JP2003200183A - Activated carbon biological water treatment device - Google Patents

Activated carbon biological water treatment device

Info

Publication number
JP2003200183A
JP2003200183A JP2002001863A JP2002001863A JP2003200183A JP 2003200183 A JP2003200183 A JP 2003200183A JP 2002001863 A JP2002001863 A JP 2002001863A JP 2002001863 A JP2002001863 A JP 2002001863A JP 2003200183 A JP2003200183 A JP 2003200183A
Authority
JP
Japan
Prior art keywords
activated carbon
water
element module
carbon fiber
treated
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
JP2002001863A
Other languages
Japanese (ja)
Inventor
Yoichi Hirose
洋一 広瀬
Takashi Kuboya
隆 久保谷
Hiroshi Matsuura
寛 松浦
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.)
FUSO KENSETSU KOGYO
Fuso Kensetsu Kogyo KK
Original Assignee
FUSO KENSETSU KOGYO
Fuso Kensetsu Kogyo KK
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 FUSO KENSETSU KOGYO, Fuso Kensetsu Kogyo KK filed Critical FUSO KENSETSU KOGYO
Priority to JP2002001863A priority Critical patent/JP2003200183A/en
Publication of JP2003200183A publication Critical patent/JP2003200183A/en
Pending 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

  • Water Treatment By Sorption (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide an activated carbon biological water treatment device directly treating raw city water by a biological activated carbon, exhibiting a treating ability for a long period of time while decomposing a substance adsorbed to an activated carbon fiber and capable of easily removing manganese or the like and enhancing a sanitary value of city water. <P>SOLUTION: The activated carbon fiber 1 molded to a sheet-like shape is fixed to a mesh plate 2 to form a plate-like element 3 and an element module 4 is formed by providing a plurality of elements in parallel at a predetermined interval. This element module 4 is immersed in a water tank 5 and a diffusing pipe 6 is installed below this element module 4. <P>COPYRIGHT: (C)2003,JPO

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、水道原水を処理し
飲料水として安全な水道水を生産する生物活性炭水処理
装置に関し、特に、水道原水を直接生物活性炭処理する
とともに、活性炭繊維への被吸着物質を分解しながら長
期間に亘って処理能力を発揮し、さらにマンガン等も容
易に除去することができる生物活性炭水処理装置に関す
るものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a biological activated carbon water treatment apparatus for treating raw tap water to produce safe tap water as drinking water. The present invention relates to a biological activated carbon water treatment device which exhibits a treatment capacity for a long period of time while decomposing adsorbed substances and can easily remove manganese and the like.

【0002】[0002]

【従来の技術】現在、日本における水道原水としては、
ダム等の貯水池水の比重が増しつつある。これらの貯水
池では、流入する生活排水や農業排水に含まれる窒素や
リン等の、いわゆる栄養塩によって、緑藻や藍藻等の微
細藻類が増殖することが多く、貯水池水を原水とする水
道水では、これら微細藻類が産生する異臭味原因物質に
よって、カビ臭や藻臭等の異臭味の問題が数多く発生し
ている。また、貯水池周辺の農地やゴルフ場等から流入
する除草剤を主体とする農薬や工場排水に含まれる微量
化学物質の混入も疑われることから、水道水としての安
全性も懸念されている。さらに、これらの水道原水中に
含まれる有機物は水道浄水処理において、一般的な塩素
消毒を実施した際に、発ガン性が指摘されているトリハ
ロメタン等の消毒副生成物を生成する。
2. Description of the Related Art At present, as raw water for water supply in Japan,
The specific gravity of reservoir water such as dams is increasing. In these reservoirs, microalgae such as green algae and cyanobacteria are often proliferated by so-called nutrient salts such as nitrogen and phosphorus contained in inflowing domestic wastewater and agricultural wastewater, and in tap water using the reservoir water as raw water, Due to the offensive odor-causing substances produced by these microalgae, many problems of offensive odor such as mold odor and algae odor have occurred. In addition, since it is suspected that agrochemicals mainly containing herbicides and trace chemical substances contained in factory effluent flowing from farmlands and golf courses around the reservoir are suspected to be contaminated, safety as tap water is also a concern. Furthermore, the organic substances contained in these raw water for tap water produce disinfection by-products such as trihalomethanes, which have been pointed out to be carcinogenic, when general chlorine disinfection is carried out in tap water purification treatment.

【0003】このような水道原水を処理し、水道水とし
て供給するための従来の技術としては、凝集沈殿や急速
ろ過というプロセスに、粒状活性炭吸着処理を単独で付
加するか、この粒状活性炭吸着処理にオゾン処理と粒状
活性炭吸着処理とを組み合わせたプロセスを付加する、
いわゆる高度浄水処理プロセスが一般的であり、このよ
うな方式による浄水場の建設実績も数多くみられるよう
になっている。
As a conventional technique for treating such raw tap water and supplying it as tap water, a granular activated carbon adsorption treatment is separately added to the process of coagulation sedimentation or rapid filtration, or this granular activated carbon adsorption treatment is carried out. Add a process that combines ozone treatment and granular activated carbon adsorption treatment to
The so-called advanced water treatment process is generally used, and there are many records of construction of water purification plants using this method.

【0004】このように、急速ろ過の後ろにオゾン処理
と粒状活性炭吸着処理を組み合わせると、オゾン処理に
よって異臭味原因物質や水道浄水処理時の塩素消毒によ
って生成されるトリハロメタン等の消毒副生成物の原因
となる被処理水中の有機物が低分子化され、後段の粒状
活性炭表面に多数存在する小径の孔の内部に棲息する好
気性微生物によって活性炭表面に吸着された有機物が分
解されるので、活性炭本来の吸着能力から想定される期
間以上に亘って除去能力が発揮されるとされ、このよう
な活性炭処理は生物活性炭処理(BAC)と呼ばれてい
る。
When the ozone treatment and the granular activated carbon adsorption treatment are combined after the rapid filtration as described above, the offensive odor-causing substance and the disinfection by-products such as trihalomethane produced by chlorine disinfection at the time of tap water purification treatment are combined by the ozone treatment. The organic matter in the treated water, which is the cause, is reduced in molecular weight, and the organic matter adsorbed on the surface of the activated carbon is decomposed by aerobic microorganisms that live inside the small pores present on the surface of the granular activated carbon in the latter stage. It is said that the removal ability is exhibited for a period longer than the period assumed from the adsorption ability of the activated carbon, and such activated carbon treatment is called biological activated carbon treatment (BAC).

【0005】[0005]

【発明が解決しようとする課題】しかしながら、このよ
うに有効な粒状活性炭による生物活性炭処理であるが、
下記のような幾つかの技術的課題が残されている。
However, the treatment of biological activated carbon with granular activated carbon is effective in this way,
There are some technical problems that remain as below.

【0006】すなわち、活性炭は、粒状であるが故に使
用にあたっては概ね1.5〜2.5mの高さに充填し、
下向流で被処理水を粒状活性炭層に一定の速度で流すの
であるが、このプロセスでは、活性炭本来の機能である
吸着作用よりも、むしろ、ろ過作用の方が卓越する場合
がある。このような場合、被処理水中に残留する懸濁物
や鉄分の酸化されたものが、粒状活性炭層の上層に抑留
されることによって、この部分の粒状活性炭の表面がこ
の抑留物によって覆われることになり、これにより、異
臭味原因有機物や消毒副生成物原因物質、農薬等の微量
化学物質等被処理水中に溶解している被吸着物質が活性
炭表面に到達しにくくなることから、活性炭吸着層全体
としての吸着効率が低下する。また、抑留物の上層での
堆積によって、活性炭層での圧力損失が増加することか
ら、概ね3日に1回程度の頻度で定期的に活性炭下部か
ら処理水を逆流させ洗浄する必要がある。したがって、
粒状活性炭を層状に積み上げて使用する従来の生物活性
炭処理装置は、水道原水が懸濁物質や鉄の酸化物、微細
藻類等の活性炭層を急激に目詰まりさせるような物質を
含む場合には、凝集沈殿や急速ろ過等の何らかの前処理
を施さないかぎり適用できないという限界があった。さ
らに、これら縣濁物や鉄分の酸化物の他に被処理水中に
還元状態のマンガンが存在すると、オゾン処理によって
酸化されて粒状活性炭表面に付着することになり、表面
の小径の孔を閉塞させることによって縣濁物と同様に活
性炭としての吸着機能を低下させる要因となる。
[0006] That is, since activated carbon is granular, it is packed in a height of about 1.5 to 2.5 m in use.
Although the water to be treated is caused to flow through the granular activated carbon layer in a downward flow at a constant speed, in this process, the filtering action may be superior to the adsorption action which is the original function of the activated carbon. In such a case, the suspended matter remaining in the water to be treated or the oxidized iron content is retained in the upper layer of the granular activated carbon layer, so that the surface of the granular activated carbon in this part is covered with this retained substance. As a result, the adsorbed substances dissolved in the water to be treated, such as organic substances causing off-flavors, substances causing disinfection by-products, trace chemical substances such as pesticides, etc., become difficult to reach the surface of the activated carbon. The overall adsorption efficiency decreases. In addition, since the pressure loss in the activated carbon layer increases due to the accumulation in the upper layer of the detained matter, it is necessary to backwash the treated water from the lower portion of the activated carbon periodically at a frequency of about once every three days. Therefore,
A conventional biological activated carbon treatment device that uses granular activated carbon stacked in layers is used in the case where the raw tap water contains suspended substances, iron oxides, substances such as microalgae that rapidly clog the activated carbon layer, There is a limit that it cannot be applied unless some pretreatment such as coagulation sedimentation or rapid filtration is performed. Furthermore, in addition to these suspensions and iron oxides, if reduced manganese is present in the water to be treated, it will be oxidized by ozone treatment and attached to the surface of the granular activated carbon, blocking small-diameter pores on the surface. As a result, it becomes a factor of lowering the adsorption function as activated carbon as well as the suspension.

【0007】また、従来生物活性炭処理において多用さ
れている粒状活性炭は、活性炭表面に多数の小径孔が存
在し、この小径孔に好気性微生物が棲息・繁殖し、さら
にこれを捕食するミミズ状の後生動物が棲息・繁殖する
こととなって、これらが処理水中に漏洩することがあ
り、水道水の衛生的価値が著しく低下するという問題が
あった。
Further, granular activated carbon, which has been frequently used in the treatment of biological activated carbon, has a large number of small pores on the surface of the activated carbon, and aerobic microorganisms inhabit and propagate in the small pores, and further, earthworm-like particles that predate this. Since metazoans live and breed, they may leak into the treated water, resulting in a significant decrease in the sanitary value of tap water.

【0008】本発明は、上記従来の生物活性炭水処理装
置が有する問題点に鑑み、水道原水を直接生物活性炭処
理するとともに、活性炭繊維への被吸着物質を分解しな
がら長期間に亘って処理能力を発揮し、さらにマンガン
等も容易に除去することができ、また、水道水の衛生的
価値を向上することができる生物活性炭水処理装置を提
供することを目的とする。
In view of the problems of the above-mentioned conventional biological activated carbon water treatment apparatus, the present invention directly treats raw tap water with biological activated carbon and decomposes substances to be adsorbed on the activated carbon fiber for a long period of time. It is an object of the present invention to provide a biological activated charcoal water treatment device that exhibits the above effects, can easily remove manganese and the like, and can improve the sanitary value of tap water.

【0009】[0009]

【課題を解決するための手段】上記目的を達成するた
め、本第1発明の生物活性炭水処理装置は、シート状に
成形した活性炭繊維を網板に固定して板状のエレメント
を形成し、該エレメントを複数、所定間隔で並設してエ
レメントモジュールを形成するとともに、該エレメント
モジュールを水槽内に浸漬して、該エレメントモジュー
ルの下に散気管を設置したことを特徴とする。
In order to achieve the above object, the biological activated carbon water treatment device of the first aspect of the present invention is a sheet-shaped activated carbon fiber fixed to a mesh plate to form a plate-shaped element, A plurality of the elements are arranged side by side at a predetermined interval to form an element module, the element module is immersed in a water tank, and an air diffuser is installed under the element module.

【0010】この生物活性炭水処理装置は、シート状に
成形した活性炭繊維を網板に固定して板状のエレメント
を形成し、このエレメントを複数、所定間隔で並設して
エレメントモジュールを形成するとともに、このエレメ
ントモジュールを水槽内に浸漬して、このエレメントモ
ジュールの下に散気管を設置したことから、散気管から
の送気によりエレメント間にエアリフト効果による流動
を生じさせて、活性炭繊維の表面と被処理水との接触の
促進と水槽全体の撹拌とを行うことができ、さらに、生
物活性炭処理に必要な酸素の補給を行うことができる。
これにより、縣濁物質や鉄の酸化物、微細藻類等を含む
水道原水を直接生物活性炭処理するとともに、活性炭本
来の異臭味物質や消毒副生成物起因有機物、農薬等の有
害な微量化学物質の吸着能力を損なうことなく、しか
も、活性炭繊維上に付着した好気性微生物の作用により
活性炭繊維への被吸着物質を分解しながら長期間に亘っ
て処理能力を発揮することができる。また、被処理水中
にアンモニア性窒素を含む場合でも、活性炭繊維上に付
着した硝化細菌によりアンモニアの硝酸化も可能であ
り、アンモニア性窒素に起因する塩素消費量を低減する
ことができ、さらに、被処理水中のマンガンも活性炭繊
維上に棲息する微生物の触媒的酸化によって処理し易い
形態の酸化マンガンに変換されることから、後段に凝集
沈殿装置やろ過装置を設置することによって容易に除去
することが可能である。
In this biological activated carbon water treatment apparatus, sheet-shaped activated carbon fibers are fixed to a mesh plate to form plate-shaped elements, and a plurality of these elements are arranged side by side at predetermined intervals to form an element module. At the same time, since this element module was dipped in a water tank and an air diffuser was installed under this element module, air flow from the air diffuser caused a flow due to the air lift effect between the elements, and the surface of the activated carbon fiber It is possible to promote contact with the water to be treated and to stir the entire water tank, and further to supplement oxygen necessary for the treatment with biological activated carbon.
As a result, tap water containing suspended solids, iron oxides, microalgae, etc. is directly treated with biological activated carbon, and the harmful carbonaceous substances such as organic odorous substances and organic substances caused by disinfection by-products, which are the original of activated carbon, and harmful agricultural chemicals are also removed. It is possible to exert the treatment ability for a long period of time without deteriorating the adsorption ability, and further, while decomposing the substance to be adsorbed on the activated carbon fiber by the action of the aerobic microorganism attached to the activated carbon fiber. Further, even when the water to be treated contains ammonia nitrogen, it is possible to nitrify ammonia by nitrifying bacteria adhering to the activated carbon fiber, and it is possible to reduce chlorine consumption due to ammonia nitrogen, and further, Manganese in the water to be treated is also converted into manganese oxide in a form that can be easily treated by the catalytic oxidation of microorganisms living on the activated carbon fiber, so it can be easily removed by installing a coagulating sedimentation device or a filtration device in the subsequent stage. Is possible.

【0011】また、同じ目的を達成するため、本第2発
明の生物活性炭水処理装置は、シート状に成形した活性
炭繊維を網板に固定して円板状のエレメントを形成し、
該エレメントを複数、所定間隔で並設し中心を軸で連結
してエレメントモジュールを形成するとともに、該エレ
メントモジュールの一部を水槽に浸漬して、前記軸を中
心に回転駆動するようにしたことを特徴とする。
In order to achieve the same object, in the biological activated carbon water treatment device of the second aspect of the present invention, a sheet-shaped activated carbon fiber is fixed to a mesh plate to form a disc-shaped element,
A plurality of the elements are arranged side by side at a predetermined interval and the centers are connected by a shaft to form an element module, and a part of the element module is immersed in a water tank so as to be rotationally driven about the shaft. Is characterized by.

【0012】この生物活性炭水処理装置は、シート状に
成形した活性炭繊維を網板に固定して円板状のエレメン
トを形成し、このエレメントを複数、所定間隔で並設し
中心を軸で連結してエレメントモジュールを形成すると
ともに、このエレメントモジュールの一部を水槽に浸漬
して、軸を中心に回転駆動するようにしたことから、エ
レメントモジュールの回転により、エレメントの活性炭
繊維と被処理水とを効率良く接触させるとともに、水槽
内の被処理水の撹拌と、大気中からの酸素の補給を同時
に行うことができる。これにより、縣濁物質や鉄の酸化
物、微細藻類等を含む水道原水を直接生物活性炭処理す
るとともに、活性炭本来の異臭味物質や消毒副生成物起
因有機物、農薬等の有害な微量化学物質の吸着能力を損
なうことなく、しかも、活性炭繊維上に付着した好気性
微生物の作用により活性炭繊維への被吸着物質を分解し
ながら長期間に亘って処理能力を発揮することができ
る。また、被処理水中にアンモニア性窒素を含む場合で
も、活性炭繊維上に付着した硝化細菌によりアンモニア
の硝酸化も可能であり、アンモニア性窒素に起因する塩
素消費量を低減することができ、さらに、被処理水中の
マンガンも活性炭繊維上に棲息する微生物の触媒的酸化
によって処理し易い形態の酸化マンガンに変換されるこ
とから、後段に凝集沈殿装置やろ過装置を設置すること
によって容易に除去することが可能である。
In this biological activated carbon water treatment apparatus, sheet-shaped activated carbon fibers are fixed to a mesh plate to form disc-shaped elements, and a plurality of these elements are arranged side by side at predetermined intervals and the centers are connected by an axis. The element module is formed by immersing a part of the element module in a water tank and is driven to rotate about an axis. It is possible to efficiently contact with each other, simultaneously stir the water to be treated in the water tank, and simultaneously supplement oxygen from the atmosphere. As a result, tap water containing suspended solids, iron oxides, microalgae, etc. is directly treated with biological activated carbon, and the harmful carbonaceous substances such as organic odorous substances and organic substances caused by disinfection by-products, which are the original of activated carbon, and harmful agricultural chemicals are also removed. It is possible to exert the treatment ability for a long period of time without deteriorating the adsorption ability, and further, while decomposing the substance to be adsorbed on the activated carbon fiber by the action of the aerobic microorganism attached to the activated carbon fiber. Further, even when the water to be treated contains ammonia nitrogen, it is possible to nitrify ammonia by nitrifying bacteria adhering to the activated carbon fiber, and it is possible to reduce chlorine consumption due to ammonia nitrogen, and further, Manganese in the water to be treated is also converted into manganese oxide in a form that can be easily treated by the catalytic oxidation of microorganisms living on the activated carbon fiber, so it can be easily removed by installing a coagulating sedimentation device or a filtration device in the subsequent stage. Is possible.

【0013】[0013]

【発明の実施の形態】以下、本発明の生物活性炭水処理
装置の実施の形態を図面に基づいて説明する。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the biological activated carbon water treatment apparatus of the present invention will be described below with reference to the drawings.

【0014】図1〜図2に、本発明の生物活性炭水処理
装置の第1実施例を示す。この生物活性炭水処理装置
は、シート状に成形した活性炭繊維1を網板2に固定し
て板状のエレメント3を形成するとともに、このエレメ
ント3を複数、所定間隔で並列に配設してエレメントモ
ジュール4を形成している。そして、この生物活性炭水
処理装置は、エレメントモジュール4を、被処理水を導
入する水槽5内に浸漬し、エレメントモジュール4の下
に散気管6を設置している。
1 to 2 show a first embodiment of the biological activated carbon water treatment apparatus of the present invention. In this biological activated carbon water treatment device, a sheet-shaped activated carbon fiber 1 is fixed to a mesh plate 2 to form a plate-shaped element 3, and a plurality of the elements 3 are arranged in parallel at a predetermined interval. It forms the module 4. In this biological activated carbon water treatment device, the element module 4 is immersed in a water tank 5 into which water to be treated is introduced, and an air diffusing pipe 6 is installed below the element module 4.

【0015】活性炭繊維1は、レイヨン等の化学繊維を
水蒸気混在下で、高温処理を施して炭素化させることに
より、吸着能力が粒状活性炭の数百倍の活性炭繊維を得
ることができる。この活性炭繊維1をシート状に成形
し、ステンレスや合成樹脂等の耐食性素材からなる網板
2に固定して板状のエレメントを形成する。シート状の
活性炭繊維1は網板2の片面又は両面に配設することが
でき、また、網板2への固定は接着やボルト等の締結具
により行うことができる。そして、この実施例では、多
数のエレメント3を一定の間隔で配設するとともに、エ
レメント3の周囲を側板7で取り囲むことにより箱状の
エレメントモジュール4を一体に形成している。
The activated carbon fiber 1 can be obtained by subjecting a chemical fiber such as rayon or the like to a high temperature treatment to carbonize it in the presence of steam, to obtain an activated carbon fiber having an adsorption capacity several hundred times that of granular activated carbon. This activated carbon fiber 1 is formed into a sheet and fixed to a net plate 2 made of a corrosion resistant material such as stainless steel or synthetic resin to form a plate-shaped element. The sheet-shaped activated carbon fiber 1 can be arranged on one side or both sides of the mesh plate 2, and can be fixed to the mesh plate 2 by adhesion or a fastener such as a bolt. In addition, in this embodiment, a large number of elements 3 are arranged at regular intervals, and the box-shaped element module 4 is integrally formed by surrounding the elements 3 with side plates 7.

【0016】一方、エレメントモジュール4が浸漬され
る水槽5は、その上部でエレメントモジュール4の周囲
を取り囲む中囲い壁51を有し、エレメントモジュール
4の側板7とともに、散気管6によるエアリフト効果を
高めている。また、散気管6は、ブロワ(図示省略)と
接続されており、エレメントモジュール4に曝気を行う
ことができる。なお、本実施例では、図1(b)に示す
ように、生物活性炭水処理装置Aの後段に、凝集沈殿装
置9やろ過装置10を設けている。
On the other hand, the water tank 5 in which the element module 4 is immersed has an inner enclosure wall 51 which surrounds the periphery of the element module 4 at its upper part, and enhances the air lift effect by the air diffuser 6 together with the side plate 7 of the element module 4. ing. Further, the air diffuser 6 is connected to a blower (not shown) and can aerate the element module 4. In this embodiment, as shown in FIG. 1 (b), a coagulating sedimentation device 9 and a filtration device 10 are provided after the biological activated carbon water treatment device A.

【0017】かくして、この第1実施例の生物活性炭水
処理装置は、シート状に成形した活性炭繊維1を網板2
に固定して板状のエレメント3を形成し、このエレメン
ト3を多数、所定間隔で並設してエレメントモジュール
4を形成するとともに、このエレメントモジュール4を
水槽5内に浸漬して、このエレメントモジュール4の下
に散気管6を設置したことから、散気管6からの送気に
よりエレメント3間にエアリフト効果による流動を生じ
させて、活性炭繊維1の表面と被処理水との接触の促進
と水槽5全体の撹拌とを行うことができ、さらに、生物
活性炭処理に必要な酸素の補給を行うことができる。そ
の結果、縣濁物質や鉄の酸化物、微細藻類等を含む水道
原水を直接生物活性炭処理するとともに、活性炭本来の
異臭味物質や消毒副生成物起因有機物、農薬等の有害な
微量化学物質の吸着能力を損なうことなく、しかも、活
性炭繊維1上に付着した好気性微生物の作用により活性
炭繊維1への被吸着物質を分解しながら長期間に亘って
処理能力を発揮することができる。また、被処理水中に
アンモニア性窒素を含む場合でも、活性炭繊維1上に付
着した硝化細菌によりアンモニアの硝酸化も可能であ
り、アンモニア性窒素に起因する塩素消費量を低減する
ことができ、さらに、被処理水中のマンガンも活性炭繊
維1上に棲息する微生物の触媒的酸化によって処理し易
い形態の酸化マンガンに変換されることから、後段に凝
集沈殿装置やろ過装置を設置することによって容易に除
去することが可能である。
Thus, in the biological activated carbon water treatment apparatus of the first embodiment, the activated carbon fiber 1 formed into a sheet shape is used as the net plate 2.
To form a plate-shaped element 3, and a large number of the elements 3 are juxtaposed at predetermined intervals to form an element module 4, and the element module 4 is immersed in a water tank 5 to form the element module. Since the air diffuser 6 is installed below the air diffuser 6, the air from the air diffuser 6 causes a flow due to the air lift effect between the elements 3 to promote the contact between the surface of the activated carbon fiber 1 and the water to be treated and the water tank. It is possible to carry out stirring of the whole 5 and to supplement oxygen necessary for the treatment of biological activated carbon. As a result, tap water containing suspended solids, oxides of iron, microalgae, etc. is directly treated with bioactive carbon, and the harmful carbonaceous substances such as pesticides and other organic substances caused by the original off-flavor substances of active carbon and disinfection by-products. It is possible to exert the treatment ability for a long period of time without deteriorating the adsorption ability and further decomposing the substance to be adsorbed on the activated carbon fiber 1 by the action of the aerobic microorganisms attached on the activated carbon fiber 1. Further, even when the water to be treated contains ammonia nitrogen, nitrification of ammonia can be carried out by the nitrifying bacteria adhering to the activated carbon fiber 1, and the chlorine consumption due to ammonia nitrogen can be reduced. Since manganese in the water to be treated is also converted into manganese oxide in a form that can be easily treated by catalytic oxidation of microorganisms living on the activated carbon fiber 1, it is easily removed by installing a coagulating sedimentation device or a filtration device in the subsequent stage. It is possible to

【0018】次に、図3〜図4を参照して、本発明の生
物活性炭水処理装置の第2実施例を説明する。この生物
活性炭水処理装置は、シート状に成形した活性炭繊維1
を網板2に固定して円板状のエレメント3を形成すると
ともに、このエレメント3を多数、所定間隔で並設し、
並設したエレメント3の中心を軸8で連結してエレメン
トモジュール4を形成している。そして、この生物活性
炭水処理装置は、エレメントモジュール4の下部が被処
理水を導入する水槽5に浸漬するように軸8を支持する
とともに、モータ等の駆動装置(図示省略)により、軸
8を中心に回転駆動するように構成し、エレメントモジ
ュール4を回転させながら水処理を行うようにしてい
る。
Next, a second embodiment of the biological activated carbon water treatment apparatus of the present invention will be described with reference to FIGS. This biological activated carbon water treatment device is a sheet-shaped activated carbon fiber 1
Is fixed to the mesh plate 2 to form a disc-shaped element 3, and a large number of the elements 3 are arranged side by side at predetermined intervals.
The centers of the juxtaposed elements 3 are connected by a shaft 8 to form an element module 4. The biological activated carbon water treatment device supports the shaft 8 so that the lower part of the element module 4 is immersed in the water tank 5 into which the water to be treated is introduced, and the shaft 8 is driven by a driving device (not shown) such as a motor. It is configured so as to be driven to rotate in the center, and the water treatment is performed while rotating the element module 4.

【0019】活性炭繊維1は、レイヨン等の化学繊維を
水蒸気混在下、高温処理で炭素化させることにより、吸
着能力が粒状活性炭の数百倍の活性炭繊維1を得ること
ができる。この活性炭繊維1をシート状に成形し、ステ
ンレスや合成樹脂等の耐食性素材からなる網板2に固定
して板状のエレメント3を形成する。シート状活性炭繊
維1は網板2の片面又は両面に配設することができ、ま
た、網板2への固定は接着やボルト等の締結具により行
うことができる。なお、本実施例では、図3(b)に示
すように、生物活性炭水処理装置Aの後段に、膜ろ過装
置11等を設けている。
The activated carbon fiber 1 can be obtained by carbonizing a chemical fiber such as rayon by steaming at a high temperature in the presence of steam to obtain an activated carbon fiber 1 having an adsorption capacity several hundred times that of granular activated carbon. This activated carbon fiber 1 is formed into a sheet and fixed to a net plate 2 made of a corrosion resistant material such as stainless steel or synthetic resin to form a plate-shaped element 3. The sheet-shaped activated carbon fiber 1 can be arranged on one side or both sides of the mesh plate 2, and can be fixed to the mesh plate 2 by adhesion or a fastener such as a bolt. In this embodiment, as shown in FIG. 3 (b), the membrane filtration device 11 and the like are provided at the subsequent stage of the biological activated carbon water treatment device A.

【0020】かくして、この第2実施例の生物活性炭水
処理装置は、シート状に成形した活性炭繊維1を網板2
に固定して円板状のエレメント3を形成し、このエレメ
ント3を多数、所定間隔で並設し中心を軸8で連結して
エレメントモジュール4を形成するとともに、このエレ
メントモジュール4の一部を水槽5に浸漬して、軸8を
中心に回転駆動するようにしたことから、エレメントモ
ジュール4の回転により、エレメント3の活性炭繊維1
と被処理水とを効率良く接触させるとともに、水槽5内
の被処理水の撹拌と、大気中からの酸素の補給を同時に
行うことができる。その結果、縣濁物質や鉄の酸化物、
微細藻類等を含む水道原水を直接生物活性炭処理すると
ともに、活性炭本来の異臭味物質や消毒副生成物起因有
機物、農薬等の有害な微量化学物質の吸着能力を損なう
ことなく、しかも、活性炭繊維1上に付着した好気性微
生物の作用により活性炭繊維1への被吸着物質を分解し
ながら長期間に亘って処理能力を発揮することができ
る。また、被処理水中にアンモニア性窒素を含む場合で
も、活性炭繊維1上に付着した硝化細菌によりアンモニ
アの硝酸化も可能であり、アンモニア性窒素に起因する
塩素消費量を低減することができ、さらに、被処理水中
のマンガンも活性炭繊維1上に棲息する微生物の触媒的
酸化によって処理し易い形態の酸化マンガンに変換され
ることから、後段に凝集沈殿装置やろ過装置を設置する
ことによって容易に除去することが可能である。
Thus, in the biological activated carbon water treatment apparatus of the second embodiment, the activated carbon fiber 1 formed into a sheet is used as the net plate 2.
To form the disk-shaped element 3, a large number of the elements 3 are arranged in parallel at a predetermined interval, and the centers are connected by the shaft 8 to form the element module 4, and a part of the element module 4 is formed. Since it is immersed in the water tank 5 and is driven to rotate about the shaft 8, the activated carbon fiber 1 of the element 3 is rotated by the rotation of the element module 4.
And the water to be treated can be efficiently contacted, and the water to be treated in the water tank 5 can be stirred and oxygen from the atmosphere can be supplied at the same time. As a result, suspended substances and iron oxides,
Raw tap water containing microalgae is directly treated with bioactive carbon, and the ability to adsorb harmful trace chemicals such as natural odorous substances and disinfection by-products originating from activated carbon and harmful chemical substances such as pesticides is not impaired, and activated carbon fiber 1 By the action of the aerobic microorganisms attached to the upper part, it is possible to exert the treatment ability for a long period of time while decomposing the substance to be adsorbed on the activated carbon fiber 1. Further, even when the water to be treated contains ammonia nitrogen, nitrification of ammonia can be carried out by the nitrifying bacteria adhering to the activated carbon fiber 1, and the chlorine consumption due to ammonia nitrogen can be reduced. Since manganese in the water to be treated is also converted into manganese oxide in a form that can be easily treated by catalytic oxidation of microorganisms living on the activated carbon fiber 1, it is easily removed by installing a coagulating sedimentation device or a filtration device in the subsequent stage. It is possible to

【0021】以上、本発明の生物活性炭水処理装置の実
施例を説明したが、本発明の構成はこの実施例の記載に
限定されるものではなく、その趣旨を逸脱しない範囲に
おいて適宜変更することが可能である。
Although the embodiment of the biological activated carbon water treatment apparatus of the present invention has been described above, the structure of the present invention is not limited to the description of this embodiment, and may be appropriately modified within the scope of the invention. Is possible.

【0022】[0022]

【発明の効果】本第1発明の生物活性炭水処理装置によ
れば、シート状に成形した活性炭繊維を網板に固定して
板状のエレメントを形成し、このエレメントを複数、所
定間隔で並設してエレメントモジュールを形成するとと
もに、このエレメントモジュールを水槽内に浸漬して、
このエレメントモジュールの下に散気管を設置したこと
から、散気管からの送気によりエレメント間にエアリフ
ト効果による流動を生じさせて、活性炭繊維の表面と被
処理水との接触の促進と水槽全体の撹拌とを行うことが
でき、さらに、生物活性炭処理に必要な酸素の補給を行
うことができる。これにより、縣濁物質や鉄の酸化物、
微細藻類等を含む水道原水を直接生物活性炭処理すると
ともに、活性炭本来の異臭味物質や消毒副生成物起因有
機物、農薬等の有害な微量化学物質の吸着能力を損なう
ことなく、しかも、活性炭繊維上に付着した好気性微生
物の作用により活性炭繊維への被吸着物質を分解しなが
ら長期間に亘って処理能力を発揮することができる。ま
た、被処理水中にアンモニア性窒素を含む場合でも、活
性炭繊維上に付着した硝化細菌によりアンモニアの硝酸
化も可能であり、アンモニア性窒素に起因する塩素消費
量を低減することができ、さらに、被処理水中のマンガ
ンも活性炭繊維上に棲息する微生物の触媒的酸化によっ
て処理し易い形態の酸化マンガンに変換されることか
ら、後段に凝集沈殿装置やろ過装置を設置することによ
って容易に除去することが可能である。さらに、この発
明の生物活性炭水処理装置に用いられるシート状に成形
した活性炭繊維を網板に固定したエレメントは、従来生
物活性炭処理において用いられている粒状活性炭のよう
に活性炭表面に小径孔がほとんど存在しないことから、
好気性微生物を捕食するミミズ状の後生動物が処理水中
に漏洩することがなく、水道水の衛生的価値を向上する
ことができる。
According to the biological activated carbon water treatment apparatus of the first aspect of the present invention, sheet-shaped activated carbon fibers are fixed to a mesh plate to form plate-shaped elements, and a plurality of these elements are arranged at predetermined intervals. Installed to form an element module, dip this element module in a water tank,
Since the air diffuser is installed under this element module, the air from the air diffuser causes a flow due to the air lift effect between the elements, which promotes the contact between the surface of the activated carbon fiber and the water to be treated and the entire water tank. Stirring can be performed, and in addition, supplementation of oxygen required for biological activated carbon treatment can be performed. As a result, suspended solids and iron oxides,
Raw tap water containing microalgae is directly treated with bioactive carbon, and it does not impair the ability to adsorb harmful trace chemical substances such as the original off-flavor substances of the active carbon, disinfection by-products, pesticides, etc. By the action of the aerobic microorganisms attached to the, it is possible to exert the treatment ability for a long period of time while decomposing the substance to be adsorbed on the activated carbon fiber. Further, even when the water to be treated contains ammonia nitrogen, it is possible to nitrify ammonia by nitrifying bacteria adhering to the activated carbon fiber, and it is possible to reduce chlorine consumption due to ammonia nitrogen, and further, Manganese in the water to be treated is also converted into manganese oxide in a form that can be easily treated by the catalytic oxidation of microorganisms living on the activated carbon fiber, so it can be easily removed by installing a coagulating sedimentation device or a filtration device in the subsequent stage. Is possible. Furthermore, the element in which the activated carbon fiber formed in a sheet shape used for the biological activated carbon water treatment device of the present invention is fixed to the mesh plate has almost no small holes on the activated carbon surface like the granular activated carbon conventionally used in biological activated carbon treatment. Because it doesn't exist,
Earthworm-like metazoans that prey on aerobic microorganisms do not leak into the treated water, and the sanitary value of tap water can be improved.

【0023】また、本第2発明の生物活性炭水処理装置
によれば、シート状に成形した活性炭繊維を網板に固定
して円板状のエレメントを形成し、このエレメントを複
数、所定間隔で並設し中心を軸で連結してエレメントモ
ジュールを形成するとともに、このエレメントモジュー
ルの一部を水槽に浸漬して、前記軸を中心に回転駆動す
るようにしたことから、エレメントモジュールの回転に
より、エレメントの活性炭繊維と被処理水とを効率良く
接触させるとともに、水槽内の被処理水の撹拌と、大気
中からの酸素の補給を同時に行うことができる。これに
より、縣濁物質や鉄の酸化物、微細藻類等を含む水道原
水を直接生物活性炭処理するとともに、活性炭本来の異
臭味物質や消毒副生成物起因有機物、農薬等の有害な微
量化学物質の吸着能力を損なうことなく、しかも、活性
炭繊維上に付着した好気性微生物の作用により活性炭繊
維への被吸着物質を分解しながら長期間に亘って処理能
力を発揮することができる。また、被処理水中にアンモ
ニア性窒素を含む場合でも、活性炭繊維上に付着した硝
化細菌によりアンモニアの硝酸化も可能であり、アンモ
ニア性窒素に起因する塩素消費量を低減することがで
き、さらに、被処理水中のマンガンも活性炭繊維上に棲
息する微生物の触媒的酸化によって処理し易い形態の酸
化マンガンに変換されることから、後段に凝集沈殿装置
やろ過装置を設置することによって容易に除去すること
が可能である。さらに、この発明の生物活性炭水処理装
置に用いられるシート状に成形した活性炭繊維を網板に
固定した円板状のエレメントは、従来生物活性炭処理に
おいて用いられている粒状活性炭のように活性炭表面に
小径孔がほとんど存在しないことから、好気性微生物を
捕食するミミズ状の後生動物が処理水中に漏洩すること
がなく、水道水の衛生的価値を向上することができる。
According to the biological activated carbon water treatment apparatus of the second aspect of the present invention, the sheet-shaped activated carbon fiber is fixed to the mesh plate to form a disc-shaped element, and a plurality of these elements are arranged at predetermined intervals. While forming an element module by arranging them side by side and connecting the centers with an axis, by immersing a part of this element module in a water tank so as to drive the rotation about the axis, the rotation of the element module The activated carbon fiber of the element and the water to be treated can be efficiently contacted, and the water to be treated in the water tank can be stirred and oxygen can be supplied from the atmosphere at the same time. As a result, tap water containing suspended solids, iron oxides, microalgae, etc. is directly treated with biological activated carbon, and the harmful carbonaceous substances such as organic odorous substances and organic substances caused by disinfection by-products, which are the original of activated carbon, and harmful agricultural chemicals are also removed. It is possible to exert the treatment ability for a long period of time without deteriorating the adsorption ability, and further, while decomposing the substance to be adsorbed on the activated carbon fiber by the action of the aerobic microorganism attached to the activated carbon fiber. Further, even when the water to be treated contains ammonia nitrogen, it is possible to nitrify ammonia by nitrifying bacteria adhering to the activated carbon fiber, and it is possible to reduce chlorine consumption due to ammonia nitrogen, and further, Manganese in the water to be treated is also converted to manganese oxide in a form that can be easily treated by the catalytic oxidation of microorganisms living on activated carbon fibers, so it can be easily removed by installing a coagulating sedimentation device or a filtration device in the subsequent stage. Is possible. Further, the disk-shaped element used in the biological activated carbon water treatment device of the present invention, in which the activated carbon fiber formed into a sheet is fixed to the mesh plate, is on the surface of the activated carbon like the granular activated carbon conventionally used in the treatment of biological activated carbon. Since there are few small holes, earthworm-like metazoans that prey on aerobic microorganisms do not leak into the treated water, and the sanitary value of tap water can be improved.

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

【図1】本発明の生物活性炭水処理装置の第1実施例を
示し、(a)は断面図、(b)は生物活性炭水処理装置
と他の処理装置との組み合わせ例を示す正面図である。
FIG. 1 shows a first embodiment of a biological activated carbon water treatment apparatus of the present invention, (a) is a cross-sectional view, and (b) is a front view showing an example of a combination of the biological activated carbon water treatment apparatus and another treatment apparatus. is there.

【図2】同実施例の生物活性炭水処理装置を示し、
(a)はエレメントの一部破断正面図、(b)はエレメ
ントモジュールの斜視図である。
FIG. 2 shows a biological activated carbon water treatment apparatus of the same embodiment,
(A) is a partially broken front view of the element, and (b) is a perspective view of the element module.

【図3】本発明の生物活性炭水処理装置の第2実施例を
示し、(a)は断面図、(b)は生物活性炭水処理装置
と他の処理装置との組み合わせ例を示す正面図である。
FIG. 3 shows a second embodiment of the biological activated carbon water treatment apparatus of the present invention, (a) is a sectional view, and (b) is a front view showing an example of a combination of the biological activated carbon water treatment apparatus and another processing apparatus. is there.

【図4】同実施例の生物活性炭水処理装置を示し、
(a)はエレメントの一部破断正面図、(b)はエレメ
ントモジュールの斜視図である。
FIG. 4 shows a biological activated carbon water treatment apparatus of the same embodiment,
(A) is a partially broken front view of the element, and (b) is a perspective view of the element module.

【符号の説明】[Explanation of symbols]

1 活性炭繊維 2 網板 3 エレメント 4 エレメントモジュール 5 水槽 51 中囲い壁 6 散気管 7 側板 8 軸 9 凝集沈殿装置 10 ろ過装置 11 膜ろ過装置 1 activated carbon fiber 2 mesh plate 3 elements 4 element module 5 aquarium 51 Middle enclosure wall 6 Air diffuser 7 side plate 8 axes 9 Coagulation sedimentation equipment 10 Filtration device 11 Membrane filtration device

フロントページの続き Fターム(参考) 4D003 AA01 AA09 AB02 EA02 EA16 EA25 4D024 AA01 AB04 AB13 AB16 BA02 BB02 BC01 BC04 CA07 DA06 DA07 DB15 Continued front page    F-term (reference) 4D003 AA01 AA09 AB02 EA02 EA16                       EA25                 4D024 AA01 AB04 AB13 AB16 BA02                       BB02 BC01 BC04 CA07 DA06                       DA07 DB15

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 シート状に成形した活性炭繊維を網板に
固定して板状のエレメントを形成し、該エレメントを複
数、所定間隔で並設してエレメントモジュールを形成す
るとともに、該エレメントモジュールを水槽内に浸漬し
て、該エレメントモジュールの下に散気管を設置したこ
とを特徴とする生物活性炭水処理装置。
1. A sheet-shaped activated carbon fiber is fixed to a mesh plate to form a plate-shaped element, and a plurality of the elements are arranged side by side at a predetermined interval to form an element module. A biological activated carbon water treatment device, characterized in that it is immersed in a water tank and an air diffuser is installed under the element module.
【請求項2】 シート状に成形した活性炭繊維を網板に
固定して円板状のエレメントを形成し、該エレメントを
複数、所定間隔で並設し中心を軸で連結してエレメント
モジュールを形成するとともに、該エレメントモジュー
ルの一部を水槽に浸漬して、前記軸を中心に回転駆動す
るようにしたことを特徴とする生物活性炭水処理装置。
2. An element module is formed by fixing sheet-shaped activated carbon fibers to a mesh plate to form disc-shaped elements, and arranging a plurality of such elements at predetermined intervals and connecting the centers with an axis. At the same time, a part of the element module is immersed in a water tank so that the element module is driven to rotate about the shaft as a center.
JP2002001863A 2002-01-09 2002-01-09 Activated carbon biological water treatment device Pending JP2003200183A (en)

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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7425274B1 (en) * 2004-12-09 2008-09-16 Leon Helfet Aquarium filter unit
US7628913B2 (en) 2005-10-05 2009-12-08 J.W. Pet Company, Inc. Aquarium filter cartridge and filtration system
US7816110B2 (en) 2005-12-15 2010-10-19 Hitachi Plant Technologies, Ltd. Process for producing pellets containing entrapped microorganisms
CN102887589A (en) * 2011-07-21 2013-01-23 中国环境科学研究院 Nano aeration biofilm reactor
CN104876293A (en) * 2015-05-26 2015-09-02 四川环博环境科技有限公司 Method of filtering and adsorbing wastewater with carbon fiber for wastewater treatment
RU171607U1 (en) * 2016-12-12 2017-06-07 Закрытое акционерное общество "КРЕАЛ" Filter sump

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7425274B1 (en) * 2004-12-09 2008-09-16 Leon Helfet Aquarium filter unit
US7628913B2 (en) 2005-10-05 2009-12-08 J.W. Pet Company, Inc. Aquarium filter cartridge and filtration system
US7816110B2 (en) 2005-12-15 2010-10-19 Hitachi Plant Technologies, Ltd. Process for producing pellets containing entrapped microorganisms
CN102887589A (en) * 2011-07-21 2013-01-23 中国环境科学研究院 Nano aeration biofilm reactor
CN104876293A (en) * 2015-05-26 2015-09-02 四川环博环境科技有限公司 Method of filtering and adsorbing wastewater with carbon fiber for wastewater treatment
RU171607U1 (en) * 2016-12-12 2017-06-07 Закрытое акционерное общество "КРЕАЛ" Filter sump

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