JPH08155476A - Nitration treatment method for seawater containing ammonical nitrogen - Google Patents

Nitration treatment method for seawater containing ammonical nitrogen

Info

Publication number
JPH08155476A
JPH08155476A JP6323954A JP32395494A JPH08155476A JP H08155476 A JPH08155476 A JP H08155476A JP 6323954 A JP6323954 A JP 6323954A JP 32395494 A JP32395494 A JP 32395494A JP H08155476 A JPH08155476 A JP H08155476A
Authority
JP
Japan
Prior art keywords
seawater
treatment
nitrogen
ammonia
nitrification
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
JP6323954A
Other languages
Japanese (ja)
Inventor
Teruyasu Hirayama
照康 平山
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.)
Shimizu Construction Co Ltd
Shimizu Corp
Original Assignee
Shimizu Construction Co Ltd
Shimizu 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 Shimizu Construction Co Ltd, Shimizu Corp filed Critical Shimizu Construction Co Ltd
Priority to JP6323954A priority Critical patent/JPH08155476A/en
Publication of JPH08155476A publication Critical patent/JPH08155476A/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

  • Biological Treatment Of Waste Water (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

PURPOSE: To efficiently nitrate ammomiacal nitrogen in seawater. CONSTITUTION: The nitration capacity per unit volume of ammoniacal nitrogen in seawater can be increased eminently by using a filler in which immobilized microorganisms 5 are stuck or deposited on the surface of oyster shell 6 as a filler for treatment by catalytic aeration, and an enough nitration capacity is kept even at low water temperature.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、含アンモニア態窒素海
水の硝化処理法及びそのための装置に関し、特には固定
化微生物を担持した牡蠣殻を接触曝気法の充填材として
用いる含アンモニア態窒素海水の硝化処理法及び硝化処
理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a nitrification treatment method for ammonia-containing nitrogen seawater and an apparatus therefor, and particularly to an ammonia-containing nitrogen seawater in which oyster shells carrying immobilized microorganisms are used as a packing material for the contact aeration method. The present invention relates to a nitrification treatment method and a nitrification treatment device.

【0002】[0002]

【従来の技術】自然環境浄化の観点から、最近は淡水に
ついては下水道の普及、浄化施設の充実などからかなり
の改善が図られてきている。しかしながら、海水の浄化
については一旦汚染排水などで海水が汚染されてしまっ
たりすると、それは終末に位置することからなかなか浄
化が進まず汚染が海水中に蓄積し、かつ、最近のように
海洋の利用が増大するに連れて汚染が海域に拡大するこ
となどが大きな問題となってきている。ところでこれま
では、海水中には雑多な成分が含まれていることからそ
の効率的な浄化処理ができなかった。また、浄化処理の
対象物が大量の水(海水)であることから、経済的かつ
技術的に有効な手段の提供がなされていなかった。特に
最近では獲る漁業から育てる漁業への転換もすすめら
れ、養殖において富栄養の飼料などが使用され、それに
伴い海域がアンモニア態窒素を多量に含むこととなって
汚染されること、イケスなどの水質の悪化から大量の魚
や貝、エビなどが死亡することなどの被害も生じてい
る。そこで、こうした含アンモニア態窒素海水の処理技
術の開発が強く求められている。
2. Description of the Related Art From the viewpoint of purifying the natural environment, recently, considerable improvements have been made to fresh water by popularizing sewerage and improving purification facilities. However, regarding the purification of seawater, once the seawater is contaminated by contaminated wastewater, etc., it is located at the end, so purification does not proceed easily and the pollution accumulates in the seawater, and recently the use of the ocean As pollution increases, pollution is becoming a major problem in the sea area. By the way, up to now, seawater contains various components, so that it has not been possible to efficiently purify the seawater. In addition, since the object of purification treatment is a large amount of water (seawater), economically and technically effective means have not been provided. In particular, recently, the shift from catching fisheries to breeding fisheries has been promoted, and eutrophication feeds are used in aquaculture, and the sea area is polluted with a large amount of ammonia nitrogen and water quality such as squid. Due to the deterioration of fishery, a lot of fish, shellfish and shrimp have been killed. Therefore, there is a strong demand for development of a treatment technology for such ammonia-containing nitrogen seawater.

【0003】通常、アンモニア態窒素を含む水を浄化処
理するには、硝化処理(アンモニア態窒素の亜硝酸態窒
素や硝酸態窒素への生物学的酸化処理)を施してなされ
るが、そのアンモニア態窒素を含む水の硝化処理は、砂
ろ過処理装置によりろ過砂中に硝化菌を高濃度に保持し
て行われる。しかしながら、海水のように、塩素イオン
濃度が30,000mg/リットルと高い水の硝化処理
は、硝化菌の活性が塩素イオンにより阻害されるため、
淡水の場合と比べて困難である。
Usually, in order to purify water containing ammonia nitrogen, nitrification treatment (biological oxidation treatment of ammonia nitrogen to nitrite nitrogen or nitrate nitrogen) is carried out. Nitrification of water containing volatile nitrogen is carried out by keeping a high concentration of nitrifying bacteria in the filter sand by a sand filter treatment device. However, the nitrification treatment of water such as seawater, which has a high chloride ion concentration of 30,000 mg / liter, inhibits the activity of nitrifying bacteria by chloride ions,
This is more difficult than in the case of fresh water.

【0004】[0004]

【発明が解決しようとする課題】このようなアンモニア
態窒素を含む水の硝化処理を、砂ろ過処理装置によりろ
過砂中に硝化菌を高濃度に保持して行われる方法は、以
下のような問題がある。 (1)砂ろ過装置は目詰まり防止のためにろ過砂を逆洗
する必要があるが、逆洗により大部分の硝化菌が装置外
に流出し、硝化効率が著しく低下する。その結果、逆洗
後、数日間は未処理のアンモニア態窒素が処理水中に含
まれることになる。こうした操作は煩雑であり、コスト
もかかる。 (2)好気性細菌である硝化菌への酸素供給は、海水中
に含有する溶存酸素により行われるが、溶存酸素量が不
足したり、ろ過砂内で微生物が繁殖しすぎた場合は、硝
化効率が著しく低下する。 一方、淡水系の含アンモニア態窒素排水の硝化処理の場
合、ハニカムチューブや波板系プラスチック充填材が硝
化菌を含む微生物を付着させる担体として用いられる。
これは接触曝気法と呼ばれる。この方法に用いる装置の
概念構成を、図3に示す。図中、1は接触曝気槽,2は
ハニカムチューブ等の充填材,3は散気装置(エアレー
タ)、4は隔壁である。まず、接触曝気槽1内へ導入さ
れた含アンモニア態窒素排水(原水)に対して、接触曝
気槽1底部からエアレータ3により空気が送給される。
これにより、接触曝気槽1内では、硝化菌を含む微生物
を付着した充填材2面で排水中のアンモニア態窒素が硝
化処理されて浄化され、その後上方端部の隔壁4側部か
ら清澄された浄化処理水として系外へ導出される。こう
した淡水系の含アンモニア態窒素排水の硝化処理方法を
含アンモニア態窒素海水の硝化処理に適用したところ、
殆ど微生物の付着が認められず、硝化現象も殆ど認めら
れなかった。このように淡水浄化のための施設を直ぐさ
ま海水処理の施設として使用しても、所期の効果が得ら
れないという問題があった。他方、生物学的排水処理法
において微生物濃度を高める方法として、固定化微生物
法が知られている。この方法は図4にその概念図を模式
的に示すごとく、固定化微生物片5’群を曝気槽1内に
投入し、エアレータ2から空気を送給して排水に対する
生物学的処理を行って硝化処理によりアンモニア態窒素
の硝化処理による浄化を行い、隔壁4側部から浄化処理
水を導出するものである。ここで、固定化微生物片5’
を製造するには、濃縮微生物と固定化物質の加熱などし
た溶液とを混合し冷却すると、ゲル状物質が生じるの
で、これを切断等により適当な大きさに成型することに
より取得される。
The method of carrying out such nitrification treatment of water containing ammoniacal nitrogen by using a sand filtration treatment device while maintaining a high concentration of nitrifying bacteria in the filter sand is as follows. There's a problem. (1) In the sand filter, it is necessary to backwash the filter sand in order to prevent clogging, but most of the nitrifying bacteria flow out of the device by backwashing, and the nitrification efficiency is significantly reduced. As a result, untreated ammonia nitrogen is contained in the treated water for several days after backwashing. Such operations are complicated and costly. (2) Oxygen is supplied to nitrifying bacteria, which are aerobic bacteria, by dissolved oxygen contained in seawater. However, if the amount of dissolved oxygen is insufficient, or if microorganisms grow too much in the filter sand, nitrification is performed. The efficiency is significantly reduced. On the other hand, in the case of nitrification treatment of fresh water-based ammonia-containing nitrogen wastewater, a honeycomb tube or a corrugated plate-based plastic filler is used as a carrier to which microorganisms including nitrifying bacteria are attached.
This is called the contact aeration method. The conceptual configuration of the apparatus used in this method is shown in FIG. In the figure, 1 is a contact aeration tank, 2 is a filler such as a honeycomb tube, 3 is an air diffuser (aerator), and 4 is a partition. First, the aerator 3 supplies air from the bottom of the contact aeration tank 1 to the ammonia-containing nitrogen wastewater (raw water) introduced into the contact aeration tank 1.
As a result, in the contact aeration tank 1, the ammonia nitrogen in the wastewater was purified by nitrification on the surface of the packing material 2 to which microorganisms including nitrifying bacteria were adhered, and then clarified from the side of the partition wall 4 at the upper end. It is led out of the system as purified treated water. When this method of nitrification of freshwater-based ammonia-containing nitrogen wastewater was applied to nitrification of ammonia-containing nitrogen seawater,
Almost no adhesion of microorganisms was observed, and nitrification phenomenon was hardly observed. Thus, even if the facility for purifying fresh water is immediately used as a facility for seawater treatment, there is a problem that the desired effect cannot be obtained. On the other hand, the immobilized microorganism method is known as a method for increasing the concentration of microorganisms in the biological wastewater treatment method. In this method, as shown in the schematic diagram in FIG. 4, a group of immobilized microorganisms 5'is put into the aeration tank 1 and air is sent from the aerator 2 to perform biological treatment of wastewater. Purification by nitrification treatment of ammonia nitrogen is performed by nitrification treatment, and purified treatment water is led out from the side of the partition wall 4. Here, immobilized microorganism piece 5 '
In order to produce, a gelled substance is produced by mixing a concentrated microorganism with a heated solution of an immobilizing substance and then cooling it. The gelled substance is obtained by molding it into an appropriate size.

【0005】[0005]

【課題を解決する手段】本発明者等は、硝化菌を含む微
生物を付着させる担体として牡蠣殻を利用して、硝化実
験を行ったところ、硝化現象を確認することが出来た。
この時、曝気槽内部の微生物の付着状況を観察したとこ
ろ、微生物は付着しているというよりは、牡蠣殻表面に
沈着している状況であった。つまりこの微生物は極めて
粘着性の低いものであった。本発明者等は、こうした牡
蠣殻を利用し、硝化菌を含む微生物を付着又は沈着させ
る担体として用い含アンモニア態窒素海水の硝化処理方
法を開発すべく種々検討を重ね、その結果固定化微生物
法と牡蠣殻を充填材とした接触曝気法とからなる含アン
モニア態窒素海水の処理装置が優れた処理機能を有する
こと、さらにその処理法及び処理装置は簡単な操作でか
つ経済上のメリットも大きく、環境への悪影響が少ない
ばかりか予想外の優れた作用効果も期待できることを見
出し、本発明を完成したものである。
Means for Solving the Problems The inventors of the present invention were able to confirm the nitrification phenomenon by conducting a nitrification experiment using oyster shells as a carrier to which microorganisms including nitrifying bacteria adhere.
At this time, when the state of attachment of the microorganisms inside the aeration tank was observed, it was found that the microorganisms were not attached but were deposited on the surface of the oyster shell. That is, this microorganism had extremely low stickiness. The present inventors have made various studies using such oyster shells to develop a nitrification treatment method of ammonia-containing nitrogen seawater used as a carrier for attaching or depositing microorganisms including nitrifying bacteria, and as a result, immobilized microbial method Ammonia-containing nitrogen seawater treatment equipment consisting of a contact aeration method with oyster shell as a packing material has an excellent treatment function, and the treatment method and treatment equipment have simple operation and great economic merit. The present invention has been completed by finding that not only the adverse effect on the environment is small but also an unexpectedly excellent action effect can be expected.

【0006】本発明においては、固定化微生物法と牡蠣
殻を充填材とした接触曝気法とを組み合わせた含アンモ
ニア態窒素海水の新規な水処理法及びそれに適した処理
装置が提供される。本発明の目的の一つは、含アンモニ
ア態窒素海水の硝化処理において、接触曝気槽内の硝化
菌濃度を高め、硝化性能の向上を図ることにある。すな
わち本発明は、(1)固定化微生物を牡蠣殻表面に付着
あるいは沈着せしめた充填材を接触曝気による処理充填
材として用い、水中のアンモニア態窒素を硝化処理する
ことを特徴とする含アンモニア態窒素海水の処理法、及
び(2)固定化微生物を牡蠣殻表面に付着あるいは沈着
せしめた充填材を接触曝気による含アンモニア態窒素海
水の硝化処理充填材として備えてなることを特徴とする
含アンモニア態窒素海水の処理装置、である。
[0006] The present invention provides a novel water treatment method of ammonia-containing nitrogen seawater, which is a combination of an immobilized microbial method and a contact aeration method using oyster shell as a packing material, and a treatment apparatus suitable for the method. One of the objects of the present invention is to improve the nitrification performance by increasing the concentration of nitrifying bacteria in the contact aeration tank in the nitrification treatment of ammonia-containing nitrogen seawater. That is, the present invention comprises (1) an ammonium-containing state characterized by subjecting an ammoniacal nitrogen in water to a nitrification treatment, using a filler obtained by adhering or depositing immobilized microorganisms on the surface of an oyster shell as a treatment filler by contact aeration. Nitrogen seawater treatment method, and (2) Ammonia-containing nitrogen-containing filler which is obtained by contacting and aerating an immobilizing microorganism adhered to or deposited on an oyster shell surface as a nitrifying filler for ammonia-containing nitrogen seawater. It is a state nitrogen seawater treatment device.

【0007】上記本発明における微生物源としては、下
水処理場等の活性汚泥が挙げられるが、活性汚泥中の微
生物は耐塩素イオン菌を選抜したり、変異誘発法を適用
してより耐塩素イオン菌としたり、遺伝子組換え法によ
り有用遺伝子を導入したりしてより耐塩素イオン菌とし
たりでき、また硝化処理能に優れた菌を選抜したり、変
異誘発法を適用してより硝化処理能に優れた菌を得た
り、遺伝子組換え法により有用遺伝子を導入したりして
より硝化処理能に優れた菌としたりできる。好ましく
は、アンモニウム・イオンや塩素イオン存在下に下水処
理場等の活性汚泥を培養して耐塩素イオン性を向上させ
且つ硝化処理能をもつ微生物を得ることができる。この
場合、塩素イオン濃度を徐々に高めて行き、最終的に海
水と同程度の濃度とすることが好ましい。微生物の固定
化法としては、当該分野で知られた方法あるいは公知の
方法を当業者に知られた方法で改変された方法を適用す
ることができ、例えば包括法、担体結合法、ろ過法など
が挙げられ、例えば包括法では、天然高分子、合成高分
子などを利用し、モノマー法、ポリマー法、プレポリマ
ー法などの方法を用いることができる。また例えば担体
結合法では、微孔あるいは微小粒子法、バイオマス・サ
ポート・パーティクルなどの多孔性物質利用法などの方
法を用いることができ、ろ過法では高分子膜あるいはセ
ラミック・フィルターなどを用いる方法が挙げられる。
Examples of the microorganism source in the present invention include activated sludge from sewage treatment plants, etc., but the microorganisms in the activated sludge are more resistant to chlorine ions by selecting a chlorine-resistant bacterium or applying a mutagenesis method. It can be used as a bacterium, or by introducing a useful gene by a gene recombination method to make it a more chloride-resistant bacterium, and a bacterium excellent in nitrification treatment ability can be selected. It is possible to obtain an excellent bacterium or to introduce a useful gene by a gene recombination method to obtain a bacterium having a higher nitrification treatment ability. Preferably, activated sludge in a sewage treatment plant or the like is cultured in the presence of ammonium ions or chloride ions to obtain a microorganism having improved chloride ion resistance and nitrification treatment ability. In this case, it is preferable that the chlorine ion concentration be gradually increased to finally reach the same level as seawater. As a method for immobilizing microorganisms, a method known in the art or a method modified by a method known to those skilled in the art can be applied, for example, a comprehensive method, a carrier binding method, a filtration method, etc. For example, in the encapsulation method, a natural polymer, a synthetic polymer or the like can be used, and a method such as a monomer method, a polymer method or a prepolymer method can be used. Further, for example, in the carrier binding method, a method such as a micropore or fine particle method, a method of using a porous material such as biomass support particles, etc. can be used, and a method of using a polymer membrane or a ceramic filter etc. is used in the filtration method. Can be mentioned.

【0008】固定化物質としては、包括法でよく用いら
れる天然高分子のアルギン酸ナトリウムなどのアルギン
酸、寒天、κ−カラギーナンなどのカラギーナンなど多
糖類が挙げられ、合成高分子ではポリアクリルアミド、
光硬化性樹脂プレポリマー、ウレタンプレポリマーなど
が挙げられ、光硬化性樹脂プレポリマーとしては、例え
ばポリエチレングリコールあるいはポリプロピレングリ
コールの両端にイソホロンジイソシアナートやヒドロキ
シエチルアクリレートが結合したものなどが挙げられ、
ウレタンプレポリマーとしては、例えばポリエチレング
リコールあるいはポリエチレングリコールとポリプロピ
レングリコールの共重合物の両端にトルエンジイソシア
ナートが結合したものなどが挙げられる。例えばアルギ
ン酸では、微生物を含むアルギン酸ナトリウム塩の水溶
液をゲル化剤であるカルシウムイオンなどの多価金属イ
オンを含む水溶液と接触させることで微生物を固定化で
きる。またカラギーナン、寒天などでは加熱、溶解した
ものを微生物共存下冷却するか、あるいは金属イオン、
アミン類等のゲル化剤と接触させることで微生物を固定
化できる。
Examples of the immobilizing substance include natural polymers such as sodium alginate, which are often used in the entrapping method, alginic acid, agar, and polysaccharides such as carrageenan, such as κ-carrageenan.
Examples of the photocurable resin prepolymer, urethane prepolymer, and the like, examples of the photocurable resin prepolymer include those in which isophorone diisocyanate or hydroxyethyl acrylate is bonded to both ends of polyethylene glycol or polypropylene glycol,
Examples of the urethane prepolymer include those in which toluene diisocyanate is bonded to both ends of polyethylene glycol or a copolymer of polyethylene glycol and polypropylene glycol. For example, in the case of alginic acid, the microorganism can be immobilized by contacting an aqueous solution of sodium alginate containing a microorganism with an aqueous solution containing a polyvalent metal ion such as calcium ion which is a gelling agent. Carrageenan, agar, etc. are heated, and the dissolved one is cooled in the presence of microorganisms, or metal ions,
The microorganism can be immobilized by contacting with a gelling agent such as amines.

【0009】牡蠣殻は好ましくは洗浄後、適当な大きさ
にされたものが用いられる。牡蠣殻に上記固定化微生物
を付着又は沈着せしめるには、上記固定化微生物含有液
に牡蠣殻片を微生物付着するあるいは表面上に沈着する
に適当な時間浸漬することにより行われることができ
る。牡蠣殻は次のような利点があり、接触曝気法の充填
材として優れている。 (1)一般に硝化反応により、処理水のpHが低下し、
硝化反応そのものに悪影響を与えることが起こるが、牡
蠣殻を用いた場合は牡蠣殻表面からのカルシウムイオン
の溶出により処理水のpHの低下を防止することが可能
である。したがって、硝化反応が処理水のpHが低下に
よる悪影響を受けることが少なく効率的な運転が可能で
ある。 (2)本来、廃棄物として捨てられる牡蠣殻を水処理材
料として有効に利用している。したがって安価な材料を
使用できる。また牡蠣殻は天然物であるので環境上も問
題が少ない。なお、本発明で言う「海水」とは海洋にお
ける海水のみに限定されるものではなく、それと同等の
人工海水(水中の塩類、pH等を海水同様に調整して造
られたもの)をも含むものである。
The oyster shell is preferably used after being washed and then sized appropriately. The immobilized microorganisms can be attached or deposited on the oyster shell by immersing the immobilized microorganism-containing liquid in the oyster shell for a suitable period of time for attaching the microorganisms to the oyster shell pieces or depositing them on the surface. The oyster shell has the following advantages and is excellent as a filler for the contact aeration method. (1) Generally, the pH of treated water decreases due to the nitrification reaction,
Although the nitrification reaction itself may be adversely affected, when oyster shells are used, it is possible to prevent the pH of the treated water from decreasing by elution of calcium ions from the surface of the oyster shells. Therefore, the nitrification reaction is less likely to be adversely affected by the decrease in the pH of the treated water, and efficient operation is possible. (2) Originally, oyster shells, which are originally discarded as waste, are effectively used as a water treatment material. Therefore, an inexpensive material can be used. Also, since oyster shells are natural products, there are few environmental problems. The "seawater" referred to in the present invention is not limited to seawater in the ocean, and includes artificial seawater equivalent to that (made by adjusting salt, pH, etc. in water like seawater). It is a waste.

【0010】[0010]

【実施例】次に実施例を示して、本発明をさらに具体的
に説明する。 実施例1 (1)耐塩素イオン硝化菌の培養 下水処理場等の活性汚泥を所定の容量の容器に入れて、
アンモニア剤(塩化アンモニウム)、ミネラル物質、p
H調整剤を毎日所定量投入する。さらに、塩化ナトリウ
ムを培養初期には塩素イオンで数十mg/リットルの濃
度になるよう添加し、徐々に添加濃度を上げ、最終的に
海水の塩素濃度になるようにする。この溶液は、連続的
に曝気により、攪拌混合されると同時に酸素供給を受け
る。培養期間は、2〜3か月である。
EXAMPLES Next, the present invention will be described more specifically by showing examples. Example 1 (1) Cultivation of Chloride-Resistant Nitrifying Bacteria Activated sludge from a sewage treatment plant or the like was placed in a container having a predetermined capacity,
Ammonia agent (ammonium chloride), mineral substances, p
Add a prescribed amount of H-adjusting agent every day. Further, sodium chloride is added with chlorine ions at a concentration of several tens of mg / liter at the initial stage of culture, and the concentration is gradually increased to finally reach the chlorine concentration of seawater. The solution is continuously aerated and agitated and mixed, and simultaneously supplied with oxygen. The culture period is 2-3 months.

【0011】(2)固定化微生物溶液の調製 固定化物質を2〜3%の濃度となるように水に溶解さ
せ、約50℃まで加熱する。一方、上記(1)で培養さ
れた耐塩素イオン硝化菌を遠心分離等により濃縮して得
られた硝化菌を含む微生物溶液と固定化物質溶液とを均
一となるように攪拌混合する。 (3)牡蠣殻への固定化微生物溶液の付着 洗浄した牡蠣殻を上記(2)で得られた溶液に浸漬し、
牡蠣殻表面に固定化微生物を付着させた後、室温にて放
冷する。固定化微生物を付着させた牡蠣殻を図2に模式
的に示す。図中、6は牡蛎殻、5は固定化微生物を示
す。
(2) Preparation of immobilized microbial solution The immobilized substance is dissolved in water to a concentration of 2-3% and heated to about 50 ° C. On the other hand, the chloride-resistant nitrifying bacterium cultivated in the above (1) is concentrated by centrifugation or the like, and the microbial solution containing the nitrifying bacterium and the immobilizing substance solution are stirred and mixed to be uniform. (3) Adhesion of immobilized microbial solution to oyster shell The washed oyster shell is dipped in the solution obtained in (2) above,
After allowing the immobilized microorganisms to adhere to the surface of the oyster shell, it is allowed to cool at room temperature. The oyster shell to which the immobilized microorganism is attached is schematically shown in FIG. In the figure, 6 indicates an oyster shell and 5 indicates an immobilized microorganism.

【0012】実施例2 (1)含アンモニア態窒素海水の連続処理法 図1に処理装置の概念図を示すごとく、牡蛎殻6の表面
に固定化微生物7を付着させたものを充填材20とし
て、曝気槽1内に配設し、下部のエアレータ3から空気
を送給し、充填材20面で排水中のアンモニア態窒素を
硝化処理して、浄化水となし、上方端部から浄化処理水
を導出する。なお、図中、7は貯留槽、8は砂ろ過塔、
Pは送水ポンプ、Bは送風機である。含アンモニア態窒
素海水としてアンモニア態窒素濃度が少なくとも3mg
/リットルの水産養殖排水を用い、1日当たり4立方メ
ートルの処理水量とした。砂ろ過塔におけるろ過速度を
10m/時とし、ろ層厚さを0.5mとした。そして接
触曝気層の条件は、滞留時間約1.5時間、充填材充填
率60%としたところ、浄化処理水のアンモニア態窒素
濃度は0.5mg/リットル以下となっていた。この結
果、アンモニア態窒素の83%が除去されたことが解
る。
Example 2 (1) Continuous Treatment Method of Ammonium-containing Nitrogen Sea Water As shown in the conceptual diagram of the treatment apparatus in FIG. 1, the oyster shell 6 with the immobilized microorganisms 7 attached to the surface thereof is used as the filler 20. , Disposed in the aeration tank 1, air is fed from the aerator 3 at the lower part, nitrification treatment of ammonia nitrogen in the wastewater is carried out on the surface of the filling material 20 to obtain purified water, and the purified water is treated from the upper end. Derive. In the figure, 7 is a storage tank, 8 is a sand filtration tower,
P is a water pump and B is a blower. Ammonium-containing nitrogen Seawater with an ammonium-nitrogen concentration of at least 3 mg
/ Liter of aquaculture wastewater was used and the treated water amount was 4 cubic meters per day. The filtration rate in the sand filtration tower was 10 m / hr, and the filter layer thickness was 0.5 m. When the conditions of the contact aeration layer were such that the residence time was about 1.5 hours and the filling rate of the filler was 60%, the ammonia nitrogen concentration in the purified water was 0.5 mg / liter or less. As a result, it can be seen that 83% of ammonia nitrogen was removed.

【0013】[0013]

【発明の効果】上記のとおりの本発明によれば、 (1)接触曝気槽内に高い濃度で硝化菌を含む微生物を
保持することが可能であるため、牡蠣殻単独の接触曝気
法に比べて、含アンモニア態窒素海水の単位容量あたり
の硝化能力を格段に高めることができる。 (2)10℃前後の低水温の海水に対しても、十分な硝
化能力を持つ。 (3)牡蠣殻単独の接触曝気法にみられるような微生物
の剥離による処理水の懸濁物質濃度の増大という現象が
起きにくい。 (4)牡蠣殻表面からのカルシウムイオンの溶出により
処理水のpHの低下を防止することが可能である。
EFFECTS OF THE INVENTION According to the present invention as described above, (1) it is possible to retain microorganisms containing nitrifying bacteria in a high concentration in a contact aeration tank, and therefore, compared with the contact aeration method using only oyster shells. As a result, the nitrification capacity per unit volume of ammonia-containing nitrogen seawater can be significantly increased. (2) It has a sufficient nitrification capacity even for low-temperature seawater around 10 ° C. (3) The phenomenon of increasing the concentration of suspended solids in treated water due to exfoliation of microorganisms unlike the contact aeration method using only oyster shells is unlikely to occur. (4) It is possible to prevent the pH of treated water from decreasing by elution of calcium ions from the surface of the oyster shell.

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

【図1】本発明実施例の含アンモニア態窒素海水の処理
装置の概念図を示す。
FIG. 1 is a conceptual diagram of a treatment apparatus for ammonia-containing nitrogen seawater according to an embodiment of the present invention.

【図2】固定化微生物を付着させた牡蠣殻の模式図を示
す。
FIG. 2 shows a schematic diagram of an oyster shell to which an immobilized microorganism is attached.

【図3】接触曝気による硝化処理装置の概念構成図を示
す。
FIG. 3 shows a conceptual configuration diagram of a nitrification treatment apparatus by contact aeration.

【図4】固定化微生物法の処理概念図を示す。【符号の
説明 1:曝気槽 2:充填材 3:散気装置(エアレータ) 4:隔壁 5:固定化微生物 6:牡蛎殻 7:貯留槽 8:砂ろ過塔 B:送風機 P:送水ポンプ
FIG. 4 shows a conceptual diagram of processing by the immobilized microorganism method. [Explanation of symbols] 1: Aeration tank 2: Filler 3: Air diffuser (aerator) 4: Partition wall 5: Immobilized microorganisms 6: Oyster shell 7: Storage tank 8: Sand filtration tower B: Blower P: Water pump

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 固定化微生物を牡蠣殻表面に付着あるい
は沈着せしめた充填材を接触曝気による処理充填材とし
て用い、水中のアンモニア態窒素を硝化処理することを
特徴とする含アンモニア態窒素海水の処理法。
1. Ammonia-containing nitrogen seawater, characterized in that ammonia-nitrogen-containing seawater is treated by nitrifying ammonia-nitrogen in water by using a filler having immobilized microorganisms attached or deposited on the surface of an oyster shell as a treatment filler by contact aeration. Processing method.
【請求項2】 固定化微生物を牡蠣殻表面に付着あるい
は沈着せしめた充填材を接触曝気による含アンモニア態
窒素海水の硝化処理充填材として備えてなることを特徴
とする含アンモニア態窒素海水の処理装置。
2. Treatment of ammonia-containing nitrogen seawater, characterized by comprising a filler having immobilized microorganisms attached or deposited on the surface of an oyster shell as a nitrification filler of ammonia-containing nitrogen seawater by contact aeration. apparatus.
JP6323954A 1994-12-02 1994-12-02 Nitration treatment method for seawater containing ammonical nitrogen Pending JPH08155476A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6323954A JPH08155476A (en) 1994-12-02 1994-12-02 Nitration treatment method for seawater containing ammonical nitrogen

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6323954A JPH08155476A (en) 1994-12-02 1994-12-02 Nitration treatment method for seawater containing ammonical nitrogen

Publications (1)

Publication Number Publication Date
JPH08155476A true JPH08155476A (en) 1996-06-18

Family

ID=18160489

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6323954A Pending JPH08155476A (en) 1994-12-02 1994-12-02 Nitration treatment method for seawater containing ammonical nitrogen

Country Status (1)

Country Link
JP (1) JPH08155476A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100441522C (en) * 2005-08-02 2008-12-10 马守祥 Oyster case active filtering material for sewage treatment and preparation method thereof
JP2015043740A (en) * 2013-08-29 2015-03-12 独立行政法人農業・食品産業技術総合研究機構 Production method of inorganic fertilizer
JP7298785B1 (en) * 2022-03-28 2023-06-27 中国電力株式会社 Sewage purification equipment

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100441522C (en) * 2005-08-02 2008-12-10 马守祥 Oyster case active filtering material for sewage treatment and preparation method thereof
JP2015043740A (en) * 2013-08-29 2015-03-12 独立行政法人農業・食品産業技術総合研究機構 Production method of inorganic fertilizer
JP7298785B1 (en) * 2022-03-28 2023-06-27 中国電力株式会社 Sewage purification equipment
WO2023187932A1 (en) * 2022-03-28 2023-10-05 中国電力株式会社 Waste water purification device

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