 may be arranged.

膜分離活性汚泥処理装置20においては、散気管22と分離膜モジュール25とが一体化された分離膜ユニットを用いてもよい。このような分離膜ユニットとしては、例えば特開2013−202524号公報に記載の分離膜ユニット等が挙げられる。   In the membrane separation activated sludge treatment device 20, a separation membrane unit in which the air diffuser 22 and the separation membrane module 25 are integrated may be used. Examples of such a separation membrane unit include the separation membrane unit described in JP2013-202524A.

図1に示す処理システム1を用いた廃水の処理方法は、蒸発分離装置10で有機物を含む廃水を蒸発濃縮処理又は蒸留処理し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する蒸発分離工程と、前記溶液Bを、膜分離活性汚泥処理装置20で膜分離活性汚泥処理(MBR)法により処理して処理水を得る工程と、を含む。   In the method of treating wastewater using the treatment system 1 shown in FIG. 1, a wastewater containing organic matter is subjected to an evaporative concentration treatment or a distillation treatment in an evaporative separation device 10 to reduce the concentration of the solution A in which the organic matter is concentrated and the concentration of the organic matter. The method includes an evaporative separation step of separating the solution B into a treated solution B, and a step of treating the solution B by a membrane separation activated sludge treatment device 20 by a membrane separation activated sludge treatment (MBR) method to obtain treated water.

(高濃度有機物を含む廃水)
本発明において「高濃度有機物を含む廃水」とは、MBR法で一般に処理される有機物含有廃水よりも、有機物が高い濃度で含まれる廃水を意味し、例えば全有機炭素(TOC)濃度が、2,000mg/L以上の廃水である。本発明における高濃度有機物を含む廃水中のTOC濃度の下限値は、2,000mg/L以上が好ましく、3,000mg/L以上がより好ましく、4,000mg/L以上がさらに好ましい。本発明における高濃度有機物を含む廃水中のTOC濃度の上限値は、特に限定されないが、50,000mg/L以下が好ましく、40,000mg/L以下がより好ましく、30,000以下がさらに好ましい。高濃度有機物を含む廃水中のTOC濃度が上記の好ましい範囲であると本発明の効果が得られやすくなる。
本発明の処理システムで処理される廃水は、蒸発分離工程によって、有機物が濃縮された溶液Aと、有機物の濃度が低減された溶液Bとに分離できれば、特に限定されない。前記廃水としては、例えば工場廃水(化学、製薬、製紙、飲料、製油、半導体、電子等)、生活廃水、畜産廃水等が挙げられる。
高濃度有機物を含む廃水は、蒸発分離装置10に供給される前に、あらかじめ当該廃水中から粗大な浮遊物質や土砂等を取り除く処理や、pHを調整する処理等が施されてもよい。
(Wastewater containing high-concentration organic matter)
In the present invention, “wastewater containing high-concentration organic matter” means wastewater containing organic matter at a higher concentration than the wastewater containing organic matter generally treated by the MBR method, and for example, total organic carbon (TOC) concentration is 2 Waste water of 1,000 mg / L or more. The lower limit of the TOC concentration in the wastewater containing high-concentration organic matter in the present invention is preferably 2,000 mg / L or more, more preferably 3,000 mg / L or more, and further preferably 4,000 mg / L or more. The upper limit of the TOC concentration in the wastewater containing the high-concentration organic matter in the present invention is not particularly limited, but is preferably 50,000 mg / L or less, more preferably 40,000 mg / L or less, still more preferably 30,000 or less. When the TOC concentration in the wastewater containing high-concentration organic matter is within the above-mentioned preferable range, the effect of the present invention is easily obtained.
The wastewater treated by the treatment system of the present invention is not particularly limited as long as it can be separated into the solution A in which the organic matter is concentrated and the solution B in which the concentration of the organic matter is reduced by the evaporative separation step. Examples of the wastewater include factory wastewater (chemical, pharmaceutical, papermaking, beverage, oil, semiconductor, electronic, etc.), domestic wastewater, livestock wastewater, and the like.
Before being supplied to the evaporative separation device 10, the wastewater containing high-concentration organic matter may be subjected in advance to a treatment of removing coarse floating substances, earth and sand, etc. from the wastewater, a treatment of adjusting the pH, and the like.

(蒸発分離工程)
蒸発分離工程では、まず、原水槽41に貯留された有機物を含む廃水が、廃水流路12を経て蒸発分離装置10に供給される。
次いで、蒸発分離装置10では、蒸発分離器11により有機物を含む廃水を蒸発処理して、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する分離操作が行われる。
上記分離操作では、有機物を含む廃水に含まれる有機物の沸点により、以下の(i)蒸発濃縮処理又は(ii)蒸留処理を行う。
(Evaporative separation process)
In the evaporative separation step, first, the wastewater containing the organic matter stored in the raw water tank 41 is supplied to the evaporative separation apparatus 10 through the wastewater flow path 12.
Next, in the evaporative separation device 10, a separation operation of evaporating the wastewater containing organic matter by the evaporative separator 11 to separate the solution A in which the organic matter is concentrated and the solution B in which the concentration of the organic matter is reduced is performed. Done.
In the above separation operation, the following (i) evaporative concentration treatment or (ii) distillation treatment is performed depending on the boiling point of the organic matter contained in the wastewater containing the organic matter.

(i)蒸発濃縮処理
蒸発濃縮処理は、常圧下での沸点が100℃以上である有機物を含む廃水を蒸発し、これを凝縮した凝縮分と、蒸発しなかった蒸発残分とに分離し、前記凝縮分を有機物の濃度が低減された溶液Bとして回収し、前記蒸発残分を有機物が濃縮された溶液Aとして回収する処理である。
(ii)蒸留処理
蒸留処理は、常圧下での沸点が100℃未満である有機物を含む廃水を蒸発し、これを凝縮した凝縮分と、蒸発しなかった蒸発残分とに分離し、前記凝縮分を有機物が濃縮された溶液Aとして回収し、前記蒸発残分を有機物の濃度が低減された溶液Bとして回収する処理である。
上記(i)蒸発濃縮処理と、(ii)蒸留処理は、廃水に含まれる有機物の沸点に応じて適宜選択される。
なお、常圧下での沸点が100℃以上である有機物と、常圧下での沸点が100℃未満の有機物の両方を含む廃水の場合には、前記廃水を蒸発し、これを凝縮した凝縮分と、蒸発しなかった蒸発残分とに分離する。そして、有機物の濃度が蒸発処理前の廃水よりも低減されている方を溶液Bとして回収し、有機物の濃度が蒸発処理前の廃水よりも高くなっている方を溶液Aとして回収すればよい。
また、溶液Bとしては、上記分離操作前の廃水中の有機物濃度よりも、有機物濃度が低減されたものであればよい。例えば、廃水に含まれる有機物が水と共沸等して、上記分離操作後の溶液Bに廃水中の有機物が含まれる場合であっても、溶液B中の有機物濃度が、上記分離操作前の有機物濃度よりも低減されていれば、本発明の廃水の処理方法を適用できる。
(I) Evaporative Concentration Treatment In the evaporative concentration treatment, waste water containing an organic substance having a boiling point of 100 ° C. or higher under normal pressure is evaporated, and this is separated into a condensed fraction that is condensed and an evaporation residue that is not evaporated, In this process, the condensed component is recovered as a solution B having a reduced concentration of organic substances, and the evaporation residue is recovered as a solution A having concentrated organic substances.
(Ii) Distillation treatment In the distillation treatment, wastewater containing an organic substance having a boiling point under atmospheric pressure of less than 100 ° C. is evaporated, and this is separated into a condensed fraction that is condensed and an evaporation residue that is not evaporated, In this process, the components are recovered as a solution A in which organic substances are concentrated, and the evaporation residue is recovered as a solution B in which the concentration of organic substances is reduced.
The above-mentioned (i) evaporative concentration treatment and (ii) distillation treatment are appropriately selected according to the boiling points of the organic substances contained in the wastewater.
In the case of waste water containing both an organic substance having a boiling point of 100 ° C. or more under normal pressure and an organic substance having a boiling point of less than 100 ° C. under normal pressure, the waste water is evaporated and condensed with condensed components. , And the evaporation residue that has not evaporated is separated. Then, one having a concentration of organic matter lower than that of the wastewater before the evaporation treatment may be recovered as the solution B, and one having a concentration of organic matter higher than that of the wastewater before the evaporation treatment may be recovered as the solution A.
In addition, the solution B may be any solution that has a lower organic matter concentration than the organic matter concentration in the wastewater before the separation operation. For example, even when the organic matter contained in the wastewater is azeotroped with water and the like and the solution B after the separation operation contains the organic matter in the wastewater, the concentration of the organic matter in the solution B is the same as that before the separation operation. If it is lower than the organic matter concentration, the wastewater treatment method of the present invention can be applied.

上記分離操作により分離された溶液Bは、溶液B流路14を経て、膜分離活性汚泥処理工程が行われる膜分離活性汚泥処理装置20に移送される。
また、上記分離操作により分離された溶液Aは、溶液A流路13を経て排出され、溶液A貯留槽(図示略)に貯留される。この溶液Aは産業廃棄物として処理されてもよい。
The solution B separated by the above separation operation is transferred to the membrane separation activated sludge treatment device 20 in which the membrane separation activated sludge treatment step is performed, through the solution B flow path 14.
The solution A separated by the above separating operation is discharged through the solution A flow path 13 and stored in a solution A storage tank (not shown). This solution A may be treated as industrial waste.

(膜分離活性汚泥処理工程)
膜分離活性汚泥処理法により処理して処理水を得る膜分離活性汚泥処理工程では、まず、上記蒸発分離工程で分離された溶液Bが、溶液B流路14を経て膜分離活性汚泥処理装置20の活性汚泥槽21に供給される。
(Membrane separation activated sludge treatment process)
In the membrane separation activated sludge treatment step of obtaining treated water by treating with the membrane separation activated sludge treatment method, first, the solution B separated in the evaporation separation step passes through the solution B flow path 14 and the membrane separation activated sludge treatment apparatus 20. Is supplied to the activated sludge tank 21.

活性汚泥槽21においては、溶液Bに対して、ブロア23を作動させて散気管22からエアを導入し、活性汚泥中の微生物に酸素を供給しながら生物処理が行われる。
さらに、活性汚泥槽21においては、吸引ポンプ27を作動させて分離膜モジュール25内を減圧にすることによって活性汚泥と処理水(透過水)とに固液分離される。この際、散気管22からエアを分離膜モジュール25に導入することによって、分離膜モジュール25の分離膜(例えば中空糸膜等)の表面を洗浄しながら、効率よく固液分離を行うことができる。
In the activated sludge tank 21, the biological treatment is performed on the solution B by operating the blower 23 to introduce air from the air diffuser 22 and supplying oxygen to the microorganisms in the activated sludge.
Further, in the activated sludge tank 21, the suction pump 27 is operated to reduce the pressure inside the separation membrane module 25, so that solid-liquid separation is performed into activated sludge and treated water (permeated water). At this time, by introducing air from the air diffuser 22 into the separation membrane module 25, solid-liquid separation can be efficiently performed while cleaning the surface of the separation membrane (for example, hollow fiber membrane) of the separation membrane module 25. .

分離膜モジュール25にて分離された処理水は、処理水流路26を経て排出される。この処理水は、工業用水(例えば、各種ボイラーの冷却水、洗浄液の溶媒等の工程水)等として再利用されたり、そのまま外部に放流されるが、環境負荷を低減でき水資源を有効活用できる点から再利用されることが好ましい。上記処理水が再利用されることで、外部に廃水が排出されない(ZLD:ゼロリキッドディスチャージ)処理方法及び処理システムを提供できる。
また、分離膜モジュール25にて分離された余剰汚泥は、余剰汚泥流路28を経て排出され、余剰汚泥貯留槽(図示略)に貯留される。なお、余剰汚泥には微生物が含まれているため、余剰汚泥の一部を、膜分離活性汚泥処理装置20の活性汚泥槽21に返送し、再び溶液Bの生物処理に用いてもよい。また、余剰汚泥は産業廃棄物として処理されてもよい。
The treated water separated by the separation membrane module 25 is discharged through the treated water channel 26. This treated water can be reused as industrial water (for example, cooling water for various boilers, process water such as solvent for cleaning liquid), or discharged directly to the outside, but it can reduce environmental load and effectively use water resources. It is preferably reused from the point. By reusing the treated water, it is possible to provide a treatment method and a treatment system in which wastewater is not discharged outside (ZLD: zero liquid discharge).
The surplus sludge separated by the separation membrane module 25 is discharged through the surplus sludge flow path 28 and stored in a surplus sludge storage tank (not shown). Since the excess sludge contains microorganisms, a part of the excess sludge may be returned to the activated sludge tank 21 of the membrane separation activated sludge treatment device 20 and used again for biological treatment of the solution B. Also, excess sludge may be treated as industrial waste.

以上説明した本発明の第一実施形態においては、膜分離活性汚泥処理(MBR)工程の前に、蒸発分離工程が行われることで、有機物濃度が低減された溶液Bに対してMBR工程が行われる。そのため、MBR工程の活性汚泥中に溶液Bを長時間滞留させて生物処理を行わなくてよい。その結果、工場や家庭から排出される廃水の排出量と、蒸発分離工程及びMBR工程で処理される廃水の処理量とのバランスが良好に保たれる。
さらに、MBR工程において活性汚泥槽を大きく形成しなくて済み、有機物を含む廃水の処理システムをコンパクトに構築できる。本発明の第一実施形態は、特に、高濃度有機物を含む廃水処理に、好適に用いることができる。
In the first embodiment of the present invention described above, the evaporative separation step is performed before the membrane separation activated sludge treatment (MBR) step, so that the MBR step is performed on the solution B having a reduced organic matter concentration. Be seen. Therefore, it is not necessary to retain the solution B in the activated sludge of the MBR process for a long time to perform biological treatment. As a result, a good balance is maintained between the amount of waste water discharged from factories and homes and the amount of waste water processed in the evaporative separation process and the MBR process.
Furthermore, it is not necessary to form a large activated sludge tank in the MBR process, and a wastewater treatment system containing organic matter can be constructed compactly. The first embodiment of the present invention can be suitably used particularly for treating wastewater containing high-concentration organic matter.

<第二実施形態>
次に、本発明の第二実施形態の有機物を含む廃水の処理方法について説明する。なお、以下に記載する実施形態において、第一実施形態に対応する構成要素には同一の符号を付してその詳細な説明を省略する。
図2は、本実施形態の処理方法に用いる処理システム2の概略構成図である。処理システム2は、膜分離活性汚泥処理装置20の下流側に、当該装置20から排出された処理水を逆浸透膜又はナノろ過膜でろ過するろ過分離装置30を備える以外は、第一実施形態で説明した処理システム1と同様の構成である。
<Second embodiment>
Next, a method for treating wastewater containing organic matter according to the second embodiment of the present invention will be described. In the embodiments described below, the components corresponding to those in the first embodiment are designated by the same reference numerals, and detailed description thereof will be omitted.
FIG. 2 is a schematic configuration diagram of the processing system 2 used in the processing method of this embodiment. The treatment system 2 is provided with a filtration separation device 30 for filtering the treated water discharged from the device 20 with a reverse osmosis membrane or a nanofiltration membrane, on the downstream side of the membrane separation activated sludge treatment device 20, except for the first embodiment. The configuration is the same as that of the processing system 1 described above.

ろ過分離装置30は、逆浸透膜又はナノろ過膜を備えるろ過装置31を備える。
ろ過分離装置30には、膜分離活性汚泥処理装置20からの処理水が供給される処理水流路26と、ろ過装置31の逆浸透膜又はナノろ過膜を透過したろ液を排出するろ液流路32と、前記逆浸透膜又はナノろ過膜を透過しない濃縮水を排出する濃縮水流路33とが接続されている。
The filtration separation device 30 includes a filtration device 31 including a reverse osmosis membrane or a nanofiltration membrane.
The filtration / separation device 30 discharges the filtrate that has passed through the treated water channel 26 to which the treated water from the membrane separation activated sludge treatment device 20 is supplied and the reverse osmosis membrane or the nanofiltration membrane of the filtration device 31 and discharges the filtrate. The channel 32 is connected to a concentrated water channel 33 that discharges concentrated water that does not pass through the reverse osmosis membrane or the nanofiltration membrane.

(ろ過分離装置30)
ろ過分離装置30は、逆浸透膜又はナノろ過膜を備えるろ過装置31を備える。
ろ過装置31は、1つ以上の逆浸透膜モジュール又はナノろ過膜モジュールを備える。
逆浸透膜又はナノろ過膜としては、特に限定されず、平膜、管状膜、中空糸膜、螺旋状膜等が挙げられる。
逆浸透膜又はナノろ過膜の材質としては、ポリアミド、ポリスルフォン、セルロースアセテート等が挙げられる。
逆浸透膜モジュール又はナノろ過膜モジュールは、逆浸透膜又はナノろ過膜を透過したろ液と、逆浸透膜又はナノろ過膜を透過しない濃縮水とを分離できる形態であればよく、特に限定されないが、例えば、集水管のまわりに逆浸透膜を巻き回した円柱状の逆浸透膜エレメントを円筒状のケーシングに収納した、いわゆるスパイラル型逆浸透膜モジュール等が挙げられる。
(Filtration and separation device 30)
The filtration separation device 30 includes a filtration device 31 including a reverse osmosis membrane or a nanofiltration membrane.
Filtration device 31 comprises one or more reverse osmosis membrane modules or nanofiltration membrane modules.
The reverse osmosis membrane or the nanofiltration membrane is not particularly limited, and examples thereof include a flat membrane, a tubular membrane, a hollow fiber membrane, and a spiral membrane.
Examples of the material for the reverse osmosis membrane or the nanofiltration membrane include polyamide, polysulfone, and cellulose acetate.
The reverse osmosis membrane module or the nanofiltration membrane module is not particularly limited as long as the filtrate that has passed through the reverse osmosis membrane or the nanofiltration membrane can be separated from the concentrated water that does not pass through the reverse osmosis membrane or the nanofiltration membrane. However, for example, there is a so-called spiral type reverse osmosis membrane module in which a cylindrical reverse osmosis membrane element in which a reverse osmosis membrane is wound around a water collection tube is housed in a cylindrical casing.

図2に示す処理システム2を用いた廃液の処理方法は、前述した蒸発分離工程及び膜分離活性汚泥処理工程に加えて、膜分離活性汚泥処理装置20からの処理水を、ろ過分離装置30に供給し、ろ過装置31の逆浸透膜又はナノろ過膜でろ過するろ過分離工程を含む以外は、第一実施形態の処理方法と同様である。   In the method for treating waste liquid using the treatment system 2 shown in FIG. 2, in addition to the evaporative separation step and the membrane separation activated sludge treatment step described above, the treated water from the membrane separation activated sludge treatment apparatus 20 is supplied to the filtration separation apparatus 30. The treatment method is the same as that of the first embodiment except that a filtration separation step of supplying and filtering with a reverse osmosis membrane or a nanofiltration membrane of the filtration device 31 is included.

(ろ過分離工程)
ろ過分離工程では、膜分離活性汚泥処理装置20からの処理水が、ろ過分離装置30に供給され、ろ過装置31の逆浸透膜又はナノろ過膜を透過するろ液と、逆浸透膜又はナノろ過膜を透過しない濃縮水とに分離される。
上記ろ液は、ろ液流路32を経て排出される。このろ液は、工業用水(例えば、各種ボイラーの冷却水、洗浄液の溶媒等の工程水)等として再利用されたり、そのまま外部に放流されるが、環境負荷を低減でき水資源を有効活用できる点から再利用されることが好ましい。上記ろ液が再利用されることで、外部に廃水が排出されない(ZLD:ゼロリキッドディスチャージ)処理方法及び処理システムを提供できる。なお、上記ろ液が外部に放流される場合には、ろ液に対し必要に応じてオゾン処理、紫外線照射等の処理が施されてもよい。
一方、上記濃縮水は、濃縮水流路33を経て排出され、濃縮水貯留槽(図示略)に貯留される。この濃縮水は産業廃棄物として処理されてもよい。
(Filtration and separation process)
In the filtration and separation step, the treated water from the membrane separation activated sludge treatment device 20 is supplied to the filtration and separation device 30 and passes through the reverse osmosis membrane or the nanofiltration membrane of the filtration device 31, and the reverse osmosis membrane or the nanofiltration. It is separated into concentrated water that does not permeate the membrane.
The filtrate is discharged through the filtrate flow path 32. This filtrate is reused as industrial water (for example, cooling water for various boilers, process water such as a solvent for cleaning liquid) or is directly discharged to the outside, but the environmental load can be reduced and water resources can be effectively used. It is preferably reused from the point. It is possible to provide a treatment method and a treatment system in which waste water is not discharged to the outside (ZLD: zero liquid discharge) by reusing the filtrate. When the filtrate is discharged to the outside, the filtrate may be subjected to a treatment such as ozone treatment or ultraviolet irradiation, if necessary.
On the other hand, the concentrated water is discharged through the concentrated water channel 33 and stored in a concentrated water storage tank (not shown). This concentrated water may be treated as industrial waste.

本実施形態の処理方法においては、第一実施形態の処理方法と同様の作用効果が得られるほか、ろ過分離工程の前に、蒸発分離工程及び膜分離活性汚泥処理工程が行われることで、有機物濃度が低減された処理水に対してろ過分離工程が行われる。そのため、有機物を含む廃水を、直接、逆浸透膜ろ過装置又はナノろ過膜ろ過装置で処理した場合に生じる逆浸透膜又はナノろ過膜の目詰まりや、逆浸透膜又はナノろ過膜の溶解等による破損を抑制できる。本実施形態の処理方法によれば、有機物廃水に含まれる有機物が、N,N−ジメチルアセトアミド、N−メチル−2−ピロリドン、N,N−ジメチルホルムアミド等の逆浸透膜又はナノろ過膜を溶解しやすい溶剤であっても、ろ過分離工程の前に、蒸発分離工程及び膜分離活性汚泥処理工程が行われ、これら溶剤の濃度が低減された処理水に対してろ過分離工程が行われるため、逆浸透膜又はナノろ過膜の溶解等による破損を抑制しやすくなる。
さらに、ろ過分離工程から得られるろ液は、膜分離活性汚泥処理工程から得られる処理水よりも水質がより高められ再利用しやすい。そのため、本実施形態の処理方法及び処理システムによれば、外部に廃水が排出されない(ZLD:ゼロリキッドディスチャージ)処理方法及び処理システムを構築しやすくなる。
本発明の第二実施形態は、特に、高濃度有機物を含む廃水処理に、好適に用いることができる。
In the treatment method of the present embodiment, in addition to the same effects as those of the treatment method of the first embodiment, before the filtration separation step, the evaporation separation step and the membrane separation activated sludge treatment step are carried out, organic matter A filtration separation step is performed on the treated water having a reduced concentration. Therefore, due to clogging of the reverse osmosis membrane or the nanofiltration membrane that occurs when the wastewater containing organic matter is directly treated with the reverse osmosis membrane filtration device or the nanofiltration membrane filtration device, the dissolution of the reverse osmosis membrane or the nanofiltration membrane, etc. Damage can be suppressed. According to the treatment method of the present embodiment, the organic matter contained in the organic matter wastewater dissolves the reverse osmosis membrane or the nanofiltration membrane of N, N-dimethylacetamide, N-methyl-2-pyrrolidone, N, N-dimethylformamide or the like. Even if it is a solvent that is easy to do, before the filtration separation step, the evaporation separation step and the membrane separation activated sludge treatment step are performed, and since the filtration separation step is performed on the treated water in which the concentration of these solvents is reduced, It becomes easy to suppress damage due to dissolution of the reverse osmosis membrane or the nanofiltration membrane.
Furthermore, the filtrate obtained from the filtration separation step has a higher water quality than the treated water obtained from the membrane separation activated sludge treatment step and is easy to reuse. Therefore, according to the treatment method and treatment system of the present embodiment, it is easy to construct a treatment method and treatment system in which wastewater is not discharged to the outside (ZLD: zero liquid discharge).
The second embodiment of the present invention can be suitably used particularly for treating wastewater containing high-concentration organic matter.

<第三実施形態>
次に、本発明の第三実施形態の有機物を含む廃水の処理方法について説明する。
図3は、本実施形態の処理方法に用いる処理システム3の概略構成図である。処理システム3は、濃縮水流路33に一端が接続され、他端が原水槽41に接続された濃縮水返送路34を備える以外は、第二実施形態で説明した処理システム2と同様の構成である。
<Third embodiment>
Next, a method for treating wastewater containing organic matter according to the third embodiment of the present invention will be described.
FIG. 3 is a schematic configuration diagram of the processing system 3 used in the processing method of the present embodiment. The treatment system 3 has the same configuration as the treatment system 2 described in the second embodiment, except that the treatment system 3 includes a concentrated water return passage 34, one end of which is connected to the concentrated water passage 33 and the other end of which is connected to the raw water tank 41. is there.

処理システム3を用いた有機物を含む廃水の処理方法においては、ろ過分離装置30から排出された濃縮水の一部を、濃縮水流路33及び濃縮水返送路34を介して、原水槽41に返送できる。   In the method for treating wastewater containing organic matter using the treatment system 3, a part of the concentrated water discharged from the filtration separation device 30 is returned to the raw water tank 41 via the concentrated water flow passage 33 and the concentrated water return passage 34. it can.

本実施形態の処理方法においては、第二実施形態の処理方法と同様の作用効果が得られるほか、ろ過分離工程で排出された濃縮水を原水槽に返送することで、該濃縮水に対して、再び、蒸発分離工程、分離膜活性汚泥処理工程及びろ過分離工程を行うことができる。これにより該濃縮水から再利用可能なろ液が得られる。そのため、産業廃棄物として処理される濃縮水量を削減でき、より環境負荷が低減された処理システムを構築できる。さらに、再利用できるろ液量を増やすことができ、水資源をより有効活用できる処理システムを構築できる。
本発明の第三実施形態は、特に、高濃度有機物を含む廃水処理に、好適に用いることができる。
In the treatment method of the present embodiment, in addition to the same operational effects as the treatment method of the second embodiment, by returning the concentrated water discharged in the filtration separation step to the raw water tank, The evaporation separation step, the separation membrane activated sludge treatment step and the filtration separation step can be performed again. This gives a reusable filtrate from the concentrated water. Therefore, the amount of concentrated water treated as industrial waste can be reduced, and a treatment system with a reduced environmental load can be constructed. Furthermore, the amount of filtrate that can be reused can be increased, and a treatment system that can make more effective use of water resources can be constructed.
The third embodiment of the present invention can be suitably used particularly for treating wastewater containing high-concentration organic matter.

<他の実施形態>
本発明について、第一実施形態〜第三実施形態を示して説明したが、本発明はこれらの実施形態に限定されない。
例えば、第一実施形態〜第三実施形態では、MBR工程における膜分離活性汚泥処理装置として、活性汚泥処理槽内に分離膜を浸漬する浸漬型(一体型)の膜分離活性汚泥処理装置20が用いられたがこれに限定されない。活性処理槽と、分離膜を浸漬した膜分離槽とをそれぞれ設け、活性処理槽での生物処理後に膜分離槽で膜分離を行うようにした、いわゆる槽外型(別置型)の膜分離活性汚泥処理装置が用いられてもよい。
<Other Embodiments>
The present invention has been described by showing the first to third embodiments, but the present invention is not limited to these embodiments.
For example, in the first to third embodiments, an immersion type (integrated type) membrane separation activated sludge treatment device 20 in which a separation membrane is immersed in an activated sludge treatment tank is used as the membrane separation activated sludge treatment device in the MBR process. Used, but not limited to. A so-called external type (separate type) membrane separation activity in which an active treatment tank and a membrane separation tank in which a separation membrane is immersed are each provided, and membrane separation is performed in the membrane separation tank after biological treatment in the active treatment tank. A sludge treatment device may be used.

第一実施形態においては、蒸発分離装置10の下流に活性汚泥処理装置20が配置されたがこれに限定されない。例えば、蒸発分離装置10と活性汚泥処理装置20の間に、蒸発分離装置10からの溶液Bを一時的に貯留する受け槽が設けられてもよい。また、活性汚泥処理装置20の下流に、活性汚泥処理装置20からの処理水を一時的に貯留する受け槽が設けられてもよい。受け槽が設けられることで、上記溶液Bや処理水の流量を調整しやすくなる。
第二実施形態及び第三実施形態においては、活性汚泥処理装置20の下流にろ過分離装置30が配置されたがこれに限定されない。例えば、活性汚泥処理装置20とろ過分離装置30の間に、活性汚泥処理装置20からの処理水を一時的に貯留する受け槽が設けられてもよい。また、ろ過分離装置30の下流に、ろ過分離装置30からのろ液を一時的に貯留する受け槽が設けられてもよい。
In the first embodiment, the activated sludge treatment device 20 is arranged downstream of the evaporative separation device 10, but it is not limited to this. For example, a receiving tank for temporarily storing the solution B from the evaporative separation device 10 may be provided between the evaporative separation device 10 and the activated sludge treatment device 20. Further, a receiving tank for temporarily storing the treated water from the activated sludge treatment device 20 may be provided downstream of the activated sludge treatment device 20. By providing the receiving tank, the flow rates of the solution B and the treated water can be easily adjusted.
In 2nd embodiment and 3rd embodiment, although the filtration separation apparatus 30 was arrange | positioned downstream of the activated sludge treatment apparatus 20, it is not limited to this. For example, a receiving tank for temporarily storing the treated water from the activated sludge treatment device 20 may be provided between the activated sludge treatment device 20 and the filtration separation device 30. Further, a receiving tank that temporarily stores the filtrate from the filtration separation device 30 may be provided downstream of the filtration separation device 30.

第一実施形態〜第三実施形態においては、溶液A貯留槽(図示略)、余剰汚泥貯留槽(図示略)及び濃縮水貯留槽(図示略)は、それぞれ別箇に設けられたがこれに限定されない。例えば、溶液A貯留槽と余剰汚泥貯留槽を一つの貯留槽とし、この貯留槽に、溶液A流路13と余剰汚泥流路28を接続するようにしたり、溶液A貯留槽、余剰汚泥貯留槽及び濃縮水貯留槽を一つの貯留槽とし、この貯留槽に、溶液A流路13、余剰汚泥流路28及び濃縮水流路33を接続するようにしてもよい。
さらに、第一実施形態〜第三実施形態における膜分離活性汚泥処理装置20に、分離膜モジュール25を洗浄するための洗浄装置を設けることや、各装置を接続する流路にポンプ等を設けることも任意である。
In the first to third embodiments, the solution A storage tank (not shown), the excess sludge storage tank (not shown), and the concentrated water storage tank (not shown) are provided separately, respectively. Not limited. For example, the solution A storage tank and the excess sludge storage tank are made into one storage tank, and the solution A flow path 13 and the excess sludge flow path 28 are connected to this storage tank, or the solution A storage tank and the excess sludge storage tank are connected. Alternatively, the concentrated water storage tank may be a single storage tank, and the solution A flow path 13, the excess sludge flow path 28, and the concentrated water flow path 33 may be connected to this storage tank.
Furthermore, the membrane separation activated sludge treatment device 20 in the first to third embodiments is provided with a cleaning device for cleaning the separation membrane module 25, and a pump or the like is provided in a flow path connecting each device. Is also optional.

以下、本発明を実施例によりさらに詳細に説明するが、本発明はこれに限定されるものではない。   Hereinafter, the present invention will be described in more detail with reference to Examples, but the present invention is not limited thereto.

本実施例においては、高濃度有機物を含む廃水を、第三実施形態に示した処理システム3を使用して、第三実施形態に示した処理方法により処理した。
本実施例における高濃度有機物を含む廃水としては、N,N−ジメチルアセトアミド(DMAC)を高濃度に含有する工程廃水を用いた。
In this example, wastewater containing high-concentration organic matter was treated by the treatment method shown in the third embodiment using the treatment system 3 shown in the third embodiment.
As the wastewater containing high-concentration organic matter in this example, process wastewater containing a high concentration of N, N-dimethylacetamide (DMAC) was used.

前記工程廃水を原水槽41に移送した。前記工程廃水の排出量は、10.0m/dであった。また、工程廃水中の全有機炭素濃度(TOC)は、4100mg/L、工程廃水中のDMAC濃度は、0.82質量%であった。
また、原水槽41に、下記ろ過分離工程で分離した濃縮水を返送するようにした。
The process wastewater was transferred to the raw water tank 41. The discharge amount of the process waste water was 10.0 m 3 / d. The total organic carbon concentration (TOC) in the process wastewater was 4100 mg / L, and the DMAC concentration in the process wastewater was 0.82% by mass.
Further, the concentrated water separated in the following filtration separation step was returned to the raw water tank 41.

(蒸発分離工程)
上記工程廃水及び上記濃縮水の混合廃水を、蒸発分離装置10に供給して、以下の条件で溶液Bと溶液Aとに分離した。
溶液Bの排出量:8.5m/d。溶液B中のDMAC濃度0.4質量%、TOC1700mg/L。
溶液Aの排出量:2.0m/d。溶液A中のDMAC濃度2.4質量%、TOC13000mg/L。
(Evaporative separation process)
The mixed wastewater of the process wastewater and the concentrated water was supplied to the evaporative separation device 10 and separated into a solution B and a solution A under the following conditions.
Discharge of solution B: 8.5 m 3 / d. DMAC concentration in solution B 0.4% by mass, TOC 1700 mg / L.
Discharge amount of solution A: 2.0 m 3 / d. DMAC concentration in solution A 2.4% by mass, TOC 13000 mg / L.

(膜分離活性汚泥処理工程)
上記溶液Bを、膜分離活性汚泥処理装置20に供給して、以下の条件で処理水を得た。
処理水(透過水)の排出量:8.5m/d。処理水中のDMAC濃度0.004質量%、TOC35mg/L。
分離膜モジュールの膜面積:18m(膜面積6mの中空糸膜モジュール×3基)。
分離膜モジュールの膜の種類:ポリフッ化ビニリデンを主成分とする公称孔径0.4μmの中空糸形状のMF膜。
(Membrane separation activated sludge treatment process)
The solution B was supplied to the membrane separation activated sludge treatment device 20 to obtain treated water under the following conditions.
Emission amount of treated water (permeated water): 8.5 m 3 / d. DMAC concentration in treated water 0.004% by mass, TOC 35 mg / L.
Membrane area of separation membrane module: 18 m 2 (hollow fiber membrane module of membrane area 6 m 2 x 3 units).
Membrane type of separation membrane module: hollow fiber MF membrane containing polyvinylidene fluoride as a main component and having a nominal pore diameter of 0.4 μm.

(ろ過分離工程)
上記処理水を、逆浸透膜を備えるろ過装置31に供給して、以下の条件でろ液と濃縮水とに分離した。
ろ液の排出量:8.0m/d。ろ液中のDMAC濃度0.0002質量%、TOC1.1mg/L。
濃縮水の排出量:0.5m/d。濃縮水中のDMAC濃度0.06質量%、TOC550mg/L。
逆浸透ろ過膜の膜面積:47m(膜面積7.9mのRO膜モジュール×6基)。
逆浸透ろ過膜:低圧スパイラル型逆浸透膜エレメント(日東電工株式会社製「ESPA2−4040」)。
上記ろ液を、製造工程における洗浄液として再利用した。また、上記濃縮水を原水槽41に返送した。
(Filtration and separation process)
The treated water was supplied to a filtration device 31 equipped with a reverse osmosis membrane, and separated into a filtrate and concentrated water under the following conditions.
Discharge of filtrate: 8.0 m 3 / d. DMAC concentration in the filtrate was 0.0002% by mass, TOC was 1.1 mg / L.
Discharge of concentrated water: 0.5 m 3 / d. DMAC concentration in concentrated water 0.06 mass%, TOC 550 mg / L.
Membrane area of reverse osmosis filtration membrane: 47 m 2 (RO membrane module of membrane area 7.9 m 2 x 6 units).
Reverse osmosis filtration membrane: Low-pressure spiral type reverse osmosis membrane element (“ESPA2-4040” manufactured by Nitto Denko Corporation).
The filtrate was reused as a cleaning liquid in the manufacturing process. The concentrated water was returned to the raw water tank 41.

上記のとおり、本発明を適用することで、製造工程から排出される工程廃水の排出量と、その処理量とのバランスに優れる処理方法及び処理システムを構築できた。また、MBR工程において活性汚泥槽を大きく形成しなくて済み、処理システムをコンパクトに構築できた。さらに、ろ過分離工程の前に、蒸発分離工程及び膜分離活性汚泥処理工程が行われることで、DMAC濃度が低減された処理水に対してろ過分離工程が行われたため、ろ過装置31の逆浸透膜の目詰まりや、逆浸透膜の溶解等による破損が生じなかった。さらに、ろ過分離工程から得られるろ液は水質に優れており、製造工程中の工程水(例えば、洗浄液)として再利用できた。これにより、外部に廃水が排出されない(ZLD:ゼロリキッドディスチャージ)処理方法及び処理システムを構築できた。   As described above, by applying the present invention, it is possible to construct a treatment method and a treatment system having an excellent balance between the discharge amount of process wastewater discharged from the manufacturing process and the treated amount thereof. Further, it was not necessary to form a large activated sludge tank in the MBR process, and the treatment system could be constructed compactly. Further, the evaporative separation step and the membrane separation activated sludge treatment step are performed before the filtration separation step, and thus the filtration separation step is performed on the treated water having a reduced DMAC concentration, so that the reverse osmosis of the filtration device 31 is performed. No membrane clogging or damage due to dissolution of the reverse osmosis membrane occurred. Furthermore, the filtrate obtained from the filtration and separation step has excellent water quality and can be reused as process water (for example, cleaning liquid) in the manufacturing process. As a result, it was possible to construct a treatment method and a treatment system in which wastewater was not discharged outside (ZLD: zero liquid discharge).

1〜3 処理システム
10 蒸発分離装置
11 蒸発分離器
20 膜分離活性汚泥処理装置
21 活性汚泥槽
22 散気管
25 分離膜モジュール
30 ろ過分離装置
31 ろ過装置
1-3 Treatment system 10 Evaporative separator 11 Evaporative separator 20 Membrane separation activated sludge treatment device 21 Activated sludge tank 22 Air diffuser 25 Separation membrane module 30 Filtration separation device 31 Filtration device

Claims (14)

有機物を含む廃水を、
蒸発濃縮処理又は蒸留処理し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する蒸発分離工程と、
前記溶液Bを、膜分離活性汚泥処理法により処理して処理水を得る膜分離活性汚泥処理工程とを含み、
前記有機物を含む廃水に含まれる有機物が、N,N−ジメチルアセトアミド、N−メチル−2−ピロリドン及びN,N−ジメチルホルムアミドから選ばれる1種以上の化合物を含むことを特徴とする、有機物を含む廃水の処理方法。
Wastewater containing organic matter,
An evaporative separation step of performing an evaporative concentration treatment or a distillation treatment to separate the solution A in which the organic matter is concentrated and the solution B in which the concentration of the organic matter is reduced;
Said solution B, seen including a membrane separation activated sludge treatment process to obtain a treated water treated by the membrane separation activated sludge treatment method,
Organic substances contained in the waste water containing the organic substance, is N, N- dimethylacetamide, N- methyl-2-pyrrolidone and N, wherein including Mukoto one or more compounds selected from N- dimethylformamide, organic Wastewater treatment method including.
常圧下での沸点が100℃以上である有機物を含む廃水を、
蒸発濃縮処理し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する蒸発分離工程と、
前記溶液Bを、膜分離活性汚泥処理法により処理して処理水を得る膜分離活性汚泥処理工程とを含み、
前記有機物を含む廃水に含まれる有機物が、N,N−ジメチルアセトアミド、N−メチル−2−ピロリドン及びN,N−ジメチルホルムアミドから選ばれる1種以上の化合物を含むことを特徴とする、有機物を含む廃水の処理方法。
Waste water containing organic matter having a boiling point of 100 ° C. or higher under normal pressure,
An evaporative separation step of performing evaporative concentration treatment to separate the solution A in which the organic matter is concentrated and the solution B in which the concentration of the organic matter is reduced;
Said solution B, seen including a membrane separation activated sludge treatment process to obtain a treated water treated by the membrane separation activated sludge treatment method,
Organic substances contained in the waste water containing the organic substance, is N, N- dimethylacetamide, N- methyl-2-pyrrolidone and N, wherein including Mukoto one or more compounds selected from N- dimethylformamide, organic Wastewater treatment method including.
常圧下での沸点が100℃未満である有機物を含む廃水を、
蒸留処理し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する蒸発分離工程と、
前記溶液Bを、膜分離活性汚泥処理法により処理して処理水を得る膜分離活性汚泥処理工程とを含み、
前記有機物を含む廃水に含まれる有機物が、N,N−ジメチルアセトアミド、N−メチル−2−ピロリドン及びN,N−ジメチルホルムアミドから選ばれる1種以上の化合物を含むことを特徴とする、有機物を含む廃水の処理方法。
Wastewater containing organic matter having a boiling point under atmospheric pressure of less than 100 ° C.,
An evaporation separation step of performing a distillation process to separate the solution A in which the organic matter is concentrated and the solution B in which the concentration of the organic matter is reduced;
Said solution B, seen including a membrane separation activated sludge treatment process to obtain a treated water treated by the membrane separation activated sludge treatment method,
Organic substances contained in the waste water containing the organic substance, is N, N- dimethylacetamide, N- methyl-2-pyrrolidone and N, wherein including Mukoto one or more compounds selected from N- dimethylformamide, organic Wastewater treatment method including.
前記処理水を再利用することを特徴とする、請求項1〜3のいずれか一項に記載の有機物を含む廃水の処理方法。   The method for treating wastewater containing organic matter according to claim 1, wherein the treated water is reused. さらに、前記処理水を、逆浸透膜又はナノろ過膜によってろ過処理し、前記逆浸透膜又はナノろ過膜を透過したろ液と、逆浸透膜又はナノろ過膜を透過しない濃縮水とに分離するろ過分離工程を含むことを特徴とする、請求項1〜3のいずれか一項に記載の有機物を含む廃水の処理方法。   Further, the treated water is filtered by a reverse osmosis membrane or a nanofiltration membrane, and separated into a filtrate that has passed through the reverse osmosis membrane or the nanofiltration membrane and concentrated water that does not pass through the reverse osmosis membrane or the nanofiltration membrane. The method for treating wastewater containing organic matter according to any one of claims 1 to 3, comprising a filtration separation step. 前記ろ液を再利用することを特徴とする、請求項5に記載の有機物を含む廃水の処理方法。   The method for treating wastewater containing organic matter according to claim 5, wherein the filtrate is reused. さらに、前記濃縮水を、前記の蒸発分離工程に返送することを特徴とする、請求項5又は請求項6に記載の有機物を含む廃水の処理方法。   Furthermore, the concentrated water is returned to the said evaporation separation process, The processing method of the waste water containing the organic substance of Claim 5 or Claim 6 characterized by the above-mentioned. 前記有機物を含む廃水の全有機炭素(TOC)濃度が、2,000〜50,000mg/Lであることを特徴とする、請求項1〜7のいずれか一項に記載の有機物を含む廃水の処理方法。   The total organic carbon (TOC) concentration of the wastewater containing organic matter is 2,000 to 50,000 mg / L, and the wastewater containing organic matter according to any one of claims 1 to 7. Processing method. 有機物を含む廃水を、蒸発濃縮処理又は蒸留処理し、前記有機物が濃縮された溶液Aと、前記有機物の濃度が低減された溶液Bとに分離する蒸発分離装置と、
前記溶液Bを、膜分離活性汚泥処理法により処理して処理水を得る膜分離活性汚泥処理装置とを備え
前記有機物を含む廃水に含まれる有機物が、N,N−ジメチルアセトアミド、N−メチル−2−ピロリドン及びN,N−ジメチルホルムアミドから選ばれる1種以上の化合物を含むことを特徴とする、有機物を含む廃水の処理システム。
An evaporative separation device that evaporatively concentrates or distills wastewater containing organic matter to separate it into a solution A in which the organic matter is concentrated and a solution B in which the concentration of the organic matter is reduced,
A membrane separation activated sludge treatment device for treating the solution B by a membrane separation activated sludge treatment method to obtain treated water ,
The organic matter contained in the wastewater containing the organic matter contains one or more compounds selected from N, N-dimethylacetamide, N-methyl-2-pyrrolidone and N, N-dimethylformamide , Wastewater treatment system including.
前記処理水を再利用するための処理水流路を備えることを特徴とする、請求項に記載の有機物を含む廃水の処理システム。 The treatment system for wastewater containing organic matter according to claim 9 , further comprising a treated water channel for reusing the treated water. さらに、前記処理水を、逆浸透膜又はナノろ過膜によってろ過処理し、前記逆浸透膜又はナノろ過膜を透過したろ液と、逆浸透膜又はナノろ過膜を透過しない濃縮水とに分離するろ過分離装置を備えることを特徴とする、請求項に記載の有機物を含む廃水の処理システム。 Further, the treated water is filtered by a reverse osmosis membrane or a nanofiltration membrane, and separated into a filtrate that has passed through the reverse osmosis membrane or the nanofiltration membrane and concentrated water that does not pass through the reverse osmosis membrane or the nanofiltration membrane. The wastewater treatment system containing organic matter according to claim 9 , further comprising a filtration separation device. 前記ろ液を再利用するためのろ液流路を備えることを特徴とする、請求項11に記載の有機物を含む廃水の処理システム。 The treatment system for wastewater containing organic matter according to claim 11 , further comprising a filtrate flow path for reusing the filtrate. さらに、前記濃縮水を、前記の蒸発分離装置に返送するための濃縮水返送路を備えることを特徴とする、請求項11又は請求項12に記載の有機物を含む廃水の処理システム。 The treatment system for wastewater containing organic matter according to claim 11 or 12 , further comprising a concentrated water return path for returning the concentrated water to the evaporation / separation device. 前記有機物を含む廃水の全有機炭素(TOC)濃度が、2,000〜50,000mg/Lであることを特徴とする、請求項13のいずれか一項に記載の有機物を含む廃水の処理システム。 The total organic carbon (TOC) concentration of the wastewater containing the organic matter is 2,000 to 50,000 mg / L, and the wastewater containing the organic matter according to any one of claims 9 to 13 . Processing system.
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