JP2010221166A - Sewage treatment apparatus for ship - Google Patents
Sewage treatment apparatus for ship Download PDFInfo
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- JP2010221166A JP2010221166A JP2009073059A JP2009073059A JP2010221166A JP 2010221166 A JP2010221166 A JP 2010221166A JP 2009073059 A JP2009073059 A JP 2009073059A JP 2009073059 A JP2009073059 A JP 2009073059A JP 2010221166 A JP2010221166 A JP 2010221166A
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- tank
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- backwashing
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- membrane separation
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- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
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- Separation Using Semi-Permeable Membranes (AREA)
- Activated Sludge Processes (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
Description
本発明は接触材による生物膜処理とろ過膜(MF膜)によるろ過を同じ槽内で同時に行う膜分離接触酸化法による船舶用汚水処理装置に関するものである。 The present invention relates to a marine sewage treatment apparatus using a membrane separation contact oxidation method in which biofilm treatment with a contact material and filtration with a filtration membrane (MF membrane) are simultaneously performed in the same tank.
従来、船舶用汚水処理装置としては全接触酸化法(接触酸化室と消毒室だけで構成され、沈殿室はない構造)がコンパクトで馴致期間も短く保守点検が容易と云う特徴を生かし主流となっている。 Conventionally, as a sewage treatment system for ships, the all-contact oxidation method (a structure consisting of only a contact oxidation chamber and a disinfection chamber and no sedimentation chamber) has become the mainstream, taking advantage of its compactness, short acclimatization period and easy maintenance and inspection. ing.
しかしながら船舶からのふん尿等の排出規制が高まるにつれ、BOD除去は接触材の面積を増やすことで対応できるが、接触材から剥離した生物膜等の浮遊物質(SS)はその基準値を担保することが困難と成ってきた。 However, as the regulation of manure discharge from ships increases, BOD removal can be dealt with by increasing the area of the contact material, but the suspended matter (SS) such as biofilm peeled off from the contact material must ensure the standard value. Has become difficult.
また、消毒薬筒への流入汚水に定量性を保つ機構が無い為、溶解過多や溶解不足が発生し安定した残留塩素(0.5mg/L以下)の確保が困難であった。 In addition, since there is no mechanism to maintain quantitativeness in the sewage flowing into the disinfecting medicine cylinder, excessive dissolution or insufficient dissolution occurred, making it difficult to secure stable residual chlorine (0.5 mg / L or less).
本発明は掛かる問題を解決するために成されたものであり、従来機能に加え高性能で残留塩素濃度の均一化も図れ且つ省エネ.省力を目的としたものである。 The present invention has been made to solve the problems involved, and in addition to the conventional functions, it is possible to achieve high performance with uniform residual chlorine concentration and energy saving. The purpose is to save labor.
本発明は上記課題に鑑みなされ、請求項1に記載の発明は、接触材とろ過膜(MF膜)を同じ槽に浸漬し、MF膜のスクラビングのエアーを接触材のエアレーションと共用し、且つ膜分離接触酸化槽後段の処理水排出ラインには吸引ポンプを介して消毒薬溶解器並びに滞留時間約15分の消毒兼逆洗タンクを設け、且つ処理水排出ラインと消毒兼逆洗タンクから分岐した逆洗ラインに夫々自動弁並びにろ過水量とろ過膜逆洗水量を夫々制御する定流量弁を設けた事を特徴とする。 The present invention has been made in view of the above problems, and the invention according to claim 1 immerses the contact material and the filtration membrane (MF membrane) in the same tank, shares the air of scrubbing the MF membrane with the aeration of the contact material, and The treatment water discharge line after the membrane separation contact oxidation tank is equipped with a disinfectant dissolver and a disinfection / backwash tank with a residence time of about 15 minutes via a suction pump, and branches from the treatment water discharge line and the disinfection / backwash tank. Each of the backwash lines is provided with an automatic valve and a constant flow valve for controlling the filtrate water amount and the membrane backwash water amount, respectively.
また、本発明の請求項2に記載の発明は、膜分離接触酸化槽に液面制御手段を設け、処理水排出ごとに時限タイマーの設定時間、逆洗を行う事を特徴とする。
Further, the invention described in
本発明の請求項1に記載の発明によれば、膜分離接触酸化槽内の中央にMF膜を浸漬し、その外周を取り囲むように接触材を浸漬し、MF膜のスクラビングのエアーを接触材のエアレーションと共用することにより空気量が節約出来、曝気用ブロワの出力が少なくて済み省エネになる。 According to the first aspect of the present invention, the MF membrane is immersed in the center of the membrane separation contact oxidation tank, the contact material is immersed so as to surround the outer periphery thereof, and the scrubbing air of the MF membrane is used as the contact material. By sharing with aeration, the amount of air can be saved, and the output of the aeration blower is reduced, saving energy.
加えて膜分離接触酸化槽後段の処理水排出ラインに吸引ポンプを介して消毒薬溶解器並びに滞留時間約15分の消毒兼逆洗タンクを設ける。一般的に有機高分子多孔質体のろ過膜は水の粘度の影響を受け透過水量が変動するが、処理水排出ラインと消毒兼逆洗タンクから分岐した逆洗ラインに夫々自動弁並びにろ過水量とろ過膜逆洗水量を夫々制御する定流量弁を設けることにより、ろ過水量(流速)が一定となり消毒殺菌効果が一様に担保できる。更にろ過膜逆洗水に定量性を持たす事により、安定した逆洗効果の維持が期待出来る。 In addition, a disinfectant dissolver and a disinfection and backwash tank with a residence time of about 15 minutes are installed in the treated water discharge line after the membrane separation contact oxidation tank via a suction pump. In general, porous membranes made of porous organic polymers fluctuate in the amount of permeated water due to the effect of water viscosity. By providing a constant flow valve that controls the amount of filtration membrane backwash water respectively, the amount of filtrate water (flow rate) becomes constant and the disinfection and sterilization effect can be ensured uniformly. Furthermore, by providing the filter membrane backwash water with a quantitative property, a stable backwash effect can be expected.
また、本発明の請求項2に記載の発明によれば、膜分離接触酸化槽に液面制御手段を設け、処理水排出完了ごとに時限タイマーの設定時間、自動逆洗と自動エアスクラビングを行うことにより、ろ過能力の伸延が計れ、手動薬液洗浄の回数が少なくなり省力化に繋がる。
According to the invention described in
以下、図面に従って本発明の実施の最良の形態により、本発明の詳細を説明する。 The details of the present invention will be described below according to the best mode for carrying out the present invention with reference to the drawings.
図1は本発明の実施形態を示す構造兼配管系統図である。図2は本発明の運転タイミングチャート図である。 FIG. 1 is a structure and piping system diagram showing an embodiment of the present invention. FIG. 2 is an operation timing chart of the present invention.
本発明の実施形態は船舶内で発生するふん尿W1を浄化するものにして、膜分離接触酸化槽1の中央にろ過膜(MF膜)3を浸漬し、その外周を取り囲むように接触材2を浸漬する。
The embodiment of the present invention purifies the manure W1 generated in the ship, soaks the filtration membrane (MF membrane) 3 in the center of the membrane separation contact oxidation tank 1, and the
MF膜3の下部より曝気ブロワ8からの空気を自動弁V5を介して吹き込む。この空気はMF膜3表面をスクラビングする傍ら、汚水中に溶け込み溶存酸素となって接触材2表面の生物膜に酸素を与える。またその回流力でスクリーン9の固形物を破砕する。
Air from the aeration blower 8 is blown from the lower part of the
膜分離接触酸化槽1の後段の処理水排出ラインには自動弁V1並びに定流量弁FC1を介して吸引ポンプ4が有り、膜分離接触酸化槽1に装填した液面制御手段(時限タイマー内蔵)7の信号で吸引ポンプ4は自動発停を繰り返す。 The treated water discharge line downstream of the membrane separation contact oxidation tank 1 has a suction pump 4 via an automatic valve V1 and a constant flow valve FC1, and the liquid level control means loaded in the membrane separation contact oxidation tank 1 (with a built-in timer) In response to the signal 7, the suction pump 4 repeats automatic start / stop.
吸引ポンプ4の後段には自動弁V2を介して消毒薬溶解器5及び滞留時間約15分の消毒兼逆洗タンク6を設け、定流量弁FC1で流量制御したろ過水は一定流速で消毒薬溶解器5に流入し固形消毒薬を定量溶かして消毒兼逆洗タンク6内を約15分掛けて通過する間に完全に殺菌され、残留塩素濃度も規制値内で船外に排出される。 A disinfectant dissolver 5 and a disinfection and backwash tank 6 with a residence time of about 15 minutes are provided at the subsequent stage of the suction pump 4 through an automatic valve V2. It flows into the dissolver 5, dissolves the solid disinfectant quantitatively, and is completely sterilized while passing through the disinfection and backwash tank 6 for about 15 minutes, and the residual chlorine concentration is discharged outside the ship within the regulation value.
吸引ポンプ4は膜分離接触酸化槽1に設けた液面制御手段7が上水位を検知すると自動起動し、下水位を検知するまで吸引ろ過を行い、処理水W2を船外に排出する。この間自動弁V1,V2,V5は開でV3,V4は閉となる。 The suction pump 4 is automatically activated when the liquid level control means 7 provided in the membrane separation contact oxidation tank 1 detects the upper water level, performs suction filtration until the lower water level is detected, and discharges the treated water W2 to the outside of the ship. During this time, the automatic valves V1, V2, and V5 are open and V3 and V4 are closed.
液面制御手段7が下水位を検知すると自動弁V3.V4が開きV1,V2,V5は閉となるも、引き続き吸引ポンプ4は運転を続け、消毒兼逆洗タンク6内の処理水を定流量弁FC2を介してろ過膜(MF膜)に一定時間(T1)送水し膜の逆洗を行う、このとき曝気ブロワ8は停止する。T1がタイムアウトすると吸引ポンプ4は停止し、曝気ブロワ8は再び起動しろ過膜(MF膜)3に空気を供給し、一定時間(T2)膜表面の異物を掻き落す(エアスクラビング)。T2タイムオウト後は液面制御手段7の上水位検知信号による再起動に備える。 When the liquid level control means 7 detects the sewage level, the automatic valve V3.V4 is opened and V1, V2, V5 are closed, but the suction pump 4 continues to operate to determine the treated water in the disinfection and backwash tank 6. The aeration blower 8 is stopped at this time by supplying water to the filtration membrane (MF membrane) through the flow valve FC2 for a predetermined time (T1) and backwashing the membrane. When T1 times out, the suction pump 4 is stopped, the aeration blower 8 is started again, air is supplied to the filtration membrane (MF membrane) 3, and the foreign matter on the membrane surface is scraped off (air scrubbing) for a certain time (T2). After the T2 time-out, the liquid level control means 7 is prepared for restart by the water level detection signal.
この一連の運転サイクルは別途設けた制御盤内(図示せず)の時限タイマーT1,T2及び液面制御手段7により運転制御する。 This series of operation cycles is controlled by timed timers T1 and T2 and liquid level control means 7 in a separately provided control panel (not shown).
これらの一連の動作を運転タイミングチャートとして図2に示す。 A series of these operations is shown in FIG. 2 as an operation timing chart.
本発明は船舶から発生する糞尿からの海洋汚染を防止する規制強化に対応出来るものであり、省スペース、省エネ、省力と言う特徴を持ち合わせる高性能船舶用汚水処理装置としての利用に適す。 The present invention can cope with the strengthening of regulations for preventing marine pollution from manure generated from a ship, and is suitable for use as a high-performance ship sewage treatment apparatus having the characteristics of space saving, energy saving and labor saving.
W1 糞尿原水
W2 処理水
1 膜分離接触酸化槽
2 接触材
3 ろ過膜(MF膜)
4 吸引ポンプ(P1)
5 消毒薬溶解器
6 消毒兼逆洗タンク
7 液面制御手段(タイマーT1,T2付)
8 曝気ブロワ(B1)
9 スクリーン
V1 自動弁
V2 自動弁
V3 自動弁
V4 自動弁
V5 自動弁
FC1 定流量弁
FC2 定流量弁
W1 Raw manure water
W2 Treated water 1 Membrane separation
4 Suction pump (P1)
5 Disinfectant dissolver 6 Disinfection and backwash tank 7 Liquid level control means (with timers T1 and T2)
8 Aeration blower (B1)
9 screens
V1 automatic valve
V2 automatic valve
V3 automatic valve
V4 automatic valve
V5 automatic valve
FC1 constant flow valve
FC2 constant flow valve
Claims (2)
2. A sewage treatment apparatus for a ship according to claim 1, wherein a liquid level control means is provided in the membrane separation contact oxidation tank, and backwashing is performed for a set time of a timed timer after completion of discharging the treated water.
Priority Applications (1)
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JP2009073059A JP2010221166A (en) | 2009-03-25 | 2009-03-25 | Sewage treatment apparatus for ship |
Applications Claiming Priority (1)
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JP2009073059A JP2010221166A (en) | 2009-03-25 | 2009-03-25 | Sewage treatment apparatus for ship |
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JP2010221166A true JP2010221166A (en) | 2010-10-07 |
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ID=43038931
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JP2009073059A Pending JP2010221166A (en) | 2009-03-25 | 2009-03-25 | Sewage treatment apparatus for ship |
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Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102417280A (en) * | 2011-12-09 | 2012-04-18 | 安庆长谷川船舶科技有限公司 | Domestic sewage treatment device for ship |
KR101215482B1 (en) | 2011-06-23 | 2012-12-26 | 삼성중공업 주식회사 | Discharge organization of effluent on ship |
CN103196735A (en) * | 2013-04-09 | 2013-07-10 | 桂林电子科技大学 | Full-automatic filtering device of water sample of in-situ environment water body monitor |
CN106474930A (en) * | 2016-10-31 | 2017-03-08 | 广东粤港供水有限公司 | One kind is dispersed into water submerged membrane cell system |
CN109133453A (en) * | 2018-08-30 | 2019-01-04 | 福建安冠环境科技有限公司 | One kind proposing target photocatalysis treatment equipment for sewage |
CN113735305A (en) * | 2021-08-02 | 2021-12-03 | 中南安全环境技术研究院股份有限公司 | Treatment device for eliminating rural black and odorous water |
CN114180765A (en) * | 2021-12-06 | 2022-03-15 | 哈尔滨工程大学 | Intelligent multiple biological prevention and control device and method for marine MBR (membrane bioreactor) water treatment equipment |
-
2009
- 2009-03-25 JP JP2009073059A patent/JP2010221166A/en active Pending
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR101215482B1 (en) | 2011-06-23 | 2012-12-26 | 삼성중공업 주식회사 | Discharge organization of effluent on ship |
CN102417280A (en) * | 2011-12-09 | 2012-04-18 | 安庆长谷川船舶科技有限公司 | Domestic sewage treatment device for ship |
CN103196735A (en) * | 2013-04-09 | 2013-07-10 | 桂林电子科技大学 | Full-automatic filtering device of water sample of in-situ environment water body monitor |
CN103196735B (en) * | 2013-04-09 | 2015-06-10 | 桂林电子科技大学 | Full-automatic filtering device of water sample of in-situ environment water body monitor |
CN106474930A (en) * | 2016-10-31 | 2017-03-08 | 广东粤港供水有限公司 | One kind is dispersed into water submerged membrane cell system |
CN109133453A (en) * | 2018-08-30 | 2019-01-04 | 福建安冠环境科技有限公司 | One kind proposing target photocatalysis treatment equipment for sewage |
CN113735305A (en) * | 2021-08-02 | 2021-12-03 | 中南安全环境技术研究院股份有限公司 | Treatment device for eliminating rural black and odorous water |
CN114180765A (en) * | 2021-12-06 | 2022-03-15 | 哈尔滨工程大学 | Intelligent multiple biological prevention and control device and method for marine MBR (membrane bioreactor) water treatment equipment |
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