JPS59179123A - Treating apparatus of captured substance such as jellyfish at intake of sea water - Google Patents

Treating apparatus of captured substance such as jellyfish at intake of sea water

Info

Publication number
JPS59179123A
JPS59179123A JP58054785A JP5478583A JPS59179123A JP S59179123 A JPS59179123 A JP S59179123A JP 58054785 A JP58054785 A JP 58054785A JP 5478583 A JP5478583 A JP 5478583A JP S59179123 A JPS59179123 A JP S59179123A
Authority
JP
Japan
Prior art keywords
jellyfish
sea water
intake
processing
captured
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.)
Granted
Application number
JP58054785A
Other languages
Japanese (ja)
Other versions
JPH0131434B2 (en
Inventor
Hiroshi Ono
尾野 博
Satoru Nagai
悟 長井
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kurita Water Industries Ltd
Nippon Steel Nisshin Co Ltd
Original Assignee
Kurita Water Industries Ltd
Nisshin Steel Co Ltd
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 Kurita Water Industries Ltd, Nisshin Steel Co Ltd filed Critical Kurita Water Industries Ltd
Priority to JP58054785A priority Critical patent/JPS59179123A/en
Publication of JPS59179123A publication Critical patent/JPS59179123A/en
Publication of JPH0131434B2 publication Critical patent/JPH0131434B2/ja
Granted legal-status Critical Current

Links

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

  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Filtration Of Liquid (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PURPOSE:To treat efficiently captured substances at an intake of sea water by cleaning an obtd. filtrated after said substances are pressed and dehydrated. CONSTITUTION:Jellyfishes 10 captured at an intake of sea water are put in a dehydrating basket 12 to drain off sea water and slurried by a pulverizer 14. The jellyfish slurry is sent to a press dehydrator 16 and separated into solid substances and a filtrate. Since a large amount of org. components are contained in the flitrate from the dehydrator 16, the filtrate is sent to an oxidation tank 18, a flocculation tank 20, a dechlorination tank 22, an activated-carbon treating tank 24 and cleaned. Until the discharging standard is satisfied, the filtrate is treated and then discharged. As a result, captured substances at an intake of sea water such as jellyfishes are treated efficiently, and further it does not generate secondary pollution.

Description

【発明の詳細な説明】 本発明は、くらげ叫の海水取水口捕捉物の処理装置に関
する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an apparatus for processing jellyfish caught at a seawater intake.

製鉄所あるいは発電所など大量の海水を利用する施設で
は、海水の取水口のスクリーンに、くらげや海藻々ど浮
遊性の海洋生物が捕捉され、これらを処理する必要があ
った。特にくらげは夏場に異常繁殖し、取水口のスクリ
ーンによって1日に数十トンも捕捉される。従来、滓渣
としてのくらげは地面に掘った穴に放置して置かれたが
、夏場には葉が多いことも相俟って、魚の腐敗したよう
な臭気が発生するとともに、その投棄箇所から汚水が流
出するという不都合があった。
At facilities that use large amounts of seawater, such as steel mills and power plants, floating marine organisms such as jellyfish and seaweed are trapped on the screens at the seawater intake, and these must be disposed of. Jellyfish in particular proliferate abnormally in the summer, and tens of tons of jellyfish are captured each day by screens at water intakes. Traditionally, jellyfish were left as waste in holes dug in the ground, but in the summer, when there are many leaves, a smell similar to rotting fish is emitted, and the place where the jellyfish is dumped smells. There was the inconvenience of sewage flowing out.

本発明はこのような不都合を改善することを目的とした
ものであシ、くらげ等の捕捉物を効率よく処理すること
のできる処理装置を提供することを目的とする。
The present invention is aimed at improving such inconveniences, and it is an object of the present invention to provide a processing device that can efficiently process captured objects such as jellyfish.

すなわち、本発明の海水取水口捕捉物の処理装置は、く
らげ等の浮遊生物を主とする海水取水口捕捉物を処理す
る装置であって、該捕捉物を固形分と水分とに分離する
だめの圧搾脱水手段と、該圧搾脱水から得られた戸液を
浄化するだめの処理手段とを含むことを特徴とする。
That is, the seawater intake capture material processing apparatus of the present invention is an apparatus for processing seawater intake capture material mainly containing floating organisms such as jellyfish, and is a device for processing the seawater intake capture material, which is mainly composed of floating organisms such as jellyfish, and is a device for processing the seawater intake capture material, which separates the captured material into solid content and moisture. The present invention is characterized in that it includes a compression dehydration means, and a treatment means for purifying the liquid obtained from the compression dehydration.

以下、本発明の実施の態様について、第1図に沿ってさ
らに詳細に説明する。海水取水口で捕捉されたくらげ1
0(海草等の他の浮遊物も含まれるが、以下くらげとよ
ぶ。)は、先ず、脱水かと12に入れられて海水を水切
シされ、ついで、粉砕機14によってスラリー化したの
ち、圧搾脱水機16に送られる。くらげを捕捉したのち
、直接、圧搾脱水することも可能であるが、脱水効率を
高めるためには、この工程に先立ってスラリー状に粉砕
したシ、するいは小片状に切断するなど破砕手段を設け
ることが好ましい。また、くらげを圧搾脱水機に移送す
るには、スラリー状であれば移送が容易になる。
Hereinafter, embodiments of the present invention will be described in more detail with reference to FIG. Jellyfish caught at seawater intake 1
0 (hereinafter referred to as jellyfish, although other floating substances such as seaweed are included) are first placed in a dehydrator 12 to drain the seawater, then made into a slurry by a crusher 14, and then compressed and dehydrated. Sent to machine 16. After capturing the jellyfish, it is possible to directly compress and dehydrate them, but in order to increase the dehydration efficiency, it is necessary to crush the jellyfish prior to this process, such as by crushing them into a slurry or cutting them into small pieces. It is preferable to provide Furthermore, in order to transfer the jellyfish to a press-dehydrator, it is easier to transfer the jellyfish if it is in the form of a slurry.

なお、くらげは軟らかいので、破砕手段として特別なも
のは必要なく、たとえば、ポンプの羽根にカッター機能
を持たせたものやインラインミキサなどで十分である。
Since jellyfish are soft, no special crushing means is required; for example, a pump blade with a cutter function or an in-line mixer will suffice.

圧搾脱水機16としては、フィルタープレスなど圧搾式
のものであればいずれも用いられ、ベルトプレス型など
も採用できる。
As the compression dehydrator 16, any compression type device such as a filter press can be used, and a belt press type can also be used.

圧・搾脱水機16で、くらげスラリーは固形物とp液と
に固液分離される。同形物は焼却してもよく、場合によ
っては、埋立用資材、動物飼料などに利用することもで
きる。
The jellyfish slurry is solid-liquid separated into solid matter and p-liquid in the press/squeezer 16. Isomorphic materials may be incinerated and, in some cases, may be used as landfill materials, animal feed, etc.

脱水機16からの炉液は多量の有機成分を含み、浄化処
理手段により放流基準を満足する値捷で処理したのち放
流される。第1図の70−シートでは、脱水F液の有機
物分解処理を、次亜塩素酸ナトリウムを用いる化学的酸
化処理で行なう場合について示している。先ずP液は酸
化処理槽18に送られ、ここでpHを中性付近に保持し
て次亜塩素酸ナトリウムによシ酸化処理がなされる。酸
化処理済の液は、凝集処理槽20に送られ、SSが除去
される。凝集処理槽20では、ポリ塩化アルミニウム(
PAC)あるいは高分子凝集剤、凝集助剤が添加され、
凝集分離は公知の凝集分離装置を用いることができる。
The furnace liquid from the dehydrator 16 contains a large amount of organic components, and is discharged after being treated by a purification treatment means at a value that satisfies discharge standards. Sheet 70 in FIG. 1 shows a case where the organic matter decomposition treatment of the dehydrated F liquid is carried out by chemical oxidation treatment using sodium hypochlorite. First, the P solution is sent to the oxidation treatment tank 18, where the pH is maintained near neutrality and oxidation treatment is performed using sodium hypochlorite. The oxidized liquid is sent to the coagulation treatment tank 20, where SS is removed. In the coagulation treatment tank 20, polyaluminum chloride (
PAC) or a polymer flocculant or flocculation aid is added,
A known coagulation separation device can be used for coagulation separation.

凝集固形物は、脱水後、焼却その他の適当な処理が施さ
れる。
After dehydration, the aggregated solids are incinerated or otherwise subjected to appropriate treatment.

凝集処理%20からの清澄液は、脱塩素榴22に送られ
て、残留塩素除去処理がなされる。
The clarified liquid from the flocculation process %20 is sent to the dechlorination process 22 and treated to remove residual chlorine.

この処理は、ニッケル触媒を用いて簡単に行なえるが、
その他の公知の処理方法も採用できる。
This treatment can be easily carried out using a nickel catalyst, but
Other known processing methods can also be employed.

残留塩素が除去された液は、ついで活性炭処理槽24に
送られ、さらに仕上げ処理がなされる。活性炭処理は、
液に粉末活性炭を添加混合し、液中のCOD成分を活性
炭に吸着除去させたのち、活性炭を分離することにより
行なわれ、処理液は放流される。活性炭吸着処理は、粉
末活性炭を充填した塔に通液するなどの方法によっても
可能である。
The liquid from which residual chlorine has been removed is then sent to the activated carbon treatment tank 24, where it is further subjected to finishing treatment. Activated carbon treatment is
This is done by adding and mixing powdered activated carbon to the liquid, allowing the activated carbon to adsorb and remove the COD components in the liquid, and then separating the activated carbon, and the treated liquid is discharged. Activated carbon adsorption treatment can also be performed by a method such as passing liquid through a column filled with powdered activated carbon.

なお、このように仕上処理として活性炭による吸着処理
を行なうときは、この処理により残留塩素も除去するこ
とができるので、脱塩素槽22を省略することもできる
。しかしながら、活性炭の負荷軽減のためには、上記の
フローによることが好ましい。
Note that when adsorption treatment using activated carbon is performed as a finishing treatment in this manner, residual chlorine can also be removed by this treatment, so the dechlorination tank 22 can be omitted. However, in order to reduce the load on activated carbon, it is preferable to follow the above flow.

本発明における酸化処理手段としては、活性汚泥を用い
る生物学的手段を用いることもできる。この場合、近く
に活性汚泥処理施設があるときは、それを利用すること
も可能である。
As the oxidation treatment means in the present invention, biological means using activated sludge can also be used. In this case, if there is an activated sludge treatment facility nearby, it is also possible to use it.

本発明のくらけの処理装置によれば、海水取水口に捕捉
された大量のくらげを効率よく処理することができ、し
かも、二次公害を引きおこすこともない。
According to the jellyfish processing device of the present invention, a large amount of jellyfish caught in the seawater intake can be efficiently processed without causing secondary pollution.

実施例 海水取水口のスクリーンで捕捉したくらげを脱水かごで
水切りし、粉砕機で粉砕し、ついで、ポリプロピレン製
のp布(PP25F、通気度;900〜1080 cc
、 (crl)−1・m1n−’)に挾んで、7、0 
Kg / crAの圧力で脱水した。脱水ケーキはゴム
状で含水率78.2〜87.3チであシ、少量の重油を
用いることによシ十分に焼却することができた。
Example: The jellyfish caught on the screen of the seawater intake port was drained in a dehydration basket, crushed in a crusher, and then crushed in polypropylene P cloth (PP25F, air permeability: 900-1080 cc).
, (crl)-1・m1n-'), 7,0
Dehydrated at a pressure of Kg/crA. The dehydrated cake was rubbery and had a water content of 78.2 to 87.3 degrees, and could be incinerated satisfactorily by using a small amount of heavy oil.

脱水機からは白濁した魚臭を呈するP液が得られた。こ
のF液は、pH; 7..7 、88 ; 75■/l
A cloudy P solution with a fish odor was obtained from the dehydrator. This F solution has a pH of 7. .. 7, 88; 75■/l
.

COD ; 253m9/l 、 TOC; 2161
1Q/lであった。
COD; 253m9/l, TOC; 2161
It was 1Q/l.

このろ液に、次亜塩素酸ナトリウム 有効塩素量12%
)をp液1を当だり 500 +l1lli’添加し、
硫酸を用いて液のpHを7.0に調整しながら30分間
保持した。
Add sodium hypochlorite to this filtrate, effective chlorine amount 12%.
) is added per p solution 1 500 +l1lli',
The pH of the solution was adjusted to 7.0 using sulfuric acid and held for 30 minutes.

ついで、この次亜塩素酸ナトリウム処理液に、ハ 右下に残留塩素を除去したのち、液1を当たシ500ダ
の粉末活性炭を添加混合し、30分経過後のCODを測
定したところ、4omg/l までになっていた。この
値は放流基準を満足するものである。
Next, after removing the residual chlorine in the lower right corner of this sodium hypochlorite treatment solution, 500 dah powdered activated carbon that had been applied with solution 1 was added and mixed, and the COD was measured after 30 minutes. It was up to 4omg/l. This value satisfies the discharge standards.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明の実施例を示すフロー図である。 FIG. 1 is a flow diagram showing an embodiment of the present invention.

Claims (1)

【特許請求の範囲】 1、くらげ等の浮遊生物を主とする海水取水口捕捉物を
処理する装置であって、該捕捉物を同形分と水分とに分
離するための圧搾脱水手段と、該圧搾脱水手段から得ら
れたF液を浄化するための処理手段とを含むことを特徴
とする海水取水口捕捉物の処理装置。 2 前記圧搾処理手段に捕捉物を破砕して供給する破砕
手段を備えた%許請求の範囲第1項記載の処理装置。 3、 前記浄化するだめの処理手段が次亜塩素酸塩を用
いる化学的酸化処理手段である特許請求の範囲第1項ま
たは第2項に記載の処理装置。 4、 前記浄化するための処理手段が生物学的酸化処理
手段である特許請求の範囲第1項または第2項に記載の
処理装置。
[Scope of Claims] 1. An apparatus for processing seawater intake trapped matter mainly consisting of floating organisms such as jellyfish, which comprises compressing dewatering means for separating the trapped matter into isomorphic components and moisture; 1. A processing device for seawater intake trapped matter, comprising processing means for purifying liquid F obtained from the compression dewatering means. 2. The processing apparatus according to claim 1, further comprising crushing means for crushing and supplying the captured material to the compression processing means. 3. The treatment apparatus according to claim 1 or 2, wherein the treatment means for the purifying basin is a chemical oxidation treatment means using hypochlorite. 4. The processing apparatus according to claim 1 or 2, wherein the processing means for purification is a biological oxidation processing means.
JP58054785A 1983-03-30 1983-03-30 Treating apparatus of captured substance such as jellyfish at intake of sea water Granted JPS59179123A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58054785A JPS59179123A (en) 1983-03-30 1983-03-30 Treating apparatus of captured substance such as jellyfish at intake of sea water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58054785A JPS59179123A (en) 1983-03-30 1983-03-30 Treating apparatus of captured substance such as jellyfish at intake of sea water

Publications (2)

Publication Number Publication Date
JPS59179123A true JPS59179123A (en) 1984-10-11
JPH0131434B2 JPH0131434B2 (en) 1989-06-26

Family

ID=12980410

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58054785A Granted JPS59179123A (en) 1983-03-30 1983-03-30 Treating apparatus of captured substance such as jellyfish at intake of sea water

Country Status (1)

Country Link
JP (1) JPS59179123A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0448986A (en) * 1990-06-19 1992-02-18 Ube Ind Ltd Method and apparatus for dehydration and solidification treatment of jellyfish
JPH053769A (en) * 1991-10-17 1993-01-14 Hitachi Zosen Mukoujima Marine Kk Method of dehydrating jellyfish and device therefor
JPH05185065A (en) * 1992-01-16 1993-07-27 Shiyain Denshi Kk Treatment of jellyfish
CN104445734A (en) * 2014-11-25 2015-03-25 中国矿业大学(北京) Method and device for removing residual aluminum in mine water
JP2016067979A (en) * 2014-09-29 2016-05-09 電源開発株式会社 Volume reduction processing method for jellyfish waste and volume reduction processing device for jellyfish waste

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4624034B2 (en) * 2004-07-16 2011-02-02 克治 甲斐田 Jellyfish dehydration method and apparatus

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5746909A (en) * 1980-09-05 1982-03-17 Sogo Yatsukou Kk Inhibitor for dandruff

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5746909A (en) * 1980-09-05 1982-03-17 Sogo Yatsukou Kk Inhibitor for dandruff

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0448986A (en) * 1990-06-19 1992-02-18 Ube Ind Ltd Method and apparatus for dehydration and solidification treatment of jellyfish
JPH053769A (en) * 1991-10-17 1993-01-14 Hitachi Zosen Mukoujima Marine Kk Method of dehydrating jellyfish and device therefor
JPH0794031B2 (en) * 1991-10-17 1995-10-11 日立造船向島マリン株式会社 Jellyfish dehydration treatment equipment
JPH05185065A (en) * 1992-01-16 1993-07-27 Shiyain Denshi Kk Treatment of jellyfish
JP2016067979A (en) * 2014-09-29 2016-05-09 電源開発株式会社 Volume reduction processing method for jellyfish waste and volume reduction processing device for jellyfish waste
CN104445734A (en) * 2014-11-25 2015-03-25 中国矿业大学(北京) Method and device for removing residual aluminum in mine water

Also Published As

Publication number Publication date
JPH0131434B2 (en) 1989-06-26

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