JP2002001356A - Method and apparatus for treating service water - Google Patents

Method and apparatus for treating service water

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Publication number
JP2002001356A
JP2002001356A JP2000179918A JP2000179918A JP2002001356A JP 2002001356 A JP2002001356 A JP 2002001356A JP 2000179918 A JP2000179918 A JP 2000179918A JP 2000179918 A JP2000179918 A JP 2000179918A JP 2002001356 A JP2002001356 A JP 2002001356A
Authority
JP
Japan
Prior art keywords
water
activated carbon
polymer flocculant
acrylamide monomer
monomer
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.)
Pending
Application number
JP2000179918A
Other languages
Japanese (ja)
Inventor
Katsuyuki Kataoka
克之 片岡
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.)
Ebara Corp
Original Assignee
Ebara Corp
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 Ebara Corp filed Critical Ebara Corp
Priority to JP2000179918A priority Critical patent/JP2002001356A/en
Publication of JP2002001356A publication Critical patent/JP2002001356A/en
Pending legal-status Critical Current

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  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Water Treatment By Sorption (AREA)
  • Apparatus Associated With Microorganisms And Enzymes (AREA)
  • Immobilizing And Processing Of Enzymes And Microorganisms (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method and an apparatus for treating by which acryl amide is not residued in service water by almost completely removing the acryl amide in a synthetic organic high molecular flocculating agent changed in the service water. SOLUTION: After acryl amide monomer is biologically degraded and adsorbed on activated carbon to be removed by coexisting an acryl amide monomer degradable bacteria sticking powdery activated carbon and stirring at the time of preparing the high molecular flocculating agent aqueous solution having a prescribed concentration by adding the polyacryl amide based synthetic organic high molecular flocculating agent into water and stirring, the high molecular flocculating agent aqueous solution, in which the powdery activated carbon is suspended, is charged into a flocculation separation process flow-in water in the service water treatment to perform the flocculation separation of the service water to be treated and the adsorption of organic materials in the raw water simultaneously.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、上水処理の凝集処
理に使用するポリアクリルアミド系合成有機高分子凝集
剤中の有害なアクリルアミドモノマーの除去と、上水処
理原水中のかび臭物質、フミン酸、農薬などの有機物の
除去を同時に行える新規な上水処理方法、及び処理装置
に関する。
TECHNICAL FIELD The present invention relates to the removal of harmful acrylamide monomers in a polyacrylamide-based synthetic organic polymer flocculant used for coagulation treatment of water treatment, and to remove musty odor substances and humic acid in raw water treated with water treatment. The present invention relates to a novel water treatment method and a treatment device capable of simultaneously removing organic substances such as agricultural chemicals.

【0002】[0002]

【従来の技術】上水処理対象原水中の懸濁質、溶存有機
物を除去するために、従来から広く凝集処理が行われて
いる。上水処理における凝集処理では、凝集剤として硫
酸アルミニウム(硫酸バンド)、ポリ塩化アルミニウム
(PAC)が利用されている。これらの無機凝集剤は、
単独使用では十分大きなフロックが形成されないため、
凝集沈殿工程、砂濾過工程の固液分離速度が小さいとい
う欠点がある。特に、上水処理の原水の富栄養化が進
み、ミクロキスチスなどの藻類が多量に含まれる原水で
は、PACまたは硫酸バンドの添加では極めて沈降性の
悪いフロックしか形成されず、フロックが浮上してしま
うこともあり、藻類の効果的除去ができなくなるという
大きな問題点もあった。また、凝集分離工程から排出さ
れる汚泥の沈降濃縮および脱水性が悪いという欠点もあ
った。
2. Description of the Related Art In order to remove suspended solids and dissolved organic matter in raw water to be treated for water treatment, agglomeration treatment has been widely performed. In the coagulation treatment in the tap water treatment, aluminum sulfate (sulfuric acid band) and polyaluminum chloride (PAC) are used as coagulants. These inorganic coagulants are
Because a sufficiently large floc is not formed when used alone,
There is a disadvantage that the solid-liquid separation speed in the coagulation sedimentation step and the sand filtration step is low. In particular, eutrophication of raw water in water treatment is advanced, and in raw water containing a large amount of algae such as microcystis, addition of PAC or sulfate band forms only flocs with extremely poor sedimentation, and flocs float. In some cases, there was a big problem that the algae could not be effectively removed. There is also a disadvantage that sludge discharged from the coagulation separation step has poor sedimentation concentration and dewatering properties.

【0003】これらの欠点を解決するには、フロック形
成を促進するために、ポリアクリルアミド系合成有機高
分子凝集剤の使用が考えられるが、上水処理では有機高
分子凝集剤の安全性、即ち、合成有機高分子凝集剤に含
まれるアクリルアミドモノマーの毒性のため、我が国の
上水処理においては、従来から使用が公的に認可されて
いない状況にある。なお、平成12年4月から日本の浄
水処理にも厳しい条件付きでポリアクリルアミド系高分
子凝集剤の使用が公的に認可された。その条件とは、
「上水処理水中のアクリルアミドモノマー残存量が0.
00005mg/リットル以下」ということであり、こ
の規制の条件は高分子凝集剤中のモノマーの含有量をき
わめて低濃度「ポリマー有効成分1g当たりのモノマー
含有率として、0.01%以下」にしない限り、実際
上、高分子凝集剤を上水処理に使用できないほどの厳し
い条件である。
In order to solve these drawbacks, use of a polyacrylamide-based synthetic organic polymer flocculant is considered to promote floc formation. Due to the toxicity of the acrylamide monomer contained in the synthetic organic polymer flocculant, its use in water treatment in Japan has not been officially approved. The use of a polyacrylamide polymer flocculant was officially approved in April 2000 under strict conditions for water purification treatment in Japan. The condition is
"The residual amount of acrylamide monomer in the treated water is 0.
00005 mg / liter or less ", and the condition of this regulation is that unless the content of the monomer in the polymer flocculant is extremely low," the monomer content per 1 g of the polymer active ingredient is 0.01% or less ". In fact, the conditions are so severe that the polymer flocculant cannot be used for water treatment.

【0004】ポリアクリルアミド系合成有機高分子凝集
剤(以下、「合成ポリマー」と略記する)製品中に不可
避的に少量のアクリルアミドモノマーが残留する原因
は、以下の点に起因する。即ち、アクリルアミドモノマ
ーを重合させて、ポリアクリルアミドを製造する重合工
程で、反応の後期においてポリアクリルアミド重合体が
ゲル状となるため、分子拡散速度が悪化し、アクリルア
ミドモノマー同士の衝突数が悪化するため、モノマーを
100%重合させることは困難なことである。この結
果、ポリアクリルアミドを原水に添加すると、不可避的
に毒性のあるアクリルアミドモノマーが、上水中に残留
する結果となってしまうのである。なお、安全性に問題
がない天然高分子凝集剤であるアルギン酸ソーダ(昆布
から抽出される食物繊維の一種)は、合成有機高分子凝
集剤に比べて薬品コストが高く、しかもフロック形成効
果がポリアクリルアミド系高分子凝集剤に比べて著しく
小さいため、我が国の上水処理では利用されていない。
[0004] The reason why a small amount of acrylamide monomer inevitably remains in a polyacrylamide-based synthetic organic polymer flocculant (hereinafter abbreviated as "synthetic polymer") product is as follows. That is, in the polymerization step of polymerizing the acrylamide monomer to produce polyacrylamide, the polyacrylamide polymer becomes a gel in the latter stage of the reaction, so the molecular diffusion rate is deteriorated, and the number of collisions between the acrylamide monomers is deteriorated. It is difficult to polymerize 100% of the monomer. As a result, when polyacrylamide is added to raw water, toxic acrylamide monomers inevitably remain in tap water. In addition, sodium alginate (a kind of dietary fiber extracted from kelp), which is a natural polymer flocculant with no safety problems, has a higher chemical cost than synthetic organic polymer flocculants and has a floc-forming effect of poly. Since it is significantly smaller than acrylamide polymer flocculants, it is not used in water treatment in Japan.

【0005】[0005]

【発明が解決しようとする課題】本発明は、上記した従
来の問題点を解消するために、合成有機高分子凝集剤
(以下「高分子凝集剤」あるいは「ポリマー」と略すこ
とがある)中のアクリルアミドモノマーを使用時にほぼ
完全に(検出限界以下に)除去してから、合成有機高分
子凝集剤を上水処理対象水に注入し、上水処理水(飲料
水)にアクリルアミドモノマーが残留しないようにする
ことを目的とする。本発明は、このように、高分子凝集
剤中のモノマー残留問題を解決することによって、卓越
したフロック形成効果を持つ合成ポリマーを、上水処理
に安全に使用できるようにする、上水処理における凝集
処理技術を提供することを目的とするものである。
SUMMARY OF THE INVENTION The present invention provides a synthetic organic polymer flocculant (hereinafter sometimes abbreviated as "polymer flocculant" or "polymer") to solve the above-mentioned conventional problems. After completely removing the acrylamide monomer when using it (below the detection limit), the synthetic organic polymer flocculant is injected into the water to be treated for drinking water, and the acrylamide monomer does not remain in the treated water (drinking water) The purpose is to be. The present invention thus solves the problem of monomer residue in a polymer flocculant, thereby enabling a synthetic polymer having an excellent floc-forming effect to be used safely in water treatment. It is an object of the present invention to provide an agglomeration treatment technique.

【0006】[0006]

【課題を解決するための手段】本発明は、以下の技術思
想によって上記諸問題点を解決できたものである。即
ち、本発明は、以下の各構成からなる。 (1)ポリアクリルアミド系合成有機高分子凝集剤を水
に添加、撹拌して所定濃度の高分子凝集剤水溶液を調製
する際に、アクリルアミドモノマー分解菌付着粉末活性
炭を共存させて撹拌し、アクリルアミドモノマーを生物
分解すると共に活性炭への吸着によって除去した後、該
粉末活性炭を懸濁した高分子凝集剤水溶液を上水処理の
凝集分離工程流入水に注入し、上水処理対象原水の凝集
分離と原水中の有機物の活性炭への吸着を同時に行うこ
とを特徴とする上水処理方法。 (2)前記アクリルアミドモノマー分解菌付着粉末活性
炭が、アクリルアミドモノマー含有水に粉末活性炭を懸
濁させて曝気することにより得たものであることを特徴
とする前記(1)記載の上水処理方法。 (3)攪拌機を備え、ポリアクリルアミド系合成有機高
分子凝集剤の供給管、アクリルアミドモノマー分解菌付
着粉末活性炭の供給管及び高分子凝集剤溶液の排出管を
設けた高分子凝集剤溶解槽を有することを特徴とする上
水処理装置。
The present invention has solved the above-mentioned problems by the following technical concept. That is, the present invention includes the following configurations. (1) When a polyacrylamide-based synthetic organic polymer flocculant is added to water and stirred to prepare a polymer flocculant aqueous solution having a predetermined concentration, the acrylamide monomer-decomposing bacterium-attached powder activated carbon is coexistent and stirred, and the acrylamide monomer is stirred. After biodegradation and removal by adsorption on activated carbon, the aqueous solution of the polymer flocculant in which the powdered activated carbon is suspended is poured into the influent water of the coagulation / separation step of water treatment, and the coagulation separation and raw A water treatment method characterized by simultaneously adsorbing organic matter in water to activated carbon. (2) The water treatment method according to the above (1), wherein the powdered activated carbon adhering to acrylamide monomer-degrading bacteria is obtained by suspending powdered activated carbon in water containing acrylamide monomer and aerating the suspension. (3) A polymer flocculant dissolving tank equipped with a stirrer and provided with a supply pipe for a polyacrylamide-based synthetic organic polymer flocculant, a supply pipe for acrylamide monomer-degrading bacteria-adhered powdered activated carbon, and a discharge pipe for a polymer flocculant solution. Water treatment equipment characterized by the above-mentioned.

【0007】[0007]

【発明の実施の形態】図1に本発明の上水処理方法を実
施する処理装置の構成例を示す。以下、図1を参照しな
がら、最も代表的な合成有機高分子凝集剤である粉末状
ポリアクリルアミドを使用する場合について説明する。
浄水場に配置した高分子凝集剤溶解槽1に水2を所定の
水位になるまで供給し、モータ3を駆動して撹拌羽根4
を回転させながら、高分子凝集剤5としてポリアクリル
アミド高分子凝集剤の粉末を供給して溶解しつつ、更
に、モノマー分解菌付着粉末活性炭6を所定量添加す
る。得られた高分子凝集剤溶液7は取り出して凝集処理
槽(図示せず)へ送る。モノマー分解菌は、種々の固体
の中で粉末活性炭に最も付着固定化され易いことがわか
った。アクリルアミドモノマー分解菌は、アクリルアミ
ドモノマーを分解する微生物のことである。これまで
に、分解菌としてはブレビバクテリウム(Brevib
akuterium)属、ノカルジア(Nocardi
a)属、シュードモナス(Pseudomonas)属
細菌、放線菌が知られているが、本発明でいうアクリル
アミドモノマー分解菌は、これらいずれの菌であっても
よく、またアクリルアミドモノマー分解能を有していれ
ば、特にこれらの菌に限定されるものでもない。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 shows an example of the configuration of a treatment apparatus for carrying out the water treatment method of the present invention. Hereinafter, the case of using powdered polyacrylamide, which is the most typical synthetic organic polymer flocculant, will be described with reference to FIG.
Water 2 is supplied to a polymer flocculant dissolving tank 1 disposed in a water purification plant until a predetermined water level is reached, and a motor 3 is driven to agitate the stirring blades 4.
While rotating, a powder of polyacrylamide polymer flocculant as the polymer flocculant 5 is supplied and dissolved, and a predetermined amount of powdered activated carbon 6 adhering to monomer-degrading bacteria is further added. The obtained polymer flocculant solution 7 is taken out and sent to a flocculation treatment tank (not shown). It was found that among the various solids, the monomer-degrading bacteria were most easily adhered and immobilized on powdered activated carbon. Acrylamide monomer-degrading bacteria are microorganisms that degrade acrylamide monomers. So far, Brevibacterium (Brevibacterium) has been used as a decomposing bacterium.
akuterium, Nocardi
a) The genus, Pseudomonas genus bacteria and actinomycetes are known, and the acrylamide monomer-degrading bacteria referred to in the present invention may be any of these bacteria, provided that they have the ability to degrade acrylamide monomers. However, the present invention is not particularly limited to these bacteria.

【0008】このようにして配合された、モノマー分解
菌付着粉末活性炭懸濁水を撹拌しながら、ポリアクリル
アミド(高分子凝集剤)の粉末をママコ(継粉)になら
ないように、少量ずつ添加して、0.1%(w/v)濃
度程度になるように十分に分散させる。上記の十分な分
散状態において、さらに撹拌を継続すると、高分子凝集
剤の粉末は徐々に溶解し始め、白色粉末が水を吸収して
透明なゲル状粒子になり、このゲルからアクリルアミド
モノマーが徐々に溶け出し始めるようになる。溶出した
アクリルアミドモノマーは、活性炭付着菌によって、速
やかに生物分解され、一部は活性炭に吸着される。
[0008] While stirring the suspension of the activated carbon suspension powder adhering to the monomer-decomposed bacteria thus mixed, a powder of polyacrylamide (polymer flocculant) is added little by little so as not to form mamako (split powder). , 0.1% (w / v). In the above-mentioned sufficiently dispersed state, when stirring is further continued, the powder of the polymer flocculant gradually starts to dissolve, the white powder absorbs water to form transparent gel-like particles, and the acrylamide monomer is gradually removed from the gel. Begin to melt into the water. The eluted acrylamide monomer is rapidly biodegraded by activated carbon-adhering bacteria, and a part of the acrylamide monomer is adsorbed on activated carbon.

【0009】このような状態において、1〜2時間程度
撹拌を継続すると、高分子凝集剤は完全に溶解し、透明
ゲル粒子も消失し、アクリルアミドモノマーもほぼ完全
に分解消失する。なお、あらかじめ高分子凝集剤製品に
モノマー分解菌固定化粉末活性炭を混合しておき、これ
を上水場において水に懸濁させ、ポリマーを溶解するよ
うにしてもよい。アクリルアミドモノマーの微生物分解
に必要な時間は、高分子凝集剤中のアクリルアミドモノ
マーの含有量、高分子凝集剤の溶解濃度、水温および微
生物付着粉末活性炭添加量に対応して変化する。
In such a state, when stirring is continued for about 1 to 2 hours, the polymer flocculant is completely dissolved, the transparent gel particles disappear, and the acrylamide monomer is almost completely decomposed and disappears. Alternatively, powdered activated carbon immobilized with the monomer-degrading bacteria may be mixed in advance with the polymer flocculant product, and this may be suspended in water in a waterworks to dissolve the polymer. The time required for the biodegradation of the acrylamide monomer varies depending on the content of the acrylamide monomer in the polymer flocculant, the dissolution concentration of the polymer flocculant, the water temperature, and the amount of the activated carbon added to the microorganism-adhered powder.

【0010】本発明者の実験によると、ポリアクリルア
ミド粉末を水温20℃の水に0.1%(w/v)濃度で
分散させてから、微生物付着活性炭を10000mg/
リットル程度添加し、1〜2時間撹拌するとアクリルア
ミドモノマーは完全に分解されることが認められた。微
生物付着活性炭の添加量としては少ない方がコストが小
さいが、原水と十分接触させるためにはある程度の量を
必要とし、1000〜20000mg/リットルの範囲
とすることが好ましい。この結果から、本発明による場
合には、アクリルアミドモノマーが完全に、もしくは高
度に除去された高分子凝集剤と粉末活性炭を原水に注入
できることになる。上記のアクリルアミドモノマーが完
全に、もしくは高度に除去された高分子凝集剤の水溶液
には、粉末活性炭が共存しているので、上水処理工程に
注入すると、フロック形成促進効果をもたらすと共に、
上水処理原水中のトリハロメタン前駆物質、農薬および
環境ホルモン等の他にかび臭が、粉末活性炭に吸着され
るという複合効果がある。
According to the experiment of the present inventor, after dispersing polyacrylamide powder in water at a water temperature of 20 ° C. at a concentration of 0.1% (w / v), 10,000 mg / w
When about 1 liter was added and stirred for 1 to 2 hours, it was confirmed that the acrylamide monomer was completely decomposed. The smaller the amount of the microorganism-attached activated carbon, the lower the cost. However, a certain amount is required in order to make sufficient contact with the raw water, and the amount is preferably in the range of 1,000 to 20,000 mg / liter. From this result, in the case of the present invention, the polymer flocculant and the powdered activated carbon from which the acrylamide monomer has been completely or highly removed can be injected into the raw water. In the aqueous solution of the polymer flocculant from which the acrylamide monomer has been completely or highly removed, powdered activated carbon coexists.
There is a combined effect that musty odor besides trihalomethane precursors, pesticides, environmental hormones and the like in raw water treated water is absorbed by powdered activated carbon.

【0011】[0011]

【実施例】以下において、実施例により本発明をより具
体的に説明するが、本発明はこの実施例により制限され
るものではない。
EXAMPLES Hereinafter, the present invention will be described more specifically with reference to examples, but the present invention is not limited to these examples.

【0012】実施例1(モノマー分解菌付着粉末活性炭
の製造) アクリルアミドモノマーを30mg/リットルで添加混
合した水道水に、粉末活性炭を10000mg/リット
ル、リンを10mg/リットルで添加混合し、さらに、
下水処理場から採取した活性汚泥を100mg/リット
ルで添加混合して、空気曝気を4週間継続した。この時
点で、粉末活性炭を遠心分離により除去した分離水のモ
ノマーの濃度は0.13mg/リットルであった。ま
た、分離した粉末活性炭を顕微鏡で観察した結果、やや
黄色の微生物が付着していた。
Example 1 (Production of powdered activated carbon adhering to monomer-decomposing bacteria) To tap water to which acrylamide monomer was added and mixed at 30 mg / l, powdered activated carbon was added at 10,000 mg / l, and phosphorus was added at 10 mg / l, and mixed.
The activated sludge collected from the sewage treatment plant was added and mixed at 100 mg / liter, and air aeration was continued for 4 weeks. At this point, the concentration of the monomer in the separated water from which the powdered activated carbon had been removed by centrifugation was 0.13 mg / liter. Further, as a result of observing the separated powdered activated carbon with a microscope, a slightly yellow microorganism was attached.

【0013】実施例2(ポリアクリルアミド水溶液中の
モノマー除去試験) 実施例1の方法によって得たモノマー分解菌付着粉末活
性炭を10000mg/リットル添加した水道水(水温
22℃)に、アニオン性ポリアクリルアミド粉末(モノ
マー含有量0.17%)を0.1%(w/v)濃度にな
るように、少量ずつ添加し2時間撹拌することにより溶
解したポリマー水溶液を調製した。得られたポリマー溶
解槽内水溶液におけるモノマー濃度は、上水試験法記載
のECDガスクロマトグラフィーによるアクリルアミド
モノマー分析法の検出限界(0.2ppm)以下であっ
た。一方、モノマー分解菌付着粉末活性炭を添加しない
水道水に上記ポリアクリルアミド粉末を0.1%(w/
v)濃度になるように添加し、2時間の撹拌継続で溶解
して得た高分子凝集剤水溶液中のアクリルアミドモノマ
ーの濃度は7.7mg/リットルであり、殆ど除去され
てはいなかった。
Example 2 (Monomer removal test in aqueous solution of polyacrylamide) [0013] Anionic polyacrylamide powder was added to tap water (water temperature: 22 ° C) containing 10,000 mg / liter of activated carbon to which monomer-decomposed bacteria obtained by the method of Example 1 was added. (Monomer content 0.17%) was added little by little to a concentration of 0.1% (w / v) and stirred for 2 hours to prepare a dissolved polymer aqueous solution. The monomer concentration in the obtained aqueous solution in the polymer dissolving tank was not more than the detection limit (0.2 ppm) of the acrylamide monomer analysis method by ECD gas chromatography described in the drinking water test method. On the other hand, the above-mentioned polyacrylamide powder was added in 0.1% (w /
v) The concentration of the acrylamide monomer in the aqueous solution of the polymer flocculant obtained by adding it to a concentration and dissolving it with continuous stirring for 2 hours was 7.7 mg / liter, and it was hardly removed.

【0014】実施例3(上水処理試験) A浄水場の原水を採水し、PACを30mg/リットル
添加して1分間撹拌後、本発明の粉末活性炭懸濁高分子
凝集剤(実施例2に同じ)を0.2mg/リットル添加
して1分間撹拌して凝集処理を行った。この結果、沈降
性が極めて大きなフロックが形成され、沈降速度は56
0m/minであった。また、原水中の溶解性色度13
度が、本発明高分子凝集剤による処理後に3度に減少し
た。さらに、凝集処理水のアクリルアミドモノマーを上
水試験法記載のECDガスクロマトグラフ法に従って分
析したところ、検出できなかった。なお、PACのみを
3mg/リットル添加した凝集処理水の色度は6度であ
った。また、形成したフロックの沈降速度は22mm/
minで著しく小であった。
Example 3 (Water treatment test) Raw water from water purification plant A was sampled, PAC was added at 30 mg / L, and the mixture was stirred for 1 minute, and then the powdered activated carbon suspended polymer flocculant of the present invention (Example 2) ) Was added, and the mixture was stirred for 1 minute to perform an aggregation treatment. As a result, a floc having extremely large sedimentation property is formed, and the sedimentation speed is 56
It was 0 m / min. In addition, the solubility chromaticity in raw water 13
The degree decreased to 3 degrees after the treatment with the polymer flocculant of the present invention. Furthermore, when the acrylamide monomer in the coagulated water was analyzed according to the ECD gas chromatography described in the water supply test method, no detection was possible. The chromaticity of the coagulated water to which only PAC was added at 3 mg / liter was 6 degrees. In addition, the sedimentation speed of the formed floc is 22 mm /
Min was extremely small.

【0015】[0015]

【発明の効果】本発明の上水処理方法及び処理装置によ
り、以下のような顕著な効果がもたらされる。 (イ)アクリルアミドモノマーが含まれる合成高分子凝
集剤から、モノマーを容易に、かつ高度に除去できるの
で、合成ポリマーを上水処理に安全に使用できる。 (ロ)卓越したフロック形成作用を持つアクリルアミド
系高分子凝集剤を上水処理に使用できるようになるた
め、凝集沈殿、濾過工程における固液分離速度を従来の
無機凝集剤単独使用時に比べ、大幅に向上でき、上水処
理プロセスを大幅に能率化できる。 (ハ)モノマーを除去する処理を行った高分子凝集剤の
水溶液中に、粉末活性炭が共存しているので、その高分
子凝集剤の水溶液をそのまま上水処理対象原水に加える
ようにしても、その際に上水処理対象原水中の各種微量
有機物、例えば、かび臭、色、農薬、フミン酸などを凝
集工程で除去することができる複合的な効果がもたらさ
れる。このことは、活性炭がアクリルアミドモノマー分
解菌の担体としての機能、上水原水からのかび臭気、
色、農薬およびフミン酸などの吸着除去機能という複合
機能を持つことに起因する。
According to the method and apparatus for treating clean water of the present invention, the following remarkable effects can be obtained. (A) Since the monomer can be easily and highly removed from the synthetic polymer flocculant containing the acrylamide monomer, the synthetic polymer can be safely used for water treatment. (B) Since an acrylamide polymer flocculant having an excellent floc-forming effect can be used for water treatment, the solid-liquid separation speed in the flocculation settling and filtration processes is significantly higher than when using the conventional inorganic flocculant alone. And the water treatment process can be greatly streamlined. (C) Since the powdered activated carbon coexists in the aqueous solution of the polymer flocculant that has been subjected to the treatment for removing the monomer, even if the aqueous solution of the polymer flocculant is added as it is to the raw water to be treated for water treatment, At this time, a combined effect is obtained in which various trace organic substances, for example, musty odor, color, pesticides, humic acid and the like in the raw water to be treated for water treatment can be removed in the coagulation step. This indicates that activated carbon functions as a carrier for acrylamide monomer-degrading bacteria, musty odor from raw water,
It has a combined function of removing color, pesticides and humic acid.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の処理方法を実施する装置の構成例を示
す概略図。
FIG. 1 is a schematic diagram showing a configuration example of an apparatus for performing a processing method of the present invention.

【符号の説明】[Explanation of symbols]

1 高分子凝集剤溶解槽 2 水 3 モータ 4 撹拌羽根 5 高分子凝集剤 6 モノマー分解菌付着粉末活性炭 7 高分子凝集剤溶液 Reference Signs List 1 polymer flocculant dissolution tank 2 water 3 motor 4 stirring blade 5 polymer flocculant 6 powdered activated carbon adhering to monomer decomposing bacteria 7 polymer flocculant solution

フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C12M 1/40 C12M 1/40 Z 4D062 C12N 1/00 C12N 1/00 R 11/14 11/14 Fターム(参考) 4B029 AA21 BB02 CC04 CC10 4B033 NA12 NA19 NB23 NB62 NB68 NC04 ND04 ND20 NE02 4B065 AA22X AA38X AA41X AC20 BA23 BB12 BC42 BD15 CA56 4D024 AA01 AB04 BA02 BB01 BC05 DB15 DB29 4D040 DD03 DD14 DD31 4D062 BA06 BA16 BA19 BB09 BB12 CA14 DA04 DB03 DC02 EA32Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat II (reference) C12M 1/40 C12M 1/40 Z 4D062 C12N 1/00 C12N 1/00 R 11/14 11/14 F term (reference) 4B029 AA21 BB02 CC04 CC10 4B033 NA12 NA19 NB23 NB62 NB68 NC04 ND04 ND20 NE02 4B065 AA22X AA38X AA41X AC20 BA23 BB12 BC42 BD15 CA56 4D024 AA01 AB04 BA02 BB01 BC05 DB15 DB29 BA03BA03 BA03 DA03 DD04 DD03 DD03 DD14 DD03 DD03 DD14 DD03 DD14 DD03

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 ポリアクリルアミド系合成有機高分子凝
集剤を水に添加、撹拌して所定濃度の高分子凝集剤水溶
液を調製する際に、アクリルアミドモノマー分解菌付着
粉末活性炭を共存させて撹拌し、アクリルアミドモノマ
ーを生物分解すると共に活性炭への吸着によって除去し
た後、該粉末活性炭を懸濁した高分子凝集剤水溶液を上
水処理の凝集分離工程流入水に注入し、上水処理対象原
水の凝集分離と原水中の有機物の活性炭への吸着を同時
に行うことを特徴とする上水処理方法。
1. When a polyacrylamide-based synthetic organic polymer flocculant is added to water and stirred to prepare a polymer flocculant aqueous solution of a predetermined concentration, stirring is carried out in the presence of activated carbon adhering to acrylamide monomer-degrading bacteria, After the acrylamide monomer is biodegraded and removed by adsorption to activated carbon, the aqueous solution of the polymer flocculant in which the powdered activated carbon is suspended is injected into the influent water of the coagulation / separation step of water treatment, and the coagulation / separation of raw water to be treated with water is carried out. And a method of treating organic water in raw water with activated carbon at the same time.
【請求項2】 前記アクリルアミドモノマー分解菌付着
粉末活性炭が、アクリルアミドモノマー含有水に粉末活
性炭を懸濁させて曝気することにより得たものであるこ
とを特徴とする請求項1記載の上水処理方法。
2. The water treatment method according to claim 1, wherein the powdered activated carbon adhering to acrylamide monomer-degrading bacteria is obtained by suspending powdered activated carbon in water containing acrylamide monomer and aerating the suspension. .
【請求項3】 攪拌機を備え、ポリアクリルアミド系合
成有機高分子凝集剤の供給管、アクリルアミドモノマー
分解菌付着粉末活性炭の供給管及び高分子凝集剤溶液の
排出管を設けた高分子凝集剤溶解槽を有することを特徴
とする上水処理装置。
3. A polymer flocculant dissolving tank equipped with a stirrer and provided with a supply pipe for a polyacrylamide-based synthetic organic polymer flocculant, a supply pipe for powdered activated carbon adhering to acrylamide monomer-degrading bacteria, and a discharge pipe for a polymer flocculant solution. A water treatment device comprising:
JP2000179918A 2000-06-15 2000-06-15 Method and apparatus for treating service water Pending JP2002001356A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Publication Number Publication Date
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Family

ID=18681100

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Country Status (1)

Country Link
JP (1) JP2002001356A (en)

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