JP5270247B2 - Wastewater treatment facility at food processing plant - Google Patents

Wastewater treatment facility at food processing plant Download PDF

Info

Publication number
JP5270247B2
JP5270247B2 JP2008196473A JP2008196473A JP5270247B2 JP 5270247 B2 JP5270247 B2 JP 5270247B2 JP 2008196473 A JP2008196473 A JP 2008196473A JP 2008196473 A JP2008196473 A JP 2008196473A JP 5270247 B2 JP5270247 B2 JP 5270247B2
Authority
JP
Japan
Prior art keywords
water
tank
oil
scum
wastewater treatment
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.)
Active
Application number
JP2008196473A
Other languages
Japanese (ja)
Other versions
JP2010029813A (en
Inventor
裕治 金子
祐介 酒井
香織 三谷
Original Assignee
日本建鐵環境エンジニアリング株式会社
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by 日本建鐵環境エンジニアリング株式会社 filed Critical 日本建鐵環境エンジニアリング株式会社
Priority to JP2008196473A priority Critical patent/JP5270247B2/en
Publication of JP2010029813A publication Critical patent/JP2010029813A/en
Application granted granted Critical
Publication of JP5270247B2 publication Critical patent/JP5270247B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • 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

Landscapes

  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Physical Water Treatments (AREA)
  • Removal Of Floating Material (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a wastewater treatment equipment having a separation tank capable of efficiently removing an oil component and water-insoluble substance or the like in wastewater as oil-containing scum without excessively adding pressure water to wastewater and having a simple tank structure. <P>SOLUTION: The wastewater treatment equipment is constituted so that a vicinity of a treated water takeout port carries a scum feed-out means for scooping up the oil-containing scum to feed it out and a vertical partition plate changing the flow direction of treated water which undergoes the flocculation treatment of the oil component and the water-insoluble substance and includes an opening end part for forming a bent water passage in the separation tank, thereby keeping a bent water passage, through which the treated water subjected to the flocculation treatment of the oil component with the water-insoluble substance flows toward the treated water takeout port, demarcated up to the vicinity of the treated water takeout port from a communication port by the partition plate. <P>COPYRIGHT: (C)2010,JPO&amp;INPIT

Description

本発明は、排水中の油分および非水溶性物質(浮遊懸濁物質:大きさが概略2m以下)などを、含油スカムとして効率的に除去することができる排水処理設備にかかり、特に油分および非水溶性物質を多く含む含油有機性排水の前処理装置として好適な食品加工工場排水処理設備に関する。
The present invention, oil in the waste water and the water-insoluble substance: the (floating suspended solids less schematic 2 m m size), etc., relates to a wastewater treatment facility which can be efficiently removed as oil-containing scum, particularly oil The present invention also relates to a wastewater treatment facility suitable for a food processing plant as a pretreatment device for oil-containing organic wastewater containing a large amount of water-insoluble substances.

従来から、有機性排水の水処理を、微生物担体を用いて行うことが知られている。たとえば家庭雑排水、農業集落排水、産業排水などの有機性排水は、貯留槽で負荷変動を吸収した後、微生物担体を用いた排水処理設備で水処理することが可能となっている(特許文献1)。
図5(a)、(b)には、特許文献1に記載の微生物担体槽を用いた排水処理設備を示した。図5(a)を用いて有機性排水の水処理フローについて説明しておく。
Conventionally, it is known that water treatment of organic wastewater is performed using a microbial carrier. For example, organic wastewater such as household wastewater, agricultural settlement wastewater, and industrial wastewater can be treated with wastewater treatment facilities using microbial carriers after absorbing load fluctuations in the storage tank (Patent Literature). 1).
FIGS. 5A and 5B show a wastewater treatment facility using the microorganism carrier tank described in Patent Document 1. FIG. The water treatment flow of organic waste water will be described with reference to FIG.

排出された有機性排水は、貯留槽30に一旦受入れて負荷変動を吸収し、その後脱窒槽40、硝化槽50からなる処理槽に送られる。脱窒槽40では嫌気条件下として脱窒処理を行い、硝化槽50では好気条件下としてBOD(Biochemical Oxygen Demand)成分の分解処理とアンモニア性窒素の硝化処理を行う。この硝化槽50内の底部に設けた散気装置34は、微生物による生物学的処理に必要な酸素を供給する手段である。脱窒槽40及び/又は硝化槽50に微生物担体(図示せず)が充填されている。   The discharged organic waste water is once received in the storage tank 30 to absorb the load fluctuation, and then sent to the treatment tank composed of the denitrification tank 40 and the nitrification tank 50. The denitrification tank 40 performs a denitrification process under anaerobic conditions, and the nitrification tank 50 performs a decomposition process of BOD (Biochemical Oxygen Demand) components and a nitrification process of ammonia nitrogen under aerobic conditions. The air diffuser 34 provided at the bottom of the nitrification tank 50 is a means for supplying oxygen necessary for biological treatment by microorganisms. The denitrification tank 40 and / or the nitrification tank 50 is filled with a microorganism carrier (not shown).

このように、有機性排水に脱窒処理と硝化処理を施した後、沈殿槽60で汚泥を沈降分離して処理水とする。処理水は下水道放流される。
なお、図5(b)には、脱窒槽40内の微生物担体31を、その底部に設けた攪拌装置33で流動させ、また、硝化槽50から送られる循環液で流動させるようにした排水処理設備を示した。図中、スクリーン32は大きな油分および非水溶性物質を除去する手段であり、スクリーン35は、微生物担体32が流れによって流れ出るのを防止する手段である。
As described above, after denitrification treatment and nitrification treatment are performed on the organic waste water, the sludge is settled and separated in the settling tank 60 to obtain treated water. The treated water is discharged into the sewer.
In FIG. 5B, the microbial carrier 31 in the denitrification tank 40 is made to flow with the stirring device 33 provided at the bottom thereof, and is also made to flow with the circulating liquid sent from the nitrification tank 50. The equipment was shown. In the figure, the screen 32 is a means for removing large oil and water-insoluble substances, and the screen 35 is a means for preventing the microbial carrier 32 from flowing out by the flow.

しかし、油分を多く含む含油有機性排水を前処理せず、上記した排水処理設備で水処理した場合、排水中の油分が微生物担体に付着してしまい、微生物による生物的処理が著しく阻害されてしまうという、問題が生じる。このため、排水中の油分を含油スカムとして効率的に分離・除去しておく前処理装置が必要となる。
たとえば、排水中の油分および非水溶性物質などに、微細な気泡を付着させ、含油スカムとして除去可能な加圧浮上分離装置が知られている(非特許文献1、2、3)。加圧浮上分離装置70の一例の構造を図7(a)に、その装置における排水流入部71での作用を図7(b)に示した。図7(a)で76は排水取入口、77は加圧水取入口である。
However, if oil-containing organic wastewater containing a large amount of oil is not pretreated and treated with the above-described wastewater treatment equipment, the oil in the wastewater adheres to the microorganism carrier, and biological treatment by microorganisms is significantly hindered. The problem arises. For this reason, the pre-processing apparatus which isolate | separates and removes the oil content in waste_water | drain as oil-impregnated scum efficiently is needed.
For example, a pressurized flotation separation device is known that allows fine bubbles to adhere to oil and water-insoluble substances in waste water and remove them as oil-containing scum (Non-Patent Documents 1, 2, and 3). FIG. 7A shows an example of the structure of the pressure levitation separator 70, and FIG. 7B shows the operation at the drainage inlet 71 in the apparatus. In FIG. 7A, 76 is a drainage inlet, and 77 is a pressurized water inlet.

また、水中油滴型エマルジョンとして油分を高濃度で含む排水中から、含油スカムとして油分を除去する排水処理設備が提案されている(特許文献2)。この特許文献2に記載の排水処理設備は、図6の水処理フローに示したように、異なる高分子凝集剤を使用する一次および二次凝集反応槽と、加圧浮上分離槽を具備している。
特許第3730367号 特開2005-246219号公報 栗田工業著、「よくわかる水処理技術」、日本実業出版社、2006年6月発行、p78〜79 井出哲夫著、「水処理工学(理論と応用)」、技報堂出版株式会社、1976年6月発行、p86〜91 (社)産業環境管理協会編、「新・公害防止の技術と法規」、丸善株式会社、2006年1月発行、p216〜227
Also, a wastewater treatment facility has been proposed that removes oil as oil-containing scum from wastewater containing oil at a high concentration as an oil-in-water emulsion (Patent Document 2). As shown in the water treatment flow of FIG. 6, the wastewater treatment facility described in Patent Document 2 includes primary and secondary flocculation reaction tanks using different polymer flocculants, and a pressurized flotation separation tank. Yes.
Patent No. 3730367 JP 2005-246219 A Kurita Kogyo, "A well-understood water treatment technology", published by Nihon Jitsugyo Publishing Co., Ltd., June 2006, p78-79 Ide Tetsuo, "Water Treatment Engineering (Theory and Application)", Gihodo Publishing Co., Ltd., June 1976, p86-91 (Environmental Environmental Management Association), “New Pollution Prevention Technology and Regulations”, Maruzen Co., Ltd., January 2006, p.

凝集反応槽で使用する凝集剤には、無機凝集剤、カチオン系高分子凝集剤、アニオン系高分子凝集剤などがある。通常はこのうちの2種類の凝集剤を用い、2段階で凝集処理を行うことにより、排水中の油分および非水溶性物質を含油スカムとして除去することが行われている。
たとえば特許文献2の場合、1次凝集処理にカチオン系高分子凝集剤、2次凝集処理にアニオン系高分子凝集剤を使用し、非特許文献3の水処理技術においては、1次凝集処理に無機凝集剤、2次凝集処理にアニオン系高分子凝集剤を使用している。このように異なる種類の凝集剤を用い、2段階で凝集処理を行うのは、1次凝集反応によって小さなフロックを形成し、2次凝集反応によってそれを粗大化させ、少ない凝集剤量で大きなフロックを形成するためである。この1次凝集反応では、大きさが概略2m以下である油分および非水溶性物質と、凝集剤とを反応させて小さなフロックを形成するための凝集剤が、それに続く2次凝集処理では、大きなフロックを形成するための凝集剤が、それぞれ排水中に添加される。
Examples of the flocculant used in the flocculation reaction tank include an inorganic flocculant, a cationic polymer flocculant, and an anionic polymer flocculant. Usually, two kinds of these flocculants are used, and the oil and water-insoluble substances in the waste water are removed as oil-impregnated scum by performing the flocculation process in two stages.
For example, in the case of Patent Document 2, a cationic polymer flocculant is used for the primary agglomeration treatment, and an anionic polymer flocculant is used for the secondary agglomeration treatment. An anionic polymer flocculant is used for the inorganic flocculant and the secondary flocculant treatment. Using different types of flocculants in this way, agglomeration treatment is performed in two stages by forming a small floc by the primary agglomeration reaction, coarsening it by the secondary agglomeration reaction, and a large floc with a small amount of flocculant It is for forming. In this primary agglomeration reaction, a flocculant for reacting an oil component and a water-insoluble substance having a size of approximately 2 mm or less with a flocculant to form a small floc is formed in the subsequent secondary agglomeration treatment. A flocculant for forming large flocs is added to the drainage respectively.

このように2段階で凝集処理を行う排水処理設備の問題点を以下に列挙する。
(1)公共水域や下水道放流ができる程度の処理水(清澄液)あるいは後段の生物的処理が著しく阻害されない程度まで油分を除去するためには、構造が複雑である加圧浮上分離槽で油分を除去する必要がある(図7(a)参照)。
(2)2段階で凝集処理を行うため、1次凝集反応と2次凝集反応の2回に分けて凝集剤を添加する必要がある。
(3)特許文献2に記載の排水処理設備では、異なる高分子凝集剤を添加する一次および二次凝集反応槽と、加圧浮上分離槽が必要なうえ、図示しないが、凝集反応槽で添加した凝集剤と、油分および非水溶性物質とを反応させて生成されるフロックを、含油スカムとして浮上・分離するスカム浮上分離槽の槽構造が複雑となる。
(4)図7(a)に示した加圧浮上分離装置70を、微生物担体槽を具備する排水処理設備の前処理装置として用いた場合、加圧水が排水に余分に加わるため、生物的処理を行う水処理量が増える。
The problems of the wastewater treatment facility that performs the agglomeration treatment in two stages are listed below.
(1) In order to remove the oil to the extent that the treated water (clarified liquid) that can be discharged into public water areas and sewers or the biological treatment in the subsequent stage is not significantly hindered, the oil content is reduced in a pressurized flotation tank with a complicated structure. Must be removed (see FIG. 7A).
(2) Since the aggregation treatment is performed in two stages, it is necessary to add the aggregating agent in two steps of the primary aggregation reaction and the secondary aggregation reaction.
(3) In the wastewater treatment facility described in Patent Document 2, primary and secondary agglomeration reaction tanks to which different polymer flocculants are added and a pressurized flotation separation tank are required, and although not shown, they are added in the agglomeration reaction tank The tank structure of the scum flotation separation tank that floats and separates the floc produced by reacting the flocculant, oil, and water-insoluble substance as oil-containing scum becomes complicated.
(4) When the pressurized flotation separation device 70 shown in FIG. 7 (a) is used as a pretreatment device for a wastewater treatment facility equipped with a microorganism carrier tank, pressurized water is added to the wastewater, so that biological treatment is performed. Increased water treatment volume.

図7(a)、(b)を用い、加圧浮上分離装置70の槽構造と、排水中の油分・非水溶性物質80などを含油スカムとして浮上・分離する作用について説明しておく。
排水中の非水溶性物質に気泡を付着させる排水流入部71が、槽内の中央に配置されており、槽上部に浮上した含油スカムを集める手段であるスキマの刃72を回転させる駆動装置が配置されてなる。
7 (a) and 7 (b), the tank structure of the pressurized flotation separation device 70 and the action of flotation / separation using oil-containing / water-insoluble substances 80 in the drainage as oil-impregnated scum will be described.
A drainage inflow part 71 for attaching air bubbles to water-insoluble substances in the drainage is disposed in the center of the tank, and a driving device that rotates a skimmer blade 72 that is a means for collecting the oil-impregnated scum that floats above the tank It is arranged.

さらに分離槽の槽内には、傾斜板73で仕切られた含油スカムが落とされる空間(槽内の右上部)が形成され、排水中の油分・非水溶性物質80などが含油スカムとして除去された後の処理水を集める集水室74が、槽底部の周囲に形成されている。
排水流入部71内で、噴出された加圧水から生じた微細な気泡81に油分80を付着させる。同様に、非水溶性物質80を微細な気泡81に付着させる。次いで、槽内中央部の矢印で示したような上昇流れに乗せて、排水中の油分・非水溶性物質80などを含油スカムとして浮上させる。分離槽の槽内周辺では、矢印で示したような下降流れが生じる。そして、槽底部の周囲の集水室74で集めた処理水が、処理水取出口75を経て取り出される。
Furthermore, in the tank of the separation tank, a space (upper right part in the tank) where the oil-impregnated scum partitioned by the inclined plate 73 is dropped is formed, and oil and water-insoluble substances 80 in the drainage are removed as oil-impregnated scum. A water collection chamber 74 for collecting the treated water after this is formed around the bottom of the tank.
In the drainage inflow portion 71, the oil 80 is adhered to the fine bubbles 81 generated from the jetted pressurized water. Similarly, the water-insoluble substance 80 is attached to the fine bubbles 81. Next, the oil component / water-insoluble substance 80 in the drainage is floated as an oil-impregnated scum on an upward flow as indicated by an arrow in the center of the tank. A downward flow as indicated by an arrow occurs around the inside of the separation tank. Then, the treated water collected in the water collecting chamber 74 around the tank bottom is taken out via the treated water outlet 75.

本発明は、上記従来技術の問題点に鑑み、加圧水を排水に余分に加えず、排水中の油分および非水溶性物質などを、含油スカムとして効率的に除去することができかつ槽構造がシンプルである分離槽を有する食品加工工場排水処理設備を提供することを第1の目的とする。
また、油分および非水溶性物質を多く含む含油有機性排水の前処理装置として好適な食品加工工場排水処理設備を提供することを第2の目的とする。
In view of the above-mentioned problems of the prior art, the present invention can efficiently remove oil and water-insoluble substances in the drainage as oil-impregnated scum without adding pressurized water to the drainage and has a simple tank structure. It is the first object to provide a food processing factory wastewater treatment facility having a separation tank.
A second object is to provide a food processing factory wastewater treatment facility suitable as a pretreatment device for oil-containing organic wastewater containing a large amount of oil and water-insoluble substances.

さらに、従来技術においては槽構造が複雑であるがゆえに、設備にかかるイニシャルコストおよび薬剤や電気代などのランニングコストが高くなるため、水処理コストを低減することを第3の目的とする。   Furthermore, since the tank structure is complicated in the prior art, the initial cost for the equipment and the running cost for chemicals, electricity bills, and the like are high, so the third object is to reduce the water treatment cost.

本発明者等は、排水中の油分および非水溶性物質を、含油スカムとして効率的に除去する排水処理設備について鋭意検討した結果、特許文献2に記載のように、高分子凝集剤を用いて油分の凝集処理を行った後、含油スカムとして排水中の油分および非水溶性物質を浮上・分離する分離処理を行うのが効率的であること、分離槽の槽内に平面で見て、処理水取出口に向かって油分および非水溶性物質の凝集処理を行った処理水が流れる折れ曲がった水路を形成することで、上記課題を解決できることを見出し、この知見に基づいて本発明をなすに至った。   As a result of intensive studies on wastewater treatment equipment that efficiently removes oil and water-insoluble substances in wastewater as oil-containing scum, the present inventors have used a polymer flocculant as described in Patent Document 2. After the oil is agglomerated, it is efficient to separate and separate the oil and water-insoluble substances in the wastewater as oil-impregnated scum. It was found that the above problem can be solved by forming a bent water channel through which treated water that has been subjected to agglomeration treatment of oil and water-insoluble substances toward the water outlet, and the present invention has been made based on this finding. It was.

すなわち本発明は、以下のとおりである。
請求項1 槽内に攪拌装置を有し、油分および非水溶性物質を含む排水を排水取入口から取り入れるとともに、高分子凝集剤添加手段により添加される高分子凝集剤と排水中の油分および非水溶性物資とを反応させて凝集処理を行う凝集槽と、該凝集槽に連絡口で連通され、前記凝集処理で形成されるフロックを含油スカムとして浮上・分離する分離処理を行うとともに、排水中の油分および非水溶性物質を含油スカムとして除去した後の処理水のみを処理水取出口から取り出す分離槽を有する食品加工工場排水処理設備であって、
前記処理水取出口近傍に、前記含油スカムを掬い上げて搬出するスカム搬出手段と、前記分離槽の槽内に、油分および非水溶性物質の凝集処理を施した処理水の流れ方向を変え前記分離槽の底面に平行な面内で曲がった水路とする開口端部をもつ垂直な仕切り板とを有し、該仕切り板によって前記連絡口から前記処理水取出口近傍までの間に、前記処理水取出口に向かって油分および非水溶性物質の凝集処理を施した処理水が流れる前記分離槽の底面に平行な面内で曲がった水路が形成されてなり、前記連絡口および前記処理水取出口が機械的移送手段として、ヘッド差を利用したオーバーフロー堰で形成され、前記スカム搬出手段は、長い布状のフィルタと前記フィルタを繰り返し回動させる回動手段とで構成し、前記分離槽には、曲がった水路のコーナー部に相当する、前記含油スカムが局部的に溜まる箇所の槽内底部に、空気を噴出するエアーレーション装置を設置し、曝気ブロワと接続してなることを特徴とする食品加工工場排水処理設備。
請求項 前記凝集槽の槽内に設ける攪拌装置は、空気を噴出するエアーレーション装置とし、該エアーレーション装置を槽内底部に設けて曝気ブロワと接続してなることを特徴とする請求項1に記載の食品加工工場排水処理設備。
請求項 前記エアーレーション装置の運転を、間欠的に行うように構成してなることを特徴とする請求項又はに記載の食品加工工場排水処理設備。
請求項 前記高分子凝集剤添加手段は、添加量を調節可能とすることを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。
請求項 前記高分子凝集剤添加手段は、形成されるフロックの状態に基づいて添加量・濃度を設定することを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。
請求項 前記高分子凝集剤添加手段は、添加口が、前記槽の上部または底部の複数箇所配置されるとともに、各々の添加量を個別に設定することを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。
請求項 前記高分子凝集剤添加手段は、凝集剤貯留槽と配水管と定量ポンプで構成することを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。
請求項 前記高分子凝集剤添加手段は、凝集剤貯留槽と配水管と定量ポンプと電動弁で構成することを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。
請求項 生物担体槽を具備する排水処理設備の前処理装置として用いることを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。
That is, the present invention is as follows.
[Claim 1] Having a stirrer in the tank and taking in wastewater containing oil and water-insoluble substances from the drainage inlet, the polymer flocculant added by the polymer flocculant adding means, A flocculation tank that reacts with water-soluble materials to perform a flocculation process, and a separation process that floats and separates the floc formed by the flocculation process as an oil-impregnated scum that communicates with the flocculation tank through a communication port, A food processing factory wastewater treatment facility having a separation tank for removing only treated water after removing the oil and water-insoluble substances as oil-containing scum from the treated water outlet,
The process water taking near the outlet, a scum discharge means for unloaded scooped the oil-impregnated scum, said in a bath of the separation tank, the change of oil and the flow direction of the treated water subjected to coagulation treatment of water-insoluble material A vertical partition plate having an open end that is a water channel bent in a plane parallel to the bottom surface of the separation tank, and the treatment is performed between the communication port and the vicinity of the treated water outlet by the partition plate. water taking Ri Na and waterways bent in a plane parallel to the bottom of the separation tank the process water flows subjected to coagulation treatment of oil and water-insoluble substance is formed toward the exit, the communication ports and the treated water The take-out port is formed by an overflow weir utilizing a head difference as a mechanical transfer means, and the scum carry-out means is constituted by a long cloth filter and a rotation means for repeatedly rotating the filter, and the separation tank Is bent Corresponding to the corner portions of the waterway, the tank bottom inside of a portion the oil-containing scum accumulates locally, established the aeration device for ejecting air, food processing plants wastewater characterized by being connected to the aeration blower Processing equipment.
Stirrer provided in claim 2 wherein the coagulation tank in the tank, the aeration device for injecting air according to claim 1, characterized by being connected to the aeration blower is provided the aeration device in Tank bottom food processing plant waste water treatment plant according to.
The operation of claim 3 wherein the aeration device, food processing plant wastewater treatment facility of claim 1 or 2, characterized by being configured to intermittently performed.
[ 4] The food processing factory wastewater treatment facility according to any one of [1] to [ 3] , wherein the polymer flocculant addition means is capable of adjusting the addition amount.
Claim 5 wherein the polymeric flocculant means, food processing plants wastewater according to any one of claims 1 to 4, characterized in that for setting the amount and density based on the state of the flocs formed Processing equipment.
Claim 6, wherein the polymeric flocculant means addition port, along with the plurality of locations located on either the top or the bottom of the tank, according to claim 1 to 5, characterized in that setting the amount of addition of each individual The wastewater treatment facility of any one of the food processing factories .
7. The polymeric flocculant means, food processing plant wastewater treatment facility according to any one of claims 1 to 6, characterized in that consist of water pipe and a metering pump and flocculant reservoir.
8. The polymeric flocculant means, food processing plants wastewater according to any one of claims 1 to 7, characterized in that configured in coagulant reservoir and distribution pipes and the metering pump and the electric valve Processing equipment.
Food processing plants wastewater treatment facilities according to any one of claims 1-8, characterized by using as a wastewater treatment facility before processing apparatus comprising according to claim 9 microbial carrier vessel.

本発明によれば、排水中の油分および非水溶性物質を含油スカムとして効率的に除去することができる、分離槽の槽構造がシンプルである食品加工工場排水処理設備を提供することができる。また、この排水処理設備は、加圧水を加えず、排水中の油分および非水溶性物質を効率的に除去することができるため、微生物担体槽を具備する排水処理設備の前処理装置として好適に用いることができる。また、槽構造がシンプルな分離槽を有するため、水処理コストの低減が可能となる。
ADVANTAGE OF THE INVENTION According to this invention, the food processing factory waste water treatment facility with the simple tank structure of a separation tank which can remove efficiently the oil content and water-insoluble substance in waste_water | drain as oil-containing scum can be provided. In addition, since this wastewater treatment facility can efficiently remove oil and water-insoluble substances in the wastewater without adding pressurized water, it is suitably used as a pretreatment device for wastewater treatment facilities having a microorganism carrier tank. be able to. Moreover, since the tank structure has a simple separation tank, the water treatment cost can be reduced.

以下、本発明について図を用い説明する。
図1は、図2に示した排水処理設備を、微生物担体槽を具備する排水処理設備の前処理装置とする場合の全体構成図である。図2は、本発明の実施の形態にかかる排水処理設備の要部を示す横断面図、図3は、排水中の油分および非水溶性物質を含油スカムとして除去した後の処理水のみを取り出す処理水取出口9近傍を示す縦断面図である。
The present invention will be described below with reference to the drawings.
FIG. 1 is an overall configuration diagram when the wastewater treatment facility shown in FIG. 2 is used as a pretreatment device for a wastewater treatment facility including a microorganism carrier tank. FIG. 2 is a cross-sectional view showing a main part of the wastewater treatment facility according to the embodiment of the present invention, and FIG. 3 takes out only treated water after removing oil and water-insoluble substances in the wastewater as oil-containing scum. It is a longitudinal cross-sectional view which shows the treated water extraction exit 9 vicinity.

図1中、11は大きい油分および非水溶性物質、すなわち大きさが概略2mを超える物質を除去する公知のスクリーンを示す。たとえば食品加工工場からは、肉片、骨片、脂肪分などの物質を含む排水が排出され、このうち大きさが大きいものは公知のスクリーン11で効率的に除去することができるが、大きさが概略2mm以下の肉片、骨片、脂肪分などは、排水中に浮遊しているため、公知のスクリーン11で除去することが困難である。 In FIG. 1, 11 indicates a known screen for removing large oils and water-insoluble substances, ie substances having a size exceeding approximately 2 mm . For example, a wastewater containing substances such as meat pieces, bone pieces, and fats is discharged from a food processing factory. Of these, large ones can be efficiently removed with the known screen 11, but the size is small. Meat pieces, bone pieces, fats, and the like, which are approximately 2 mm or less, are floating in the drainage and are difficult to remove with the known screen 11.

そこで、本発明の実施の形態にかかる排水処理設備は、図1、図2に示したように、槽内に攪拌装置3を有し、油分および非水溶性物質を含む排水を排水取入口7から取り入れるとともに、高分子凝集剤添加手段(単に凝集剤添加手段ともいう)により添加される高分子凝集剤と排水中の油分および非水溶性物質とを反応させて凝集処理を行う凝集槽1と、凝集槽1に連絡口8で連通され、凝集槽1の凝集処理で形成されるフロックを含油スカムとして浮上・分離する分離処理を行う分離槽2を有する。   Therefore, the wastewater treatment facility according to the embodiment of the present invention has a stirrer 3 in the tank as shown in FIGS. 1 and 2, and discharges wastewater containing oil and water-insoluble substances into the drainage inlet 7. A flocculation tank 1 for performing a flocculation treatment by reacting a polymer flocculating agent added by means of a polymer flocculating agent addition means (also simply referred to as a flocculating agent addition means), an oil in waste water, and a water-insoluble substance. The separation tank 2 communicates with the agglomeration tank 1 through the communication port 8 and performs a separation process for floating and separating the floc formed by the agglomeration process of the aggregation tank 1 as an oil-impregnated scum.

この分離槽2の処理水取出口9近傍には、スカム搬出手段4が配置されている。これらの処理槽の他、凝集剤貯留槽12、排水貯留槽16、処理水貯留槽17、流量調整用槽18が配置されている(図1参照)。
まず、凝集槽1内で油分および非水溶性物質の凝集処理を行う高分子凝集剤について説明する。なお、凝集剤貯留槽12に貯留されている高分子凝集剤は、配管26と定量ポンプ27と電動弁12a、12b、12c、12dとで構成される高分子凝集剤添加手段で凝集槽1内および分離槽2内へ添加するのが好適である。
A scum carry-out means 4 is arranged in the vicinity of the treated water outlet 9 of the separation tank 2. In addition to these treatment tanks, a flocculant storage tank 12, a drainage storage tank 16, a treated water storage tank 17, and a flow rate adjusting tank 18 are arranged (see FIG. 1).
First, the polymer flocculant which performs the agglomeration treatment of oil and water-insoluble substances in the agglomeration tank 1 will be described. The polymer flocculant stored in the flocculant storage tank 12 is stored in the flocculant tank 1 by means of a polymer flocculant addition means comprising a pipe 26, a metering pump 27, and motor-operated valves 12a, 12b, 12c, 12d. It is preferable to add it into the separation tank 2.

本発明に用いる高分子凝集剤は、排水中に存在している油分および非水溶性物質と反応させて、大きいフロックを形成するために用いられる。
本発明には、このような作用をもち、長い鎖状の分子構造を有し、好ましくは分子量が300万〜800万の範囲である高分子凝集剤を用いる。このような高分子凝集剤は、大きいフロックを形成でき、含油スカムとして排水中の油分および非水溶性物質を浮上・分離する分離処理を行うのに有利である(特許文献2、非特許文献2、3参照)。
The polymer flocculant used in the present invention is used to form a large floc by reacting with oil and water-insoluble substances present in waste water.
In the present invention, a polymer flocculant having such an action, having a long chain molecular structure, and preferably having a molecular weight in the range of 3 to 8 million is used. Such a polymer flocculant is capable of forming a large floc and is advantageous for performing a separation treatment for floating and separating oil content and water-insoluble substances as waste oil scum (Patent Document 2, Non-Patent Document 2). 3).

高分子凝集剤としては、カチオン系に限定されず、排水中に含まれる油分および非水溶性物質の形態、油分および非水溶性物質の種類、油分および非水溶性物質の量などに応じて実験的に決めることができ、より好適な処理を行うためには、分子量のより大きな高分子、かつ通常の高分子凝集剤における使用濃度である0.1〜0.2%ではなく、1〜2%の濃度に調整するのが良い。   The polymer flocculant is not limited to the cationic system, and experiments are conducted according to the form of oil and water-insoluble substances contained in the waste water, the type of oil and water-insoluble substances, the amount of oil and water-insoluble substances, etc. In order to carry out a more suitable treatment, it is necessary to adjust the concentration to 1 to 2% instead of 0.1 to 0.2%, which is the concentration used in a polymer having a larger molecular weight and a normal polymer flocculant. It is good to adjust.

本発明にかかる排水処理設備では、槽内に攪拌装置3を有する凝集槽1の方で、高分子凝集剤と排水中の油分および非水溶性物質とを反応させて大きいフロックを生成した後、分離槽2で排水中の油分および非水溶性物質を含油スカムとして浮上・分離する分離処理を行う。つまり、凝集槽1では、槽内に設けた攪拌装置3によって、添加した高分子凝集剤と排水とを均一に混合し、排水中の油分および非水溶性物質と高分子凝集剤とを反応させること、さらにその反応で生成した大きいフロックに油分および非水溶性物質を取り込むために、凝集処理を施した処理水を攪拌する。   In the wastewater treatment facility according to the present invention, after the flocculant 1 having the stirring device 3 in the tank reacts with the polymer flocculant, the oil in the wastewater and the water-insoluble substance, a large floc is generated, In the separation tank 2, a separation process is performed in which the oil and water-insoluble substances in the wastewater are floated and separated as oil-containing scum. That is, in the agglomeration tank 1, the added polymer flocculant and the waste water are uniformly mixed by the stirring device 3 provided in the tank, and the oil and water-insoluble substance in the waste water react with the polymer flocculant. In addition, the treated water subjected to the agglomeration treatment is agitated in order to incorporate oil and water-insoluble substances into the large flocs produced by the reaction.

そこで、凝集槽1の槽内に設ける攪拌装置3は、上記した作用を発揮するように、空気を噴出するエアーレーション装置とし、対流を生じさせるようにエアーレーション装置を槽内底部に設け、曝気ブロワ19と接続してなるのが好ましい。
また、凝集槽1の槽内底部に、空気を噴出するエアーレーション装置を設けることによって、以下のような作用も発揮できる。この作用とは、反応で生成した大きいフロックに、油分よりも比重の大きい非水溶性物質が取り込まれると、分離槽2で含油スカムとして浮上・分離する浮上速度が遅くなるばかりでなく、排水に比べて含油スカムの比重が大きくなった場合、分離槽2で含油スカムとして浮上・分離することができなくなることを防止するという作用である。エアーレーション装置から噴出された空気を、反応で生成した大きいフロックに追加的に取り込むことで、空気が含まれない場合に比べて含油スカムの比重を小さくでき、分離槽2の槽内で含油スカムとして浮上・分離する分離処理を効率的に行える。
Therefore, the stirring device 3 provided in the tank of the coagulation tank 1 is an aeration apparatus that blows out air so as to exhibit the above-described action, and an aeration apparatus is provided at the bottom of the tank so as to generate convection. It is preferably connected to the blower 19.
In addition, by providing an aeration device for ejecting air at the bottom of the agglomeration tank 1, the following effects can be exhibited. This action means that if a water-insoluble substance with a specific gravity greater than the oil content is taken into the large flocs produced by the reaction, not only will the rising speed to float and separate as oil-impregnated scum in the separation tank 2 be reduced, but also to the drainage. In comparison, when the specific gravity of the oil-impregnated scum is increased, the separation tank 2 prevents the oil-impregnated scum from being lifted and separated as an oil-impregnated scum. By additionally taking in the air blown from the aeration device into the large flocs generated by the reaction, the specific gravity of the oil-containing scum can be reduced compared to the case where no air is contained, and the oil-containing scum in the tank of the separation tank 2 As a result, the separation process that floats and separates can be performed efficiently.

なお、高分子凝集剤と排水中の油分および非水溶性物質とを反応させて大きいフロックを生成する凝集処理は、主に槽内に攪拌装置3を有する凝集槽1で行うが、分離槽2の方でも行うことができる。分離槽2の方では、凝集槽1で添加する高分子凝集剤が少な過ぎたときの微調節を、電動弁12dを開き、配管26と定量ポンプ27を介して分離槽2内へ高分子凝集剤を添加することで行う(図2参照)。   The agglomeration treatment for producing a large floc by reacting the polymer flocculant with the oil in the waste water and the water-insoluble substance is mainly performed in the agglomeration tank 1 having the stirring device 3 in the tank, but the separation tank 2 Can also do it. In the separation tank 2, fine adjustment when the polymer flocculant added in the aggregation tank 1 is too small is performed by opening the motor-operated valve 12 d and polymer aggregation into the separation tank 2 through the pipe 26 and the metering pump 27. This is done by adding an agent (see FIG. 2).

次いで、分離槽2の槽内で排水中の油分および非水溶性物質を、含油スカムとして浮上・分離する分離処理について説明する。
油分および非水溶性物質の凝集処理を施した処理水は、連絡口8から分離槽2の槽内に流れ込む。含油スカムとして除去した後の処理水のみを取り出す処理水取出口9近傍には、スカム搬出手段4が配置されている。
Next, a description will be given of a separation process in which the oil and water-insoluble substances in the waste water are floated and separated as oil-containing scum in the tank of the separation tank 2.
The treated water subjected to the coagulation treatment of the oil and the water-insoluble substance flows into the separation tank 2 from the communication port 8. A scum discharge means 4 is disposed in the vicinity of the treated water outlet 9 for taking out only treated water after being removed as oil-impregnated scum.

ところで、油分および非水溶性物質の凝集処理を施した処理水中から、含油スカムの浮力を利用して、フロックとされた油分および非水溶性物質を浮上・分離するに要する時間は、含油スカムの浮上速度によって決まる。そこで、排水中の油分および非水溶性物質の種類、その量、用いる高分子凝集剤の種類とその添加量などを変えて実験を行えば、含油スカムの浮上速度が求まり、分離槽2の槽内に形成する水路長が決定できる。   By the way, using the buoyancy of the oil-containing scum from the treated water that has been subjected to the coagulation treatment of the oil and water-insoluble substances, the time required to float and separate the oil and water-insoluble substances that have been flocked is It depends on the ascent rate. Therefore, if the experiment was carried out by changing the type of oil and water-insoluble substances in the wastewater, the amount thereof, the type of polymer flocculant used and the amount added, etc., the ascending speed of the oil-containing scum was obtained, and the tank of the separation tank 2 The length of the water channel formed inside can be determined.

それを実現する本発明の実施の形態にかかる排水処理設備は、形成されるフロックを含油スカムとして浮上・分離する分離処理を行う分離槽2の槽内に、油分および非水溶性物質の凝集処理を施した処理水の流れ方向を変え曲がった水路とする開口端部6a,6b,6cをもつ垂直な仕切り板6とを有し、仕切り板6によって連絡口から処理水取出口9近傍までの間に、処理水取出口に向かって油分および非水溶性物質の凝集処理を施した処理水が流れる曲がった水路が形成されてなることを特徴とする。   The wastewater treatment facility according to the embodiment of the present invention that realizes this is a coagulation treatment of oil and water-insoluble substances in the tank of the separation tank 2 that performs the separation process of floating and separating the formed floc as oil-impregnated scum. And a vertical partition plate 6 having open end portions 6a, 6b, 6c that change the flow direction of the treated water and bend the water channel. The partition plate 6 extends from the communication port to the vicinity of the treated water outlet 9 by the partition plate 6. In the meantime, a bent water channel is formed in which the treated water subjected to the coagulation treatment of the oil and the water-insoluble substance is formed toward the treated water outlet.

図2中、10a,10b,10c,10d,10e,10f,10gは、開口端部6a,6b,6cをもつ垂直な仕切り板6で形成された水路を流れる凝集処理を施した処理水の流れ方向を示した。
ここで、開口端部6aをもつ垂直な仕切り板6は、分離槽2の前壁と平行に配置され、その反対側が凝集槽1との隔壁に固定されている。また、開口端部6bをもつ逆コの字状の垂直な仕切り板は、槽内の後壁近くに配置され、その反対側が分離槽2の右側壁に固定され、残る開口端部6cをもつ垂直な仕切り板も、その反対側が分離槽2の右側壁に固定されている。
In FIG. 2, 10a, 10b, 10c, 10d, 10e, 10f, and 10g are the flow of treated water subjected to agglomeration treatment that flows through the water channel formed by the vertical partition plate 6 having the open end portions 6a, 6b, and 6c. Indicated the direction.
Here, the vertical partition plate 6 having the open end 6a is arranged in parallel with the front wall of the separation tank 2, and the opposite side is fixed to a partition wall with the aggregation tank 1. In addition, an inverted U-shaped vertical partition plate having an open end 6b is arranged near the rear wall in the tank, and the opposite side is fixed to the right side wall of the separation tank 2 and has the remaining open end 6c. The other side of the vertical partition plate is also fixed to the right side wall of the separation tank 2.

このように、分離槽2の槽内に折れ曲がった水路が形成されているから、加圧水を排水に余分に加えず、排水中の油分および非水溶性物質を含油スカムとして効率的に除去することができかつ槽構造がシンプルである分離槽2を有する排水処理設備を実現することができた。但し、仕切り板は可動式とし、排水の性状や処理状況により、設置する位置を調整可能な構造とすることが好ましい。   Thus, since the bent waterway is formed in the tank of the separation tank 2, it is possible to efficiently remove the oil and water-insoluble substances in the drainage as oil-impregnated scum without adding excessive pressure water to the drainage. A wastewater treatment facility having a separation tank 2 that is simple and has a simple tank structure could be realized. However, it is preferable that the partition plate is movable and has a structure in which the installation position can be adjusted depending on the properties of the drainage and the treatment status.

また、連絡口8および処理水取出口9が、ヘッド差を利用したオーバーフロー堰で形成されてなるのが、簡単な構成によって凝集槽1と分離槽2とからなる処理槽で水処理する流量を調整することができるため、好適である。また、分離槽2には、曲がった水路のコーナー部に相当する、含油スカムが局部的に溜まる箇所の槽内底部に、空気を噴出するエアーレーション装置を設置し、曝気ブロワと接続してなるのが、その箇所に含油スカムが局部的に溜まるのを防止できるため、好適である。また、エアーレーション装置の運転は、間欠的に行うように構成してなることが、曝気ブロワの使用するエネルギーを少なくできるので好適である。   In addition, the communication port 8 and the treated water outlet 9 are formed by an overflow weir utilizing the head difference, so that the flow rate of water treatment in the treatment tank composed of the flocculation tank 1 and the separation tank 2 is simplified. This is preferable because it can be adjusted. In addition, the separation tank 2 is provided with an aeration device that blows out air at the bottom of the tank corresponding to the corner of the bent water channel, where oil-impregnated scum accumulates locally, and is connected to the aeration blower. This is preferable because it is possible to prevent the oil-impregnated scum from locally accumulating at that location. Further, it is preferable that the aeration apparatus is operated intermittently because the energy used by the aeration blower can be reduced.

処理水取出口9近傍に配置する、含油スカムを掬い上げて搬出するスカム搬出手段4としては、長い布状のフィルタ(ポリエステル製のろ布)とフィルタを繰り返し回動させる回動手段(コンベア)とで構成するのが好適である。
このようなスカム搬出手段4とすれば、長い布状のフィルタで含油スカムW2を掬い上げて搬出することができるので好適である。図3中、W1は、含油スカムW2を除去した後の処理水を示す。2aはU字状樋2bに接続される処理水供給用配管を、2bは含油スカムW2を除去した後の処理水を集めるU字状樋を示す。図1、2に示したスカム回収ホッパー5は、スカム搬出手段4で搬出された含油スカムが落下する直下に配置される。
As the scum unloading means 4 arranged in the vicinity of the treated water outlet 9 for picking up and carrying out the oil-impregnated scum, a long cloth filter (polyester filter cloth) and a rotating means for repeatedly rotating the filter (conveyor) It is suitable to comprise.
Such a scum carrying-out means 4 is preferable because the oil-impregnated scum W2 can be scooped up and carried out with a long cloth filter. In FIG. 3, W1 shows the treated water after removing the oil-impregnated scum W2. 2a is a pipe for supplying treated water connected to the U-shaped bowl 2b, and 2b is a U-shaped bowl for collecting treated water after the oil-impregnated scum W2 is removed. The scum collection hopper 5 shown in FIGS. 1 and 2 is arranged immediately below where the oil-impregnated scum carried out by the scum carrying-out means 4 falls.

以上説明した実施の形態にかかる排水処理設備は、U字状樋2bで集めた処理水W1を、その高さエネルギを利用し、処理水供給用配管2aを経て、図4に示す微生物担体槽を具備する排水処理設備へ送るようにしている。
また、高分子凝集剤の添加量は、高分子凝集剤添加手段を構成する定量ポンプ27で調整可能とし、しかも排水中の水処理状況により、電動弁12a、12b、12c、12dをそれぞれ開閉することで、凝集剤の添加法を以下のようするのがよい(図1および2を参照方)。
(a)電動弁12aを開とした場合、スクリーン11と凝集槽1をつなぐ配管の途中が凝集剤添加口となる。これによって、スクリーン11と凝集槽1をつなぐ配管内へ高分子凝集剤を添加し、凝集槽1に至る前に、高分子凝集剤と排水とを混合する添加法。
(b)電動弁12bを開とした場合、凝集槽1の排水面からある一定の高さを確保した配管の開口端が凝集剤添加口となる。これによって、凝集槽1の排水面に叩きつけるようにして高分子凝集剤と排水とを混合する添加法。
(c)電動弁12cを開とした場合、凝集槽1の底部にまで伸ばした配管の開口端が凝集剤添加口となる。この底部の凝集剤添加口を複数とすることによって、凝集槽1の底部で高分子凝集剤と排水とを混合する添加法。
(d)電動弁12dを開とした場合、図1および図2に示したように、分離槽2の角の底部にまで伸ばした配管の開口端が凝集剤添加口となる。この分離槽2への凝集剤添加口は、凝集槽1で添加する高分子凝集剤が少な過ぎたときの微調節機能を有し、未反応分の油分および非水溶性物質を完全に凝集させるために、分離槽2へ高分子凝集剤を添加する添加法。
分離槽2の底部へ高分子凝集剤を添加する凝集剤添加口を複数とし、あるいは凝集剤添加口を分離槽2の底部でなく、分離槽2の、油分および非水溶性物質の凝集処理を施した処理水面の上方とすることもできる。但し、凝集剤添加口はそれ以外に設けることもできる。
The wastewater treatment facility according to the embodiment described above uses the height energy of the treated water W1 collected by the U-shaped trough 2b, passes through the treated water supply pipe 2a, and is shown in FIG. Is sent to wastewater treatment facilities.
Further, the addition amount of the polymer flocculant can be adjusted by the metering pump 27 constituting the polymer flocculant addition means, and the motor operated valves 12a, 12b, 12c, and 12d are opened and closed depending on the state of water treatment in the waste water. Therefore, it is better to add the flocculant as follows (refer to FIGS. 1 and 2).
(a) When the motor-operated valve 12a is opened, the middle of the pipe connecting the screen 11 and the flocculation tank 1 serves as a flocculant addition port. In this way, the polymer flocculant is added to the pipe connecting the screen 11 and the flocculant tank 1, and the polymer flocculant and the waste water are mixed before reaching the flocculant tank 1.
(b) When the motor-operated valve 12b is opened, the opening end of the pipe that secures a certain height from the drainage surface of the coagulation tank 1 becomes the coagulant addition port. This is an addition method in which the polymer flocculant and the waste water are mixed so as to strike against the drainage surface of the agglomeration tank 1.
(c) When the motor-operated valve 12c is opened, the open end of the pipe extending to the bottom of the coagulation tank 1 becomes the coagulant addition port. An addition method in which a polymer flocculant and waste water are mixed at the bottom of the agglomeration tank 1 by using a plurality of flocculant addition ports at the bottom.
(d) When the motor-operated valve 12d is opened, as shown in FIGS. 1 and 2, the open end of the pipe extending to the bottom of the corner of the separation tank 2 becomes the flocculant addition port. The flocculant addition port to the separation tank 2 has a fine adjustment function when the polymer flocculant added in the flocculence tank 1 is too small, and completely aggregates the unreacted oil and water-insoluble substances. Therefore, an addition method of adding a polymer flocculant to the separation tank 2.
A plurality of flocculant addition ports for adding the polymer flocculant to the bottom of the separation tank 2 are used, or the flocculant addition port is not the bottom of the separation tank 2 but the separation of the oil and water-insoluble substances in the separation tank 2 It can also be set above the treated water surface. However, a flocculant addition port can also be provided in addition to that.

図8には、本発明に用いて好適な高分子凝集剤の添加量を制御する制御装置の構成を示した。図9には、図8に示した高分子凝集剤添加手段の定量ポンプの運転例を、図10には、同図8に示したスカム搬出手段のコンベアの運転例をフロー図としてそれぞれ示した。
水処理を開始した以降、図9、図10に示したようにして、高分子凝集剤添加手段の定量ポンプおよびスカム搬出手段のコンベアの駆動モータの運転・停止を行うことで、高分子凝集剤を効果的に添加することができ、水処理性能の安定化と水処理コストの低減が達成できる。
FIG. 8 shows the configuration of a control device that controls the amount of the polymer flocculant that is suitable for use in the present invention. FIG. 9 shows an example of operation of the metering pump of the polymer flocculant adding means shown in FIG. 8, and FIG. 10 shows an example of operation of the conveyor of the scum unloading means shown in FIG. .
After starting the water treatment, the polymer flocculant is operated by stopping and operating the metering pump of the polymer flocculant adding means and the drive motor of the conveyor of the scum unloading means as shown in FIGS. Can be effectively added to stabilize the water treatment performance and reduce the water treatment cost.

油分および非水溶性物質を多く含有する食品加工工場の水処理を可能とした排水処理設備を構築した。この食品加工工場排水中には、表1に示すように、油分のほか、非水溶性物質が多く含まれている。   We constructed a wastewater treatment facility that enables water treatment in food processing plants that contain a large amount of oil and water-insoluble substances. As shown in Table 1, the food processing factory effluent contains a large amount of water-insoluble substances in addition to oil.

Figure 0005270247
Figure 0005270247

そこで、図1に示した排水処理設備を、図4に示した微生物担体槽20を具備する排水処理設備の前処理装置として設置した。
構築した排水処理設備の主な仕様
凝集槽1の平面寸法:左右方向の内寸法=2m、前後方向の内寸法=4m。
分離槽2の平面寸法:左右方向の内寸法=4m、前後方向の内寸法=4m。
Therefore, the wastewater treatment facility shown in FIG. 1 was installed as a pretreatment device for the wastewater treatment facility including the microorganism carrier tank 20 shown in FIG.
Main specifications of the constructed wastewater treatment facility Coplanar tank 1 plane dimensions: inner dimension in the left-right direction = 2 m, inner dimension in the front-rear direction = 4 m.
Planar dimension of the separation tank 2: inner dimension in the left-right direction = 4 m, inner dimension in the front-rear direction = 4 m.

分離槽2の槽内に、油分の凝集処理を施した処理水の流れ方向を変え曲がった水路とする開口端部6a,6b,6cをもつ垂直な仕切り板6を図2のように設けた。
分離槽の槽内に設けた垂直な仕切り板6によって、水深が3m、水路の幅が800mmの曲がった水路を形成した。また、スカム搬出手段4として長い布状のフィルタ(たとえばポリエステル製のろ布)を張り付けたコンベアを、処理水取出口近傍に設けた。
In the tank of the separation tank 2, a vertical partition plate 6 having open end portions 6 a, 6 b, 6 c is provided as shown in FIG. .
A bent water channel having a water depth of 3 m and a water channel width of 800 mm was formed by a vertical partition plate 6 provided in the tank of the separation tank. Moreover, the conveyor which stuck the long cloth-like filter (for example, polyester filter cloth) as the scum carrying-out means 4 was provided in the vicinity of the treated water outlet.

このコンベアの下端部は、図3に示したように、油分の凝集処理を施した処理水中に浸漬させ、その上端部は、スカム回収ホッパー5の上方に位置させて含油スカムを掬い上げて搬出するスカム搬出手段4とした。
この構築した排水処理設備(発明例)と、従来例(図1に示した排水処理設備の代わりに一般的な加圧浮上分離装置を設置し、次いで、図4に示した微生物担体槽20を有する排水処理設備で水処理した場合)とで、食品加工工場排水を水処理し、以下の処理水の水質分析を行い、水処理性能を比較した。
As shown in FIG. 3, the lower end of the conveyor is immersed in treated water subjected to oil agglomeration, and the upper end of the conveyor is positioned above the scum recovery hopper 5 to lift up the oil-containing scum and carry it out. The scum unloading means 4 is used.
The constructed waste water treatment facility (invention example) and a conventional example (a general pressurized flotation separation device is installed in place of the waste water treatment facility shown in FIG. 1, and then the microbial carrier tank 20 shown in FIG. 4 is installed. In the case of water treatment using a wastewater treatment facility, the food processing factory wastewater was treated with water, and the water quality of the following treated water was analyzed to compare the water treatment performance.

微生物担体槽20を有する排水処理設備に投入される処理水(発明例の場合、図1に示した排水処理設備で水処理した後の処理水、従来例の場合、加圧浮上分離装置で水処理した後の処理水)の水質を表2に、微生物担体槽20を有する排水処理設備で水処理され、公共水域や下水道などに放流する直前の処理水の水質を表3に示した。   Treated water introduced into a wastewater treatment facility having a microorganism carrier tank 20 (in the case of the invention, treated water after being treated with the wastewater treatment facility shown in FIG. 1; The water quality of the treated water after treatment is shown in Table 2, and the quality of the treated water just before it is treated in the wastewater treatment facility having the microorganism carrier tank 20 and discharged into public water areas or sewers is shown in Table 3.

Figure 0005270247
Figure 0005270247

Figure 0005270247
Figure 0005270247

表2、表3に示した水質分析結果から、発明例によれば、従来例と何ら遜色なく排水中の油分および非水溶性物質を効率的に除去することができ、表3に示したとおり、公共水域や下水道などに放流することができる処理水の水質が得られた。
ここで、BOD:Biochemical Oxygen Demand(生物化学的酸素要求量)、n−Hex:n−Hexane Extract(n−ヘキサンの抽出物量)を意味し、前者は排水中の有機物量、後者は排水中の油分量を表わす。そのほかSS:Suspension Solid(浮遊懸濁物質量)は、排水中の非水溶性物質の量を、COD: Chemical Oxygen Demand(化学的酸素要求量)は、排水中の有機物量に対応する量を表わす。
(微生物担体槽20を具備する排水処理設備の構成:図4参照)
20aは微生物担体槽20内の微生物担体である。微生物担体槽20内には、散気装置25とれに隣接させて適宜なスクリーンが設置されている。21は曝気槽、22は接触曝気槽であり、散気装置25が槽内の底部に設置されている。23は沈殿槽、24は塩素減菌消毒槽である。散気装置25は、たとえば図1の4基からなる曝気ブロワ19の方と接続され、曝気ブロワ19から送られた空気で槽内を散気している。
From the water quality analysis results shown in Tables 2 and 3, according to the invention example, oil and water-insoluble substances in the waste water can be efficiently removed as in the conventional example, as shown in Table 3. The quality of treated water that can be discharged into public water areas and sewers was obtained.
Here, BOD: Biochemical Oxygen Demand (biochemical oxygen demand), n-Hex: n-Hexane Extract (the amount of n-hexane extract), the former is the amount of organic matter in the wastewater, the latter is in the wastewater Represents the oil content. In addition, SS: Suspension Solid (amount of suspended suspended solids) represents the amount of water-insoluble substances in wastewater, and COD: Chemical Oxygen Demand (chemical oxygen demand) represents the amount corresponding to the amount of organic matter in wastewater. .
(Configuration of wastewater treatment facility equipped with microbial carrier tank 20: see FIG. 4)
20 a is a microbial carrier in the microbial carrier tank 20. An appropriate screen is installed in the microorganism carrier tank 20 adjacent to the diffuser 25. 21 is an aeration tank, 22 is a contact aeration tank, and an air diffuser 25 is installed at the bottom of the tank. 23 is a sedimentation tank, 24 is a chlorine sterilization disinfection tank. The air diffuser 25 is connected to, for example, the four aeration blowers 19 shown in FIG. 1 and diffuses the inside of the tank with the air sent from the aeration blower 19.

本発明を、微生物担体槽を具備する排水処理設備の前処理装置とする場合の全体構成図である。It is a whole block diagram in case this invention is used as the pre-processing apparatus of the waste water treatment facility which comprises a microorganisms carrier tank. 本発明の実施の形態にかかる排水処理設備の要部を示す横断面図である。It is a cross-sectional view which shows the principal part of the waste water treatment facility concerning embodiment of this invention. 本発明に用いる処理槽の処理水取出口近傍を示す縦断面図である。It is a longitudinal cross-sectional view which shows the treated water intake vicinity of the processing tank used for this invention. 本発明を適用して好適な微生物担体槽を具備する排水処理設備の構成図である。It is a block diagram of the waste water treatment facility which comprises the suitable microorganism carrier tank to which this invention is applied. (a)、(b)は微生物担体を用いた他の排水処理設備の構成図である。(A), (b) is a block diagram of the other waste water treatment facility using a microorganism carrier. 特許文献2に記載の加圧浮上分離槽を用いた排水処理設備の水処理フロー図である。It is a water treatment flow figure of the wastewater treatment facility using the pressurization flotation separation tank given in patent documents 2. (a)は加圧浮上分離槽の一例の構造を示す断面図、(b)はその作用を説明する要部断面図である。(A) is sectional drawing which shows the structure of an example of a pressurization floating separation tank, (b) is principal part sectional drawing explaining the effect | action. 本発明に用いて好適な高分子凝集剤の添加量を制御する制御装置の構成図である。It is a block diagram of the control apparatus which controls the addition amount of a polymer flocculent suitable for use in the present invention. 図8に示した高分子凝集剤添加手段の定量ポンプの運転例を示すフロー図である。It is a flowchart which shows the operation example of the metering pump of the polymer flocculent addition means shown in FIG. 図8に示したスカム搬出手段のコンベアの運転例を示すフロー図である。It is a flowchart which shows the operation example of the conveyor of the scum carrying-out means shown in FIG.

符号の説明Explanation of symbols

W1 処理水(図1に示した排水処理設備で水処理した処理水)
W2 含油スカム
1 凝集槽
2 分離槽
2a 処理水供給用配管
2b U字状樋
3 攪拌装置(エアーレーション装置)
4 スカム搬出手段
5 スカム回収ホッパー
6 仕切り板
6a,6b,6c 開口端部
7 排水取入口
8 連絡口
9 処理水取出口
10a,10b,10c,10d,10e,10f,10g 流れ方向
11 スクリーン
12 凝集剤貯留槽
12a、12b、12c、12d 高分子凝集剤添加手段の電動弁
16 排水貯留槽
17 処理水貯留槽
18 流量調整用槽
19 曝気ブロワ
20 微生物担体槽
20a 微生物担体
21 曝気槽
22 接触曝気槽
23 沈殿槽
24 塩素減菌消毒槽
25 散気装置
26 配管
27 定量ポンプ
30 排水貯留槽
31 微生物担体
32 スクリーン
33 攪拌装置
34 散気装置
35 スクリーン
40 脱窒槽
50 硝化槽
60 沈殿槽
70 加圧浮上分離装置
71 排水流入部
72 含油スカム集め手段(スキマの刃)
73 傾斜板
74 集水室
75 処理水取出口
76 排水取入口
77 加圧水取入口
78 含油スカム排出口
79 スラッジ排出口
80 油分・非水溶性物質
81 気泡
W1 treated water (treated water treated with wastewater treatment facility shown in Fig. 1)
W2 Oil-impregnated scum 1 Coagulation tank 2 Separation tank
2a Pipe for treated water supply
2b U-shaped bowl 3 Stirring device (aeration device)
4 Scum unloading means 5 Scum collection hopper 6 Partition plate
6a, 6b, 6c Open end 7 Drainage intake 8 Communication port 9 Treated water intake
10a, 10b, 10c, 10d, 10e, 10f, 10g Flow direction
11 screens
12 Flocculant reservoir
12a, 12b, 12c, 12d Motorized valve for adding polymer flocculant
16 Wastewater storage tank
17 Treated water storage tank
18 Flow adjustment tank
19 Aeration blower
20 Microbial carrier tank
20a Microbial carrier
21 Aeration tank
22 Contact aeration tank
23 Settling tank
24 Chlorine sterilization tank
25 Air diffuser
26 Piping
27 Metering pump
30 Wastewater storage tank
31 Microbial carrier
32 screens
33 Stirrer
34 Air diffuser
35 screen
40 Denitrification tank
50 Nitrification tank
60 Sedimentation tank
70 Pressure levitation separator
71 Drainage inlet
72 Oil-impregnated scum collecting means (clearance blade)
73 Inclined plate
74 Catchment room
75 Treated water outlet
76 Drainage intake
77 Pressurized water inlet
78 Oil-impregnated scum outlet
79 Sludge outlet
80 Oil and water-insoluble substances
81 bubbles

Claims (9)

槽内に攪拌装置を有し、油分および非水溶性物質を含む排水を排水取入口から取り入れるとともに、高分子凝集剤添加手段により添加される高分子凝集剤と排水中の油分および非水溶性物資とを反応させて凝集処理を行う凝集槽と、該凝集槽に連絡口で連通され、前記凝集処理で形成されるフロックを含油スカムとして浮上・分離する分離処理を行うとともに、排水中の油分および非水溶性物質を含油スカムとして除去した後の処理水のみを処理水取出口から取り出す分離槽を有する食品加工工場排水処理設備であって、
前記処理水取出口近傍に、前記含油スカムを掬い上げて搬出するスカム搬出手段と、前記分離槽の槽内に、油分および非水溶性物質の凝集処理を施した処理水の流れ方向を変え前記分離槽の底面に平行な面内で曲がった水路とする開口端部をもつ垂直な仕切り板とを有し、該仕切り板によって前記連絡口から前記処理水取出口近傍までの間に、前記処理水取出口に向かって油分および非水溶性物質の凝集処理を施した処理水が流れる前記分離槽の底面に平行な面内で曲がった水路が形成されてなり、前記連絡口および前記処理水取出口が機械的移送手段として、ヘッド差を利用したオーバーフロー堰で形成され、前記スカム搬出手段は、長い布状のフィルタと前記フィルタを繰り返し回動させる回動手段とで構成し、前記分離槽には、曲がった水路のコーナー部に相当する、前記含油スカムが局部的に溜まる箇所の槽内底部に、空気を噴出するエアーレーション装置を設置し、曝気ブロワと接続してなることを特徴とする食品加工工場排水処理設備。
The tank has a stirrer, and drains containing oil and water-insoluble substances are taken from the drainage intake, and the polymer flocculant added by the polymer flocculant addition means and the oil and water-insoluble materials in the drainage are added. A flocculant tank that reacts with the flocculant and communicates with the flocculant tank at a communication port, and performs a separation process that floats and separates the floc formed by the flocculant process as an oil-containing scum, A food processing factory wastewater treatment facility having a separation tank for taking out only treated water after removing water-insoluble substances as oil-containing scum from a treated water outlet,
The process water taking near the outlet, a scum discharge means for unloaded scooped the oil-impregnated scum, said in a bath of the separation tank, the change of oil and the flow direction of the treated water subjected to coagulation treatment of water-insoluble material A vertical partition plate having an open end that is a water channel bent in a plane parallel to the bottom surface of the separation tank, and the treatment is performed between the communication port and the vicinity of the treated water outlet by the partition plate. water taking Ri Na and waterways bent in a plane parallel to the bottom of the separation tank the process water flows subjected to coagulation treatment of oil and water-insoluble substance is formed toward the exit, the communication ports and the treated water The take-out port is formed by an overflow weir utilizing a head difference as a mechanical transfer means, and the scum carry-out means is constituted by a long cloth filter and a rotation means for repeatedly rotating the filter, and the separation tank Is bent Corresponding to the corner portions of the waterway, the tank bottom inside of a portion the oil-containing scum accumulates locally, established the aeration device for ejecting air, food processing plants wastewater characterized by being connected to the aeration blower Processing equipment.
前記凝集槽の槽内に設ける攪拌装置は、空気を噴出するエアーレーション装置とし、該エアーレーション装置を槽内底部に設けて曝気ブロワと接続してなることを特徴とする請求項1に記載の食品加工工場排水処理設備。 The stirring device is provided in the flocculation tank in the tank, the aeration device for injecting air, according to claim 1, characterized by being connected to the aeration blower is provided the aeration device in Tank bottom Wastewater treatment facility at food processing plant . 前記エアーレーション装置の運転を、間欠的に行うように構成してなることを特徴とする請求項又はに記載の食品加工工場排水処理設備。 The food processing factory waste water treatment facility according to claim 1 or 2 , wherein the aeration apparatus is operated intermittently. 前記高分子凝集剤添加手段は、添加量を調節可能とすることを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。 The food processing factory wastewater treatment facility according to any one of claims 1 to 3 , wherein the polymer flocculant addition means is capable of adjusting an addition amount. 前記高分子凝集剤添加手段は、形成されるフロックの状態に基づいて添加量・濃度を設定することを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。 The food processing factory wastewater treatment facility according to any one of claims 1 to 4 , wherein the polymer flocculant addition means sets the addition amount and concentration based on the state of the floc formed. 前記高分子凝集剤添加手段は、添加口が、前記槽の上部または底部の複数箇所配置されるとともに、各々の添加量を個別に設定することを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。 The said polymer flocculent addition means sets the addition amount individually, while an addition port is arrange | positioned in multiple places of the upper part or the bottom part of the said tank, The any one of Claims 1-5 characterized by the above-mentioned. Wastewater treatment facility for food processing plant as described in the paragraph. 前記高分子凝集剤添加手段は、凝集剤貯留槽と配水管と定量ポンプで構成することを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。 The food processing factory wastewater treatment facility according to any one of claims 1 to 6 , wherein the polymer flocculant adding means includes a flocculant storage tank, a water pipe, and a metering pump. 前記高分子凝集剤添加手段は、凝集剤貯留槽と配水管と定量ポンプと電動弁で構成することを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。 The food processing factory wastewater treatment facility according to any one of claims 1 to 7 , wherein the polymer flocculant adding means includes a flocculant storage tank, a water pipe, a metering pump, and an electric valve. 生物担体槽を具備する排水処理設備の前処理装置として用いることを特徴とする請求項1〜のいずれか1項に記載の食品加工工場排水処理設備。
Food processing plants wastewater treatment facilities according to any one of claims 1-8, characterized by using as a pretreatment apparatus wastewater treatment facility having a microbial carrier vessel.
JP2008196473A 2008-07-30 2008-07-30 Wastewater treatment facility at food processing plant Active JP5270247B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2008196473A JP5270247B2 (en) 2008-07-30 2008-07-30 Wastewater treatment facility at food processing plant

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2008196473A JP5270247B2 (en) 2008-07-30 2008-07-30 Wastewater treatment facility at food processing plant

Publications (2)

Publication Number Publication Date
JP2010029813A JP2010029813A (en) 2010-02-12
JP5270247B2 true JP5270247B2 (en) 2013-08-21

Family

ID=41734955

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2008196473A Active JP5270247B2 (en) 2008-07-30 2008-07-30 Wastewater treatment facility at food processing plant

Country Status (1)

Country Link
JP (1) JP5270247B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5597314B1 (en) * 2014-03-12 2014-10-01 ヤマテック株式会社 Processing equipment
CN104828982A (en) * 2015-04-30 2015-08-12 刘孟 Waste cooking oil deposition processing and oil recycling device
CN104828974A (en) * 2015-04-30 2015-08-12 李秀林 Partitioned waste cooking oil recovery device

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56113392A (en) * 1980-02-14 1981-09-07 Nippon Steel Corp Disposal of oil-containing waste water
SE503569C2 (en) * 1995-07-06 1996-07-08 Andreas Schelin Device for separating oil from water

Also Published As

Publication number Publication date
JP2010029813A (en) 2010-02-12

Similar Documents

Publication Publication Date Title
CA2675019C (en) System and method for enhancing an activated sludge process
KR101346525B1 (en) Device to cohere and to dispose of wastes water
KR100723337B1 (en) An oxidizing Pressurized Uprising Apparatus
US8632685B2 (en) Multistage DAF-advanced oxidation system
US20090272681A1 (en) Recycle water treatment system for car wash
WO1992019547A1 (en) Wastewater treatment system
CN209493455U (en) Highly concentrated oil-bearing wastewater advanced treatment system
JP2010046602A (en) Method of treating oil-containing waste water
JP5270247B2 (en) Wastewater treatment facility at food processing plant
KR100446141B1 (en) The waster water treatment system and method
KR100576348B1 (en) Dissolved airfloatation system for treatment waste water
JP2005000845A (en) Apparatus and method for treating oil and fat in oil-containing waste water
US10961136B2 (en) Combiflotation for purification and disinfection of waste water
Babatola et al. Failure analysis of a dissolved air flotation treatment plant in a dairy industry
JP4408435B2 (en) Waste water treatment apparatus and waste water treatment method
KR200371017Y1 (en) Dissolved airfloatation system for treatment waste water
KR200194158Y1 (en) Waste water treating system
CN218709814U (en) Oily wastewater treatment system
CN213357265U (en) Cutting fluid effluent disposal system
KR100228571B1 (en) Wastewater treatment system
JP3877482B2 (en) Garbage disposal equipment
JP2005131555A (en) Garbage treatment system
Dixon et al. Chemical and Biochemical Technologies for Environmental Infrastructure Sustainability
CN117700036A (en) Oily wastewater treatment system
JPH0852486A (en) Sludge returning method for anaerobic waste water treatment

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20110214

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20120510

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20120529

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20120727

A711 Notification of change in applicant

Free format text: JAPANESE INTERMEDIATE CODE: A711

Effective date: 20130117

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A821

Effective date: 20130117

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20130423

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20130509

R150 Certificate of patent or registration of utility model

Ref document number: 5270247

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250