JPS6232993B2 - - Google Patents

Info

Publication number
JPS6232993B2
JPS6232993B2 JP55030235A JP3023580A JPS6232993B2 JP S6232993 B2 JPS6232993 B2 JP S6232993B2 JP 55030235 A JP55030235 A JP 55030235A JP 3023580 A JP3023580 A JP 3023580A JP S6232993 B2 JPS6232993 B2 JP S6232993B2
Authority
JP
Japan
Prior art keywords
red tide
polymer
red
plankton
quaternary ammonium
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.)
Expired
Application number
JP55030235A
Other languages
Japanese (ja)
Other versions
JPS56126480A (en
Inventor
Yasuo Yamamoto
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.)
Toagosei Co Ltd
Original Assignee
Toagosei 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 Toagosei Co Ltd filed Critical Toagosei Co Ltd
Priority to JP3023580A priority Critical patent/JPS56126480A/en
Publication of JPS56126480A publication Critical patent/JPS56126480A/en
Publication of JPS6232993B2 publication Critical patent/JPS6232993B2/ja
Granted legal-status Critical Current

Links

Description

【発明の詳細な説明】 本発明は一定海域に発生した赤潮の有効な回収
方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an effective method for recovering red tide generated in a certain sea area.

近年、産業活動の発展による産業廃水の増加、
都市の発展による都市下水の増加等に伴い、窒素
化合物、燐化合物その他の栄養物質が、内湾、内
海に流入して赤潮発生の好条件を作り出してい
る。瀬戸内海、伊勢湾を始めとする各地の内海、
内湾は積年の努力による養殖技術の向上により、
ハマチ、アコヤ貝、アワビ、のり、等の養殖漁業
は飛躍的な発展をとげ、漁業全体における比重も
大きくなつてきたが、この赤潮の発生により、莫
大な損害をうけ、養殖漁業が危機に瀕しているこ
とは周知の事実である。
In recent years, industrial wastewater has increased due to the development of industrial activities.
As urban sewage increases due to urban development, nitrogen compounds, phosphorus compounds, and other nutrients flow into inner bays and seas, creating favorable conditions for the occurrence of red tide. The Seto Inland Sea, Ise Bay, and other inland seas,
The inner bay has improved through years of efforts to improve aquaculture technology.
Aquaculture fisheries for yellowtail, pearl oysters, abalone, seaweed, etc. have made rapid progress, and their weight in the overall fishing industry has increased, but due to the occurrence of red tide, the aquaculture fisheries have suffered huge losses and are in danger. It is a well-known fact that they are doing so.

赤潮は、ある種のプランクトンが限られた水域
で爆発的な大繁殖を行なつたために、海水が変色
し、多くは濁つて粘性を帯び、ときには臭気を発
して、数日間あるいは数十日間も持続する現象で
あるが、現在でも、その発生を防ぐすべがないの
はもちろん、発生後に於いても、その有効な処理
方法を持たず、一度発生すると、自然消滅するの
をただ待つだけであつた。
Red tide occurs when a certain type of plankton breeds explosively in a limited area of water, causing the seawater to change color, become cloudy and viscous, and sometimes emit an odor that lasts for several days or even tens of days. Although it is a persistent phenomenon, there is currently no way to prevent it from occurring, and even after it occurs, there is no effective way to deal with it, and once it occurs, we simply wait for it to disappear naturally. Ta.

赤潮の原因となるプランクトンの種類は、場
所、時期により同一ではなく、赤色細菌、らん藻
類、けい藻類、ベン毛藻類、繊毛虫類、甲殻類な
どであるが、ベン毛藻類が最も普通である。これ
に属するものとしてゴニアウラスク、ギムノデイ
ニウム、グレノデイニウム、ケラテイウム、ペリ
デイニウムなどが、赤潮主成分として有名であ
る。これらを主とする数十ミクロンのプランクト
ン類が海水、あるいは淡水中に、1c.c.当り数千か
ら数万個も分散して存在している為、水が赤くな
るのが赤潮である。赤潮対策の一つに、一度発生
した赤潮を漁業被害が発生する前に回収する方法
が考えられる。赤潮回収は懸濁物質濃度の低い海
水中からできるだけ有効に懸濁物質を回収するこ
とを目的とする。したがつて、技術的には一般の
濁水を対象とした水処理技術と共通する点が多
い。処理方法としては、赤潮を高分子凝集剤で凝
集、濃縮したのち、回収する方法が考えられる。
しかしながら一般の濁水の処理に比べると赤潮の
処理は極めて難しい。その理由は赤潮中の懸濁物
質濃度が一般の濁水のそれに比べて希薄であり、
更には、塩濃度が高い為一般の濁水処理用の凝集
剤では凝集反応が円滑に起らなかつたり、また凝
集してもフロツク強度が弱くてすぐこわれてしま
い、有効に濃縮回収ができない点にある。
The types of plankton that cause red tides vary depending on location and time of year; they include red bacteria, cyanobacteria, diatoms, algae, ciliates, and crustaceans, but algae are the most common. . Goniaurusk, gymnodenium, glenodeinium, kerateium, peridainium, etc. are famous as the main components of red tide. These plankton, which are mainly tens of microns in size, are dispersed in seawater or freshwater in the numbers of thousands to tens of thousands per c.c., causing the water to turn red during red tide. One possible measure against red tide is to collect red tide once it occurs before it causes damage to fisheries. The purpose of red tide collection is to collect suspended solids as effectively as possible from seawater where the concentration of suspended solids is low. Therefore, technically there are many points in common with water treatment technologies for general turbid water. A possible treatment method is to collect the red tide after coagulating and concentrating it with a polymer flocculant.
However, treating red tide is extremely difficult compared to treating general turbid water. The reason for this is that the concentration of suspended solids in red tide is lower than that in general turbid water.
Furthermore, due to the high salt concentration, the flocculation reaction cannot occur smoothly with common flocculants for turbid water treatment, and even if flocculation occurs, the floc strength is weak and breaks easily, making it impossible to concentrate and recover effectively. be.

赤潮は微生物からなるものであるから、これの
凝集にはカチオン性ポリマーが有効であるが、従
来のカチオン性ポリマーは塩濃度が海水のように
高い場合にはその凝集力が低下してしまい、実用
に供し得なかつた。赤潮の回収システムの確立及
びその事業化が漁業関係者から強く望まれていな
がら、実現できなかつた理由の一つには、海水中
で赤潮中の懸濁物質を有効かつ強力に凝集、濃縮
できる高分子凝集剤がなかつた事が挙げられる。
Red tide is made up of microorganisms, so cationic polymers are effective in coagulating it, but conventional cationic polymers lose their cohesive power when the salt concentration is as high as seawater. It could not be put to practical use. Although the establishment of a red tide recovery system and its commercialization have been strongly desired by fisheries officials, one of the reasons why this has not been possible is that suspended solids in red tide can be effectively and powerfully coagulated and concentrated in seawater. One of the reasons is that there was no polymer flocculant.

本発明者は海水のような高濃度の塩の存在下に
於いてもその凝集力が低下せず、赤潮を強力に凝
集できるようなカチオン性ポリマーを見い出すべ
く種々のポリマーを合成しテストを行ない検討を
重ねた結果、一般式〔〕で示される第4アンモ
ニウム塩を有するポリマーが優れている事を見出
した。この第4アンモニウム塩は一般にジアルキ
ルアミノアルキル(メタ)アクリレートをベンジ
ルハライドで4級化することにより得られるが、
現在一般に凝集剤として用いられているカチオン
性ポリマーの一つはベンジルハライドのかわりに
メチルハライドで4級化された第4アンモニウム
塩を有するものであり、これは比較例で明らか
なように赤潮の凝集性は極めて悪い。このように
類似の構造を有するポリマーでも第4アンモニウ
ム窒素に結合する官能基の違いにより赤潮の凝集
力の差が大きく、本発明のベンジル基を有するポ
リマーのみが極めて特異的に良好な凝集性能を示
すことができるという驚くべき事実を発見し、本
発明を完成するに至つた。
The present inventor synthesized various polymers and conducted tests in order to find a cationic polymer that can strongly coagulate red tide without decreasing its cohesive force even in the presence of highly concentrated salts such as seawater. As a result of repeated studies, it was discovered that a polymer having a quaternary ammonium salt represented by the general formula [] is superior. This quaternary ammonium salt is generally obtained by quaternizing dialkylaminoalkyl (meth)acrylate with benzyl halide,
One of the cationic polymers currently commonly used as a flocculant has a quaternary ammonium salt quaternized with methyl halide instead of benzyl halide, and as is clear from the comparative example, this has a strong effect on red tide. Cohesion is extremely poor. In this way, even polymers with similar structures have large differences in red tide cohesive strength due to differences in the functional groups bonded to the quaternary ammonium nitrogen, and only the benzyl group-containing polymer of the present invention exhibits very specific and good cohesive performance. We have discovered the surprising fact that it is possible to demonstrate this, and have completed the present invention.

即ち本発明は、プランクトン類の異常繁殖によ
つて生成した赤潮に、前記一般式〔〕で示され
る第4アンモニウム塩を一構成単位とするカチオ
ン性ポリマーを添加し、該プランクトン類を凝集
させたのち、回収することを特徴とする赤潮の回
収方法である。
That is, in the present invention, a cationic polymer having a quaternary ammonium salt represented by the general formula [] as one constituent unit is added to red tide generated due to abnormal proliferation of plankton, and the plankton is aggregated. This method of collecting red tide is characterized by collecting it later.

本発明に用いられるカチオン性ポリマーについ
てさらに具体的に説明する。
The cationic polymer used in the present invention will be explained in more detail.

一般式〔〕で示される第4アンモニウム塩の
代表例としては、例えば、ジメチルアミノエチル
アクリレート又はメタクリレート、ジエチルアミ
ノエチルアクリレート又はメタクリレート、ジメ
チルアミノプロピルアクリレート又はメタクリレ
ートなどを、ベンジルハライドで4級化された第
4アンモニウム塩をあげることができる。本発明
の凝集剤はこの第4アンモニウム塩を単独、ある
いは他の単量体と常法にしたがつて共重合させて
得ることができる。
Typical examples of quaternary ammonium salts represented by the general formula [] include dimethylaminoethyl acrylate or methacrylate, diethylaminoethyl acrylate or methacrylate, dimethylaminopropyl acrylate or methacrylate, etc., which are quaternized with benzyl halide. 4 ammonium salts can be mentioned. The flocculant of the present invention can be obtained by copolymerizing this quaternary ammonium salt alone or with other monomers in a conventional manner.

この場合、共重合性単量体としてはアクリルア
マイドが最も望ましく、その他N―ビニルピロリ
ドンなども使用出来る。かゝる単量体との共重合
割合は経済性および対象となる赤潮により任意に
調整することが出来るが、充分な性能を発揮する
為には上記第4アンモニウム塩が概ね10モル%以
上であることが望ましい。
In this case, the most preferred copolymerizable monomer is acrylamide, and other materials such as N-vinylpyrrolidone can also be used. The copolymerization ratio with such monomers can be arbitrarily adjusted depending on economic efficiency and the target red tide, but in order to exhibit sufficient performance, the quaternary ammonium salt must be approximately 10 mol% or more. It is desirable that there be.

本発明のポリマーを赤潮に添加、凝集させたの
ち濃縮、回収するが本発明ポリマーの添加量は赤
潮に対し5〜1000ppmが望ましい。濃縮、回収
方法としては例えば自然沈降させた後回収する方
法や遠心分離法、浮上分離法などの一般的な濁水
処理法を用いることができるが、赤潮中の懸濁物
質は海水と比重差があまりなく浮上し易いため、
浮上分離法を採用するのが望ましい。また本発明
によれば赤潮中の懸濁物質を90%以上回収するこ
とが可能である。
The polymer of the present invention is added to red tide, agglomerated, concentrated and recovered, and the amount of the polymer of the present invention added is preferably 5 to 1000 ppm relative to red tide. General turbid water treatment methods such as natural sedimentation followed by recovery, centrifugation, and flotation separation methods can be used for concentration and recovery, but suspended solids in red tide have a specific gravity different from that of seawater. Because there is not much and it is easy to float,
It is desirable to adopt flotation separation method. Furthermore, according to the present invention, it is possible to recover 90% or more of suspended solids in red tide.

次に実施例及び比較例をあげて本発明をさらに
具体的に説明する。
Next, the present invention will be explained in more detail with reference to Examples and Comparative Examples.

但し、以下の各例において対象とした赤潮は、
伊勢湾に異常発生したものであつて、顕微鏡観察
によると、主体は鞭毛藻類の一種であるギムノデ
イニウムより成つており、海水1c.c.当り約45000
個存在していた。液は若干粘性があり、また赤か
つ色に濁つていた。また、赤潮の懸濁物質の濃度
は13ppmであつた。
However, the red tide targeted in each of the following examples is
It is an abnormal occurrence in Ise Bay, and according to microscopic observation, it is mainly composed of Gymnodenium, a type of flagellate, and it is about 45,000 per c.c. of seawater.
There were several. The liquid was slightly viscous, red and cloudy in color. In addition, the concentration of suspended solids in red tide was 13 ppm.

実施例 1 赤潮を1のビーカーに500ml採取した。これ
に本発明のポリマー即ち、メタクリロイルオキシ
エチルジメチルベンジルアンモニウムクロライド
とアクリルアマイドのコポリマー(カチオン密度
2.8meq/gポリマー、0.5%ブルツクフイールド
粘度(BVと略)590cps)の0.1%水溶液を5ml添
加したのち、ジヤーテスターで100rpm、60秒間
撹拌した。赤潮成分は速かに凝集してフロツクを
形成し、撹拌停止と共にビーカーの底に沈降し
た。これを更に250rpmで2分間急速撹拌してフ
ロツクの破壊試験を行なつたが、フロツクはほと
んど壊れず、分離が容易であり、その濾液にも赤
色は残存せず無色透明であつた。
Example 1 500 ml of red tide was collected in a beaker. This is combined with the polymer of the present invention, a copolymer of methacryloyloxyethyldimethylbenzylammonium chloride and acrylamide (cation density
After adding 5 ml of a 0.1% aqueous solution of 2.8 meq/g polymer and 0.5% Bruckfield viscosity (BV) 590 cps), the mixture was stirred at 100 rpm for 60 seconds using a jar tester. The red tide components quickly aggregated to form a floc, which settled to the bottom of the beaker when stirring was stopped. This was further rapidly stirred at 250 rpm for 2 minutes to perform a floc destruction test, but the flocs were hardly broken and could be easily separated, and the filtrate was clear and colorless with no red remaining.

比較例 1 実施例1と同様のテストを従来のカチオン性ポ
リマー即ち、メタクリロイルオキシエチルトリメ
チルアンモニウムクロライドとアクリルアマイド
のコポリマー(カチオン密度3.0meq/gポリマ
ー、0.5%BV650cps)を用いて行なつた。赤潮成
分の凝集は実施例1に比較して遅く、フロツクを
形成したものの、ふわふわした弱いものであつ
た。また、250rpm、2分間の急速撹拌を行なつ
たところ、フロツクはほとんど壊れ液全体が赤か
つ色に戻つてしまい赤潮中の懸濁物質を分離、回
収することは出来なかつた。
Comparative Example 1 A test similar to Example 1 was conducted using a conventional cationic polymer, a copolymer of methacryloyloxyethyltrimethylammonium chloride and acrylamide (cation density 3.0 meq/g polymer, 0.5% BV 650 cps). The aggregation of the red tide components was slower than in Example 1, and although flocs were formed, they were fluffy and weak. Furthermore, when rapid stirring was performed at 250 rpm for 2 minutes, the flocs were almost destroyed and the entire liquid returned to its red color, making it impossible to separate and recover the suspended solids in the red tide.

実施例 2 実験用のフローテーシヨンテスターを用いて加
圧浮上分離テストを行なつた。浮上槽は内径100
mm、高さ500mmの透明アクリル樹脂製である。こ
れに赤潮3000mlを入れたのち、実施例1の本発明
のポリマーを20ppm添加した。これに槽の下か
ら3Kg/cm3に加圧した海水を800ml注入し加圧浮
上濃縮を行ない、浮上した赤潮のスカムを回収し
分析したところ96%の回収率であつた。
Example 2 A pressure flotation separation test was conducted using an experimental floatation tester. The flotation tank has an inner diameter of 100
Made of transparent acrylic resin with a height of 500 mm. After adding 3000 ml of red tide to this, 20 ppm of the polymer of the present invention of Example 1 was added. 800 ml of seawater pressurized to 3 kg/cm 3 was injected from the bottom of the tank to carry out pressure flotation concentration, and the red tide scum that floated to the surface was collected and analyzed, and the recovery rate was 96%.

比較例 2 実施例2において比較例1の従来のポリマーを
用いてまつたく同じ実験を行なつたところ回収率
は30%であつた。またポリマーを添加せずにテス
トしたところ回収率は12%であつた。
Comparative Example 2 When the same experiment was conducted in Example 2 using the conventional polymer of Comparative Example 1, the recovery rate was 30%. When tested without adding polymer, the recovery rate was 12%.

Claims (1)

【特許請求の範囲】 1 プランクトン類の異常繁殖により生成した赤
潮に 一般式 (但し、Rは水素又はメチル基、R1及びR2
炭素数1〜4のアルキル基、Aは炭素数2〜4の
鎖状又は分枝した脂肪族の基、×(-)はアンモニウ
ム窒素と塩を生成する陰性の基である。)で示さ
れる第4アンモニウム塩を一構成単位とするカチ
オン性ポリマーを添加し、該プランクトン類を凝
集させたのち回収することを特徴とする赤潮の回
収方法。
[Claims] 1. General formula for red tide generated due to abnormal proliferation of plankton species (However, R is hydrogen or a methyl group, R 1 and R 2 are alkyl groups having 1 to 4 carbon atoms, A is a chain or branched aliphatic group having 2 to 4 carbon atoms, × (-) is ammonium A method for treating red tide characterized by adding a cationic polymer having a quaternary ammonium salt (a negative group that forms nitrogen and a salt) as one constituent unit and collecting the plankton after agglomerating them. Collection method.
JP3023580A 1980-03-12 1980-03-12 Red tide recovering method Granted JPS56126480A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3023580A JPS56126480A (en) 1980-03-12 1980-03-12 Red tide recovering method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3023580A JPS56126480A (en) 1980-03-12 1980-03-12 Red tide recovering method

Publications (2)

Publication Number Publication Date
JPS56126480A JPS56126480A (en) 1981-10-03
JPS6232993B2 true JPS6232993B2 (en) 1987-07-17

Family

ID=12298047

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3023580A Granted JPS56126480A (en) 1980-03-12 1980-03-12 Red tide recovering method

Country Status (1)

Country Link
JP (1) JPS56126480A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4948513A (en) * 1988-05-27 1990-08-14 W. R. Grace & Co.-Conn. Method for controlling overspray in paint spray booths

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS54121557A (en) * 1978-03-15 1979-09-20 Toa Gosei Chem Ind Coagulant
JPS54150380A (en) * 1978-05-19 1979-11-26 Kurita Water Ind Ltd Suspension flocculating treatment method
JPS54158058A (en) * 1978-06-02 1979-12-13 Hitachi Ltd Separation method for microbic culture product

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS54121557A (en) * 1978-03-15 1979-09-20 Toa Gosei Chem Ind Coagulant
JPS54150380A (en) * 1978-05-19 1979-11-26 Kurita Water Ind Ltd Suspension flocculating treatment method
JPS54158058A (en) * 1978-06-02 1979-12-13 Hitachi Ltd Separation method for microbic culture product

Also Published As

Publication number Publication date
JPS56126480A (en) 1981-10-03

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