JPH05293A - Quality improvement of water - Google Patents

Quality improvement of water

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Publication number
JPH05293A
JPH05293A JP3042866A JP4286691A JPH05293A JP H05293 A JPH05293 A JP H05293A JP 3042866 A JP3042866 A JP 3042866A JP 4286691 A JP4286691 A JP 4286691A JP H05293 A JPH05293 A JP H05293A
Authority
JP
Japan
Prior art keywords
water
porous material
microorganisms
bacteria
fish
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP3042866A
Other languages
Japanese (ja)
Other versions
JP2599834B2 (en
Inventor
Tomoaki Otsuka
具明 大塚
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Individual
Original Assignee
Individual
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Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP4286691A priority Critical patent/JP2599834B2/en
Publication of JPH05293A publication Critical patent/JPH05293A/en
Application granted granted Critical
Publication of JP2599834B2 publication Critical patent/JP2599834B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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

Abstract

PURPOSE:To provide a simple and effective quality improvement method of water using the activity of bacteria, low in installation cost and adaptable to rivers and a drainageway and also useful for preventing the quality lowering of water not only in rivers or the drainageway but also in a fish pond, a fish preserve, a live fish transport tank or an aquarium. CONSTITUTION:A hydrohobic porous material 2 having aerobic bacteria supported thereon or capable of supporting said bacteria is brought into contact with objective water. The porous material has a sheet like shape, a cylindrical shape or a bag like shape and can contain a bacteria carrier 5 therein and, if desired, aerobic bacteria may be supported thereon.

Description

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

【0001】[0001]

【発明の利用分野】本発明は、水質の低下した河川や排
水溝の浄化、養魚池、生簀、活魚輸送槽、アクアリアム
等の水質低下防止等の多種多様の用途に利用しうる水質
改善法に関する。
FIELD OF THE INVENTION The present invention relates to a method for improving water quality that can be used for a wide variety of purposes such as purification of rivers and drainage channels with deteriorated water quality, prevention of water quality deterioration of fish ponds, cages, live fish transport tanks, aquariums and the like. Regarding

【0002】[0002]

【従来の技術】 背景 今日、河川や湖沼の水質低下が強く懸念されている。水
質の低下は、マクロ的には地球の環境破壊の一つの現れ
でもあるが、結果的に上水道の水質低下、水棲生物の減
少乃至絶滅、赤潮の発生による養殖魚類の死滅、悪臭の
発生など、ヒトの生活に重大な影響を及ぼす。元来地球
上には多種多様の好気性微生物が生存しており、水質低
下の主要な原因である腐敗した食物や屎尿、動物の死
体、生活排水などに含まれる窒素、炭素及びリン化合物
を栄養源としてこれらを終極的に窒素、炭酸ガスなどに
還元する作用を営んでおり、河川水もこれら微生物によ
る自浄作用により自然に浄化されるが、人口の都市への
集中、植生の破壊、農薬の散布などによる生態系の変化
は、これら微生物の増殖、延いてはそれによる自浄作用
を鈍らせ、今日の事態を招くこととなった。
BACKGROUND ART Today, there is a strong concern about deterioration of water quality in rivers and lakes. Although the deterioration of water quality is one of the macroscopically one of the environmental destruction of the earth, as a result, the water quality of the water supply deteriorates, the aquatic organisms decrease or become extinct, the aquaculture fish die due to the occurrence of red tide, and the generation of bad odors. It has a significant impact on human life. A wide variety of aerobic microorganisms live on the earth, and it nourishes nitrogen, carbon and phosphorus compounds contained in spoiled food and human waste, animal carcasses, domestic wastewater, etc., which are the main causes of water quality deterioration. As a source, it ultimately acts to reduce these to nitrogen, carbon dioxide, etc., and river water is naturally purified by the self-cleaning action of these microorganisms, but concentration of the population in cities, destruction of vegetation, pesticide Changes in the ecosystem due to spraying and the like slow down the growth of these microorganisms and, in turn, the self-cleaning action by them, leading to today's situation.

【0003】 従来技術の問題点 水質浄化のための根本的な手段は、人口の分散、下水道
の完備、森林の回復、農薬の使用中止、産業排水の完全
浄化などにより生態系を復旧させることである。しかし
ながら、これらの対策の実施には長い年月がかかり、到
底焦眉の急には間に合わないし、また産業排水の完全浄
化や農薬の使用中止のような、経済性との関連で実施困
難な事項もある。特に、下水道の完備は最重要な課題で
あるが、現在実用されている下水処理施設として、散水
濾床法、回転円板法、表面曝気活性汚泥法、浸漬濾床
法、流動層法、懸濁粒子活性汚泥法、散気式活性汚泥
法、ディープシャフト法などの何れを採用するにしても
大規模な設備とポンプ、コンプレッサなどに多量のエネ
ルギーを必要とする他、特に、各家庭その他の排水発生
源から下水処理場への配管を国内津々浦々まで張り巡ら
すことは、事実上不可能な問題である。加えて、装置か
ら処理量に応じて排出される活性汚泥は極めて強い悪臭
を持ち、処理場周囲への悪臭の防止や汚泥の廃棄処理も
関係者を悩ます問題である。
Problems of the prior art The fundamental means for water purification is to restore the ecosystem through population dispersion, complete sewerage, forest restoration, discontinuation of pesticide use, complete purification of industrial wastewater, etc. is there. However, it takes a long time to carry out these measures, and it is not possible to meet the demand in a hurry, and there are also problems that are difficult to carry out in connection with economic efficiency, such as complete purification of industrial wastewater and discontinuation of pesticide use. is there. In particular, complete sewerage is the most important issue, but as the sewage treatment facilities currently in practical use, the sprinkling filter method, the rotating disk method, the surface aeration activated sludge method, the immersion filter method, the fluidized bed method, the suspended bed method, Regardless of whether the turbid particle activated sludge method, diffused activated sludge method, or deep shaft method is adopted, a large amount of energy is required for large-scale equipment, pumps, compressors, etc. It is a virtually impossible problem to run piping from the wastewater source to the sewage treatment plant all over the country. In addition, activated sludge discharged from the equipment according to the amount of treatment has an extremely strong offensive odor, and the prevention of offensive odor around the treatment plant and the disposal of sludge are also troublesome for the concerned parties.

【0004】[0004]

【発明が解決しようとする課題】以上の実情に鑑み、本
発明は、微生物の活性を利用して、簡単で設備費が安
く、どの河川や排水溝に適用しうる有効な水質改善法を
提供するのを目的とする。本発明は、更に河川や排水溝
のみならず、養魚池、生簀、活魚輸送槽、アクアリアム
(金魚や熱帯魚の飼育水槽)の水質低下防止にも役立つ
水質改善法を提供するのを目的とする。
In view of the above circumstances, the present invention provides an effective method for improving water quality by utilizing the activity of microorganisms, which is simple and has a low equipment cost and can be applied to any river or drain. The purpose is to do. It is another object of the present invention to provide a water quality improving method that is useful not only in rivers and drains but also in preventing water quality deterioration in fish ponds, cages, live fish transport tanks, and aquariums (goldfish and tropical fish tanks). .

【0005】[0005]

【課題を解決するための手段】 概念 微生物の化学的能力は、他の生物に比べてずばぬけてい
る。例えば体重1kg当たり消費する酸素の量は、ヒトの
場合30℃で1時間当たり約200ml であるが、亜硝酸イオ
ンを硝酸に酸化する性質を有するアゾトバクター(G.Az
tobacter) の酸素消費量は1,200,000mlに達する(岩波
新書827、服部勉著《大地の微生物》58頁参照)。従
って、このような微生物の酸化能力を利用することによ
り、汚染の主因となる有機化合物をCO2 、N2、水、又は
NO3 のような無害の無機物に変化させることができれ
ば、水質低下の減少が防止できることになる。しかしな
がら、河水中への酸素の供給は大気との接触界面に限ら
れているから、酸素の供給量が少なければ、折角の微生
物の作用も発揮できない。加えて、単に微生物を水中へ
散布しても、水流により押し流され、集団としての能力
を発揮できないことになる。加えて、河水中には極めて
多種類の微生物が存在するから、好ましい有用な微生物
の増殖が他種微生物により妨害されることもありうる。
因に、微生物が棲み分けをしているかどうか、更に進ん
で、微生物同士が互いに高等動植物に見られるような生
存競争をしているかどうかは未だ充分確認されていない
が、少なくとも土壌中の団粒組織が土壌細菌の棲み家と
して役立っていることは確認されており、また放線菌類
のある種に見られる抗生物質の産生や、糸状菌と細菌と
の拮抗関係或は細菌捕食性ブデロビブリオ菌及びバクテ
リオファージの発見は、微生物の世界においてもある種
の秩序が存在すべきことを推測させるものである。
[Means for Solving the Problems] The chemical ability of conceptual microorganisms is far superior to that of other organisms. For example, the amount of oxygen consumed per 1 kg of body weight is about 200 ml per hour at 30 ° C. in humans, but Azotobacter (G.Az) has the property of oxidizing nitrite ions to nitric acid.
oxygen consumption of tobacter) reaches 1,200,000 ml (see Iwanami Shinsho 827, Tsutomu Hattori, "Microorganisms of the Earth", p. 58). Therefore, by utilizing the oxidative capacity of such microorganisms, organic compounds that cause the main pollution can be reduced to CO 2 , N 2 , water, or
If it can be changed to a harmless inorganic substance such as NO 3 , reduction in water quality deterioration can be prevented. However, since the supply of oxygen into the river water is limited to the contact interface with the atmosphere, if the supply of oxygen is small, the action of microorganisms will not be exhibited. In addition, even if the microorganisms are simply sprayed into the water, they will be swept away by the water stream, and the ability as a group will not be exhibited. In addition, since there are a great variety of microorganisms in river water, it is possible that the growth of desirable and useful microorganisms may be hindered by microorganisms of other species.
However, it has not been sufficiently confirmed whether or not the microorganisms are segregating, and whether or not the microorganisms compete with each other for survival as seen in higher animals and plants. It has been confirmed that the tissue serves as a habitat for soil bacteria, the production of antibiotics found in some species of actinomycetes, the antagonistic relationship between filamentous fungi and bacteria, or the bacterial predatory Bederovibrio and bacterium. The discovery of phages suggests that some sort of order should exist in the microbial world as well.

【0006】本発明者は、先に特開昭62-186730 号に係
る発明をし、非吸水性の化学繊維などからなる非吸水材
を水面に浮かべることにより、水中溶存酸素量を増加さ
せることを提案したが、今般、先発明から一歩を進め、
水中の有用好気的微生物に酸素と棲み家とを提供するこ
とが究極的に水質改善に役立つであろうことを発想し、
この発想を簡単に実現する手段につき検討を加えた結
果、本発明に到達した。
The present inventor has previously made an invention relating to Japanese Patent Application Laid-Open No. 62-186730, and increases the amount of dissolved oxygen in water by floating a non-water-absorbing material such as a non-water-absorbing chemical fiber on the water surface. However, we have taken a step forward from the previous invention,
The idea that providing oxygen and habitat to useful aerobic microorganisms in water will ultimately help improve water quality,
As a result of studying means for easily realizing this idea, the present invention has been achieved.

【0007】 概要 以上の構想に基づき、本発明は、好気性微生物を担持し
又は担持しうる疎水性の多孔質材を対象水と接触させる
ことを特徴とする水質改善法を要旨とする。以下、項分
けして発明を構成する要素等につき項分けして説明す
る。
[0007] Based on the above concept, the gist of the present invention is a water quality improving method characterized by bringing a hydrophobic porous material carrying or capable of carrying an aerobic microorganism into contact with target water. Hereinafter, the elements constituting the invention will be described by dividing them into items.

【0008】 好気的微生物 本発明における“好気的微生物”なる用語は、植物性で
あると動物性であるとを問わず、好気的又は通性嫌気的
に生育して有機又は無機物を資化する性質を有する顕微
鏡的な生物を意味する。ここに該微生物の電子供与体と
なる物質は、通常有機物であるが、場合により、硫化水
素、硝酸塩、アンモニアなども栄養源となりうる。特に
通性嫌気性微生物は、嫌気的条件下でも発育しうるの
で、高温の水中や水底等の溶存酸素量の低下した場所で
も増殖しうるという利点がある。
Aerobic Microorganism The term “aerobic microorganism” according to the present invention, whether plant or animal, grows aerobically or facultatively and anaerobically to form organic or inorganic substances. It means a microscopic organism that has the property of assimilating. Here, the substance serving as the electron donor of the microorganism is usually an organic substance, but depending on the case, hydrogen sulfide, nitrate, ammonia, etc. can also serve as a nutrient source. In particular, facultative anaerobic microorganisms can grow even under anaerobic conditions, and thus have an advantage that they can grow even in places where the amount of dissolved oxygen is low, such as high-temperature water and the water bottom.

【0009】本発明の実施に好適な好気性微生物の種類
を一義的に特定するのは困難であるが、活性汚泥中で優
先種となる原生動物として有柄鞭毛虫類に属するVoltic
ella,Carchesium,Zoothaminium,Opercularia,Epistytis
などの微生物は、一般的に有用である。またZoogloes,S
paerotilusなどの細菌も有効に利用される。この他、Ni
torosomonas,Azotobacter,Rhizobium などの硝化菌類、
Erythrobacter 、Rho-dospirilum、Rhodopseudomonas な
どの光合成細菌及び藍藻類も好気性微生物として利用で
きる。とりわけ、藍藻の酸素発生能力は非常に大である
から、BODの低減に特に有効である。但し、本発明の
趣旨は、好気性有機物分解菌に対し増殖に必要な酸素と
棲み家とを与えることであるので、特定微生物の使用は
要旨ではなく、次項で説明する疎水性多孔質材が水と接
触したとき、当該水中に存在した好気的微生物が該材又
は該材が担持する微生物用担体中に自然に着生する場合
を包含する。なお、本発明を海棲養殖魚介類用の生簀材
料として利用するときは、好気性微生物として耐塩性又
は好塩性のものを選ぶ必要がある。
Although it is difficult to unambiguously identify the type of aerobic microorganism suitable for the practice of the present invention, Voltic which belongs to the dinoflagellate as a protozoa which is a priority species in activated sludge.
ella, Carchesium, Zoothaminium, Opercularia, Epistytis
Microorganisms such as are generally useful. See also Zoogloes, S
Bacteria such as paerotilus are also effectively used. Besides this, Ni
nitrifying fungi such as torosomonas, Azotobacter, Rhizobium,
Photosynthetic bacteria such as Erythrobacter, Rho-dospirilum, Rhodopseudomonas and cyanobacteria can also be used as aerobic microorganisms. In particular, cyanobacteria have a very large oxygen generating ability, and are particularly effective in reducing BOD. However, the purpose of the present invention is to give oxygen and habitat necessary for growth to aerobic organic matter degrading bacteria, so the use of specific microorganisms is not the gist, and the hydrophobic porous material explained in the next section is The case where the aerobic microorganisms existing in the water spontaneously settle in the material or the carrier for microorganisms carried by the material when contacted with water. When the present invention is used as a cage material for marine aquaculture fish, it is necessary to select salt-resistant or salt-resistant aerobic microorganisms.

【0010】 担体 本発明における担体としては、疎水性多孔質材が利用さ
れる。ここに疎水性多孔質材というのは、例えば、ポリ
プロピレン、ポリエチレン、ポリエチレンテレフタレー
ト、ポリアミド、ポリビニルクロライド、ポリビニリデ
ンクロライド、ポリアクリロニトリル、ポリウレタン等
の吸水性の乏しい合成繊維又は天然ゴム若しくは合成ゴ
ムから作られた編組物、織成物、不織布又はスポンジを
意味するが、発明目的上、特に疎水性の強いポリオレフ
ィン系繊維から造られた編組物、織成物又は不織布が好
ましい。なお、色彩は通常無色でよいが、微生物の増殖
を助けるためには、黄色、橙黄色乃至赤色系の紫外線遮
断性の色彩に着色されている方が好ましい。
Carrier A hydrophobic porous material is used as the carrier in the present invention. The hydrophobic porous material here is made of, for example, polypropylene, polyethylene, polyethylene terephthalate, polyamide, polyvinyl chloride, polyvinylidene chloride, polyacrylonitrile, polyurethane, or other synthetic fibers having poor water absorption, or natural rubber or synthetic rubber. The above means a braid, a woven fabric, a nonwoven fabric or a sponge, but for the purpose of the invention, a braid, a woven fabric or a non-woven fabric made of particularly highly hydrophobic polyolefin fibers is preferable. The color is usually colorless, but in order to promote the growth of microorganisms, it is preferable that the color is yellow, orange-yellow to reddish UV blocking color.

【0011】以上の多孔質材は、シート状、管状又は袋
状の形態を有するのが望ましく、所望により、管状又は
袋状に成形された内部に綿、落綿、木綿、鋸屑、腐葉
土、鹿沼土、燻炭、ピートモス、赤玉土、蛭石、パーラ
イト、水苔、ヘゴ末、樹皮末、寒天、グルコマンナン、
カルボキシメチルセルロース、アルギン酸、ゼオライ
ト、アルミナ、シリカゲル又はスポンジゴム、ビスコー
ススポンジ、発泡ウレタン若しくはポリスチロール屑な
どの微生物用担体を含むことができる。本担体も成るべ
く水で膨潤しない性質のものが好ましい。
The above-mentioned porous material preferably has a sheet-like, tubular or bag-like form. If desired, the inside of the tube-like or bag-like molded product is made of cotton, lint, cotton, sawdust, humus, Kanuma. Soil, smoked charcoal, peat moss, red jade clay, vermiculite, perlite, water moss, hego powder, bark powder, agar, glucomannan,
It may contain a carrier for microorganisms such as carboxymethyl cellulose, alginic acid, zeolite, alumina, silica gel or sponge rubber, viscose sponge, urethane foam or polystyrene waste. It is preferable that the carrier also has a property of not swelling with water as much as possible.

【0012】更に所望により、各種の糖類又はその変性
物(例えばグルコース、スタキオース、メリビオース、
ショ糖脂肪酸エステル等)、尿素、硫安、難溶性リン酸
塩類、アミノ酸類(例えばグリシン)、各種ビタミン類
(例えばチアミン、ニコチン酸アミド、葉酸、ビオチン
等)、麦芽抽出物、廃糖蜜、酵母抽出物、コーンスティ
ープリカ−、肉エキス、微量必須元素等の微生物用栄養
源を含有していてもよい。これら成分の中、水に易溶性
の成分は、例えばチアミンを硝酸塩の形に変形したり、
又はデキストリン(好ましくはシクロデキストリン)に
包接させたり、或はシリカゲル、ゼオライト、活性炭、
アルミナなどの吸着材に担持させたりするのが望まし
い。しかしながら、多くの場合、対象水自身が高BOD
の、即ち、微生物にとって栄養水であるから、一般に特
別な栄養源の補給は不必要であり、ときたま必須アミノ
酸、ビオチンなどを補給すれば足りる。
If desired, various sugars or modified products thereof (eg glucose, stachyose, melibiose,
Sucrose fatty acid ester, etc.), urea, ammonium sulfate, sparingly soluble phosphates, amino acids (eg glycine), various vitamins (eg thiamine, nicotinic acid amide, folic acid, biotin, etc.), malt extract, molasses, yeast extraction Foods, corn steep liquor, meat extract, trace essential elements, etc., may be contained as nutrient sources for microorganisms. Among these components, the readily water-soluble component transforms thiamine into the form of nitrate,
Or inclusion in dextrin (preferably cyclodextrin), or silica gel, zeolite, activated carbon,
It is desirable to support it on an adsorbent such as alumina. However, in many cases, the target water itself has a high BOD.
That is, since it is nutrient water for microorganisms, it is generally unnecessary to supplement a special nutrient source, and sometimes it is sufficient to supplement essential amino acids, biotin and the like.

【0013】上記多孔質材は一般に水より軽いから、対
象水に適用すると水面に浮遊する。従って、若し水底又
は水面と水底との間に適用したければ、水より重い担体
を適宜併用するのがよい。
Since the above-mentioned porous material is generally lighter than water, it floats on the water surface when applied to the target water. Therefore, if it is desired to apply it to the water bottom or between the water surface and the water bottom, a carrier heavier than water is preferably used in combination.

【0014】 適用形態 本発明において、多孔質材を対象水に適用するやり方に
は種々の形式がある。最も簡単な方法は、シート状の多
孔質材に適当なアンカーを付して又は該材を岸辺から繋
索を用いて水面に浮かせる方法である。この方法は簡単
であるが、シート状多孔質材自身は多量の微生物を担持
する程の空間を有しないから、本シートをフロートと兼
用して該材から内部に微生物用担体(所望により持久的
な微生物用栄養源を含む)を入れた管状の多孔質材を懸
垂するのがよい。或は、シート状多孔質材を溝渠の上縁
からその側壁から底部及び対向する側壁に沿って他方の
上縁にまで跨がらせたり、又は一方若しくは両方の側壁
に沿わせて添設し又は底部のみに敷設する方法もある。
Application Form In the present invention, there are various types of methods for applying the porous material to the target water. The simplest method is to attach a suitable anchor to a sheet-shaped porous material or float the material on the water surface from the shore using a tether. This method is simple, but since the sheet-shaped porous material itself does not have a space for supporting a large amount of microorganisms, this sheet is also used as a float to allow the microorganism carrier (in the case of permanent It is preferable to suspend a tubular porous material containing various microbial nutrients). Alternatively, the sheet-like porous material may extend from the upper edge of the ditch to the other upper edge along the side wall from the side wall to the bottom and the opposite side wall, or may be installed along one or both side walls, or There is also a method of laying only on the bottom.

【0015】また別の形式として多孔質材を管状乃至袋
状の形態として、内部にビニロン綿等の微生物用担体を
入れたものを、水面に浮かせたり、水底に沈めたり又は
水中に懸垂させる方法がある。いづれの形式も多孔質材
が多量の微生物用担体を担持できるから、多量のBOD
負荷を処理できるという長所がある。特に管状のもの
は、大気中へ引き出した管の一端から所望により空気、
微生物用栄養源などを積極的に供給することにより、一
層浄化効率を上げることができる。
As another form, a method of suspending a porous material in the form of a tube or a bag in which a carrier for microorganisms such as vinylon cotton is placed on the water surface, submerged in the water bottom or suspended in water. There is. In either case, since the porous material can support a large amount of microbial carrier, a large amount of BOD can be obtained.
It has the advantage of being able to handle the load. Especially tubular ones, if desired air from one end of the pipe drawn into the atmosphere,
Purification efficiency can be further improved by positively supplying a nutrient source for microorganisms.

【0016】さらに特殊な方式として、レンズで菌叢に
集光する方法がある。この方式は、多くの光合成菌又は
藍藻のような、光合成を行う微生物に対し好適に利用さ
れる。
[0016] As a more special method, there is a method of focusing light on the microflora with a lens. This method is preferably used for many photosynthetic microorganisms such as photosynthetic bacteria or cyanobacteria.

【0017】 用途 本発明方法は、水質の低下した河川、湖沼、溜め池など
の水質向上、養魚池、生簀、鑑賞魚用水槽の水質低下防
止などに対し、省エネルギー的水質向上手段として広く
利用できる。
Application The method of the present invention can be widely used as an energy-saving water quality improving means for improving the water quality of rivers, lakes and marshes, reservoir ponds, etc. where the water quality has deteriorated, and preventing the water quality deterioration of fish ponds, cages, and ornamental fish tanks. .

【0018】[0018]

【作用】本発明を構成する疎水性多孔質材は、自体大き
な表面積を有すると共に、その無数の空間内に水中好気
的微生物に対し好適な住み家を提供すると同時に毛管作
用により空気/水界面間のガス交換を活発にする。それ
と同時に、前記無数の空間は、該微生物を補食するプラ
ンクトン等から微生物を保護するから、該微生物は富化
した酸素により活発に増殖して水中有機物を活発に分
解、無機化する。かつ、該菌の菌勢が活発となるにつ
れ、コロニーを形成しながら四方八方へ拡散して菌体と
水との接触面積が大きくなり、大きな浄化能力を発揮す
るようになる。このようにして、好気性微生物の増殖が
盛んとなるにつれ、悪臭発生の原因となる嫌気性菌の増
殖も押さえられ、水底のヘドロも次第に減少する。特
に、藍藻類は酸素を水中に提供するので、下層の有機物
資化細菌の増殖が増加する。さらにある種の光合成細菌
は、水底のヘドロなどから発生する硫化水素を脱水素し
て硫黄へ変化させるから、これら微生物の綜合作用によ
り水質が向上する。なお、多孔質材は、深層への酸素供
給を活発化するため、なるべく水面上から水底まで垂直
に分布していることが好ましい。
The hydrophobic porous material constituting the present invention has a large surface area itself, and provides a suitable residence for aerobic microorganisms in water in its innumerable space, and at the same time, it has an air / water interface by capillary action. Activate gas exchange between. At the same time, the innumerable space protects the microorganisms from plankton and the like that feed on the microorganisms, so that the microorganisms actively proliferate due to enriched oxygen and actively decompose and mineralize water organic matter. Moreover, as the vigor of the bacterium becomes active, it spreads in all directions while forming a colony, and the contact area between the bacterium and water becomes large, thereby exerting a large purification ability. In this way, as the growth of aerobic microorganisms increases, the growth of anaerobic bacteria that cause the generation of malodor is also suppressed, and the sludge on the bottom of the water gradually decreases. In particular, cyanobacteria provide oxygen to the water, thus increasing the growth of underlying organic matter-utilizing bacteria. Furthermore, some photosynthetic bacteria dehydrogenate hydrogen sulfide generated from sludge on the bottom of the water and convert it into sulfur, so the water quality is improved by the combined action of these microorganisms. The porous material is preferably distributed vertically from the water surface to the water bottom as much as possible in order to activate oxygen supply to the deep layer.

【0019】以上の作用に加え、多孔質材は、クロマト
グラフ的作用を持ち、水中に溶存する塩類を系外へ析出
させることにより濃縮する作用を奏するから、動物体か
ら排出されるナトリウム等の塩類濃度を低下させること
により、一層水質の向上に貢献する。なお、微生物とし
て対象水中に分布するものに替え、対象水の水質に適し
た高度の有機物乃至有害無機物分解性のものを選択する
と、一層の浄水効果を期待できる。
In addition to the above actions, the porous material has a chromatographic action and concentrates by precipitating salts dissolved in water out of the system. By reducing the salt concentration, it will contribute to further improvement of water quality. It should be noted that a further water purification effect can be expected by replacing the microorganisms distributed in the target water with microorganisms having a high degree of decomposition of organic substances or harmful inorganic substances suitable for the water quality of the target water.

【0020】以上要するに、本発明は、自然の炭素、窒
素及び硫黄などの元素循環系の中、河水などの汚染成分
である有機物、アンモニア、硫化水素等が微生物の作用
により無害の炭酸ガス、窒素、硫黄などへ変化する自浄
作用を、疎水性多孔質材の接触面積の大きさと、多孔性
とを利用して促進、助成しようとするものであって、本
質的に動力を必要としないから、汚染水の浄化手段とし
て合理的な方法である。
In summary, according to the present invention, in the natural elemental circulation system of carbon, nitrogen and sulfur, organic substances, ammonia, hydrogen sulfide, etc., which are pollutants of river water, etc. are harmless by the action of microorganisms, carbon dioxide, nitrogen. The purpose is to promote and assist the self-cleaning action that changes to sulfur, etc. by utilizing the size of the contact area of the hydrophobic porous material and the porosity, and essentially no power is required. This is a rational method for purifying contaminated water.

【0021】[0021]

【実施例】以下、実施例により発明実施の態様を説明す
るが、例示は単に説明用のもので、発明思想の制限又は
限定を意味するものではない。
The present invention will now be described in more detail by way of examples, but the examples are merely for the purpose of illustration and are not meant to limit or limit the inventive idea.

【0022】実施例1 水田の湛水(豊富に藍藻を含む)中にポリプロピレン製
織布を浸漬したものを容量50lの金魚用水槽の狭い側の
側面に添設し、これに汚染した河水(微かに臭気あり)
を満たして該槽の底部に置いたヘドロ付小石の状態を観
察した。実験10日後、織布の表面には一面に藍藻が付着
し、臭気も殆ど感じられなくなると共に、ヘドロが石の
表面から剥離した。これに反し、単に河水を満たしただ
けの対照水槽には何の変化もなかった。
Example 1 A woven polypropylene cloth was immersed in a submerged water (abundantly containing cyanobacteria) in a paddy field, which was attached to the narrow side surface of a goldfish aquarium having a capacity of 50 l, and polluted river water ( There is a slight odor)
Was observed and the state of the pebbles with sludge placed at the bottom of the tank was observed. Ten days after the experiment, cyanobacteria adhered to the entire surface of the woven fabric, the odor was hardly felt, and the sludge peeled off from the surface of the stone. On the contrary, there was no change in the control tank, which was simply filled with river water.

【0023】実施例2 図1は、多孔質材としてシート状の織布1を河川の浄化
に応用する例を示す。本例において、ポリプロピレン製
の織布1の下面から内部に綿状のポリプロピレンとゼオ
ライトとの混合担体5(予めEpistytis の培養菌体を吸
着)を充填した、同じくポリプロピレン製のマルチフィ
ラメントを編組してなる筒状体2(詳細は図2参照)が
多数吊り下げられると共に、碇Aにより水底に繋止され
ている。
Example 2 FIG. 1 shows an example in which a sheet-shaped woven fabric 1 as a porous material is applied to the purification of a river. In this example, a polypropylene multi-filament, which is the same as the polypropylene woven cloth 1 filled with a cotton-like polypropylene / zeolite mixed carrier 5 (adsorbing culture cells of Epistytis in advance) from the bottom to the inside, is also braided. A large number of tubular bodies 2 (see FIG. 2 for details) are suspended and are anchored to the bottom of the water by anchors A.

【0024】本例においては、新鮮な空気が常時織布1
から筒状体2を構成する繊維束を介して該筒状体の内部
へ供給されるから、内部で増殖する菌叢は常に豊富な酸
素を利用して活発に有機物分解、硝化などの作用を営
む。なお、使用微生物のエピスチチスは、増殖につれフ
ロックを形成して織り目に詰まるから、水流の速度が速
くても剥離し難い。
In this example, fresh air is always woven 1
Is supplied to the inside of the tubular body through the fiber bundles that form the tubular body 2, the flora that grows inside constantly uses abundant oxygen to actively perform organic substance decomposition and nitrification. Run. It should be noted that since the microorganisms used, Epististis, form flocs as they grow and become clogged in the texture, they are difficult to peel off even if the water flow rate is high.

【0025】実施例3 図3は、本発明をゴルフ場などの排水溝や灌漑用水路な
どの浄化に適用した例を示す。本例において、ポリプロ
ピレン製の矩形の織布1は、アンカーA,Aを用いて溝
Tの一方の縁から他方の縁にかけて溝の側壁から底部及
び他方の側壁に沿って添設されると共に、両端部が杭
P,Pにて固定されている。
Example 3 FIG. 3 shows an example in which the present invention is applied to the purification of drainage channels and irrigation channels of golf courses and the like. In this example, the rectangular woven fabric 1 made of polypropylene is attached from the side wall of the groove to the bottom and the other side wall from one edge to the other edge of the groove T by using the anchors A and A. Both ends are fixed by piles P, P.

【0026】本例においては、自然に織布1に着生した
好気性微生物が織布1の織り目を経て供給される空気に
より増殖を促進され、水中のBODを低減させるが、特
に溝Tの側壁や底面では水流速度が極端に低下するの
で、織布1の毛管作用により豊富に酸素が供給されるこ
とは、該微生物の発育に好条件を提供する。
In this example, the aerobic microorganisms spontaneously adhering to the woven cloth 1 are promoted to grow by the air supplied through the weaves of the woven cloth 1 to reduce the BOD in water. Since the water flow velocity on the side wall and the bottom face is extremely reduced, the abundant supply of oxygen by the capillary action of the woven fabric 1 provides favorable conditions for the growth of the microorganism.

【0027】実施例4 図4は、前例における多孔質材1をポリプロピレン繊維
製編組物からなる筒状体2に変更すると共に、該筒状体
の内部へ綿状ポリプロピレン繊維(担体)5を充填し、
更に該綿状繊維内に細い小孔7,7・・付ゴムチューブ
6を貫通させた例を示す。
Example 4 In FIG. 4, the porous material 1 in the previous example was changed to a tubular body 2 made of a braided polypropylene fiber, and a cotton-like polypropylene fiber (carrier) 5 was filled inside the tubular body. Then
Further, an example is shown in which the rubber tube 6 with small holes 7, 7, ... Is penetrated into the cotton-like fiber.

【0028】本例におけるゴムチューブ6は、必要に応
じ本チューブを介して微生物培養液、微生物用液状栄養
源又は空気を供給するのに役立つ。従って、本例は状況
に応じて優先微生物の種類を変更したり、増殖程度を変
化させたりするのに便利である。
The rubber tube 6 in this example serves to supply a culture solution of microorganisms, a liquid nutrient source for microorganisms or air through the tube as required. Therefore, this example is convenient for changing the type of priority microorganism or changing the growth degree depending on the situation.

【0029】実施例5 図5は、別の多孔質材の例を示す。本例の多孔質材は、
ポリプロピレン製の編布(ニット)3からなる袋状の外
被の内部にウレタンフォーム5'を充填してなる。
Example 5 FIG. 5 shows an example of another porous material. The porous material of this example is
Urethane foam 5'is filled inside a bag-shaped outer cover made of polypropylene knit 3.

【0030】本例の多孔質材を例えば鑑賞魚用水槽に浮
かべると、外被1'から常時新鮮な空気がスポンジ5'へ供
給され、着生した好気性微生物の増殖を促す。全体は予
め藍藻培養液に浸漬してから水槽内へ施用するのが望ま
しい。
When the porous material of this example is floated on, for example, a water tank for ornamental fish, fresh air is constantly supplied from the outer cover 1'to the sponge 5'to promote the growth of the aerobic microorganisms that have settled. It is desirable that the whole be immersed in a cyanobacterial culture solution in advance and then applied to the water tank.

【0031】実施例6 図6は、特殊な例として多孔質材が自体集光レンズを具
備している例を示すもので、合成樹脂製の集光レンズ8
の中央部に穿たれた孔9を通して内部に球状フロート10
を包みこむようにポリプロピレン繊維製の丸編みニット
4の先端部が突出すると共に、下方に実施例2と同様の
重り兼用筒状多孔質材が吊り下げられている。
Embodiment 6 FIG. 6 shows an example in which a porous material is provided with a condensing lens itself as a special example, and a condensing lens 8 made of synthetic resin is shown.
Spherical float 10 inside through hole 9 drilled in the center of
The tip of the circular knit 4 made of polypropylene fiber is projected so as to wrap around, and a cylindrical porous material that also serves as a weight and is hung is hung below the same.

【0032】本例の多孔質材4は、水面から突き出たニ
ット4の先端部4aから筒状体2の内部まで常時空気が
供給されると共に、レンズ9により集光された強い光線
が水面下を照らすから、特に寒冷時における光合成細菌
や藍藻の発育が優れている。従って、これを多数養魚池
などの水面に浮かべておくと、水中の酸素が富化して魚
介類に好影響を与えると同時に水質の汚染が抑制され
る。
In the porous material 4 of this example, air is constantly supplied from the tip portion 4a of the knit 4 protruding from the water surface to the inside of the tubular body 2, and the strong light beam condensed by the lens 9 is under the water surface. Therefore, the growth of photosynthetic bacteria and cyanobacteria is excellent especially in cold weather. Therefore, if a large number of these are floated on the surface of water such as a fish pond, oxygen in the water will be enriched, which will have a favorable effect on seafood, and at the same time, water pollution will be suppressed.

【0033】実施例7 実施例2と同様の橙色袋状多孔質材(60mm×25mmφ;内
部に綿状ポリプロピレンを充填)にフスマに吸着させた
通性嫌気性細菌(Pseudomonas sp.)の培養物各1gを収
容し、これを事前に曝気し又は曝気しない各2lの大和
川(堺市香ヶ丘町)の河水各2lを容れた3個のポリ容
器(130 ×150 ×200mm)中に夫々5個づつ収容し(但し
試料Bは水面に浮遊配置、試料Cは水底に沈下配置、試
料Aには添加せず)、平成3年1月13日から21日に至る
9日間の水質変化を被検水のpH及び酸素含有量(DO)
変化により測定した。結果を表1に示す。
Example 7 A culture of a facultative anaerobic bacterium (Pseudomonas sp.) Adsorbed on a bran to an orange bag-like porous material (60 mm × 25 mmφ; filled with cotton-like polypropylene inside) similar to that of Example 2. Each of them was placed in 3 plastic containers (130 x 150 x 200 mm) containing 1g of each and 2l of each river water of Yamatogawa (Kagaoka-cho, Sakai City) which was aerated or not aerated beforehand. 5 pieces were stored (however, sample B was placed on the surface of the water, sample C was placed on the bottom of the water, and was not added to sample A), and the change in water quality for 9 days from January 13 to 21, 1991 PH and oxygen content (DO) of test water
It was measured by the change. The results are shown in Table 1.

【表1】 [Table 1]

【0034】表1から明らかなように、多孔質材を添加
した試料のpH及び溶存酸素量は、対照に比べていづれも
高くなる傾向がある。しかし多孔質材を被処理水の水面
に浮かべるのと水底に沈めるのとの間では有意の差異は
認められなかった。
As is clear from Table 1, the pH and dissolved oxygen content of the sample to which the porous material is added tend to be higher than those of the control. However, no significant difference was observed between floating the porous material on the surface of the treated water and submerging it on the water bottom.

【0035】実施例8 図7は、発明の別の実施例を示す破断斜視図である。本
例では、ドーナッツ状のフロート10' の内部に同じく好
気性微生物を吸着したドーナツ状の発泡ポリウレタン製
芯材(担体)5'が挿入されると共に、該芯材5'の周囲を
更にポリプロピレン製ニット4で被覆してなる。なお、
装飾用の造花11が芯材5'の孔5'a の内部に挿着されてい
る。
Embodiment 8 FIG. 7 is a cutaway perspective view showing another embodiment of the invention. In this example, a doughnut-shaped polyurethane foam core material (carrier) 5 ', which also adsorbs aerobic microorganisms, is inserted inside the donut-shaped float 10', and the periphery of the core material 5'is further made of polypropylene. It is covered with a knit 4. In addition,
The artificial flower 11 for decoration is inserted inside the hole 5'a of the core material 5 '.

【0036】本例の多孔質材を鑑賞魚用アクアリアムに
浮かべると、芯材内部の微生物が次第に増殖して水槽内
の水を浄化すると同時に、魚の活動に伴って水面を浮遊
し人の眼を楽しませる。因に、本例の多孔質材を先述ポ
リプロピレン製織布等を外被として自由に拡大してゴル
フ場の池等に人口島として浮遊させることも可能であ
り、島は風により揺動(造花として大型の造木又は天然
樹を使用する)してエアレーションを活発にする。
When the porous material of this example is floated on the aquarium for viewing fish, microorganisms inside the core material gradually grow to purify the water in the aquarium, and at the same time, the water surface floats with the activity of the fish and becomes a human eye. Entertain. By the way, it is possible to freely expand the porous material of this example by using the polypropylene woven cloth etc. as an outer cover and suspend it as a population island in a pond of a golf course, etc. Use large trees or natural trees as) to activate aeration.

【0037】実施例9 図8は、本発明を下水管の浄化用に適用する場合の一例
を示す部分破断側面図である。本例の多孔質材は、ポリ
プロピレン糸製織布からなる管状体4の内部にウレタン
フォーム製担体5'を断続的に充填してなる。
Embodiment 9 FIG. 8 is a partially cutaway side view showing an example in which the present invention is applied to purify a sewer pipe. The porous material of this example is obtained by intermittently filling a urethane foam carrier 5'within a tubular body 4 made of polypropylene yarn woven cloth.

【0038】本例の多孔質材を例えば排水桝を経て下水
管中に挿入すると、排水は多孔質材の外面の凹凸部に触
れて乱流(Tf)となり、編組物3及び担体5'に増殖した微
生物に対し豊富な酸素を供給するから、活発な排水浄化
作用が行われる。なお、交換は多孔質材の一端部に設置
された鳩目12に結び付けた紐又は針金を引っ張って行
う。
When the porous material of this example is inserted into a sewer pipe through, for example, a drainage basin, the drainage comes into contact with irregularities on the outer surface of the porous material and becomes a turbulent flow (Tf) to the braid 3 and the carrier 5 '. Since abundant oxygen is supplied to the grown microorganisms, active purification of wastewater is performed. The exchange is performed by pulling a string or wire tied to the eyelet 12 installed at one end of the porous material.

【0039】実施例10 図9は、本発明を猫用トイレの脱臭に利用した例を示す
部分断面図である。本例の多孔質材は、ポリプロピレン
製織布1,1の間にリゾビウム菌、アゾトバクター菌及
びニトロソモナス菌の純粋培養物とマメ科植物の根エキ
スを担持させた綿状ポリプロピレン繊維5'' をサンドイ
ッチ状に挟んだシートである。
Embodiment 10 FIG. 9 is a partial cross-sectional view showing an example in which the present invention is used for deodorizing a cat litter box. The porous material of this example is composed of a polypropylene woven cloth 1, 1 and a cotton-like polypropylene fiber 5 '' carrying a pure culture of Rhizobium, Azotobacter and Nitrosomonas and legume root extract. It is a sandwiched sheet.

【0040】以上のシートを猫用トイレTTのすの子M上
に敷いて上面に砂SDを置くと、侵入した尿中の尿素等か
ら生じるアンモニアが微生物の作用で硝酸塩に酸化され
るから、糞便の付着した砂を除くだけで長く無臭状態を
維持できる。
When the above sheet is laid on the child M of the cat litter box TT and sand SD is placed on the upper surface, ammonia generated from urea and the like invaded in the urine is oxidized to nitrate by the action of microorganisms. The odorless state can be maintained for a long time only by removing sand with feces attached.

【発明の効果】設備上説明した如く、本発明は、微生物
の活性を利用して、簡単で設備費が安く、どの河川や排
水溝にも適用可能であって、河川や排水溝の浄化のみな
らず、養魚池、生簀、活魚輸送槽、アクアリアム(金魚
や熱帯魚の飼育水槽)の水質低下防止及びペット動物の
尿の浄化にも役立つ水質改善法を提供できたことによ
り、産業界及び民生に対して寄与しうる。
Industrial Applicability As described above, the present invention utilizes the activity of microorganisms, is simple and has a low equipment cost, and can be applied to any river or drain, and only purifies rivers or drains. In addition, by providing water quality improvement methods that are useful for preventing water quality deterioration in fish ponds, cages, live fish transport tanks, and aquarium (gold and tropical fish tanks) and for purifying urine of pet animals, industry and commercial Can contribute to.

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

【図1】本発明の一実施例を示す模型的断面図FIG. 1 is a schematic sectional view showing an embodiment of the present invention.

【図2】図1における筒状体の拡大切欠断面図FIG. 2 is an enlarged cutaway sectional view of the tubular body in FIG.

【図3】本発明のなお別の例を示す模型的断面図FIG. 3 is a schematic sectional view showing still another example of the present invention.

【図4】本発明の更に別の例を示す部分拡大切欠断面図FIG. 4 is a partially enlarged cutaway sectional view showing yet another example of the present invention.

【図5】本発明の実施に使用される多孔質材の別例を示
す切欠断面図
FIG. 5 is a cutaway sectional view showing another example of a porous material used for carrying out the present invention.

【図6】本発明の実施に使用される多孔質材の更に別の
例を示す切欠断面図
FIG. 6 is a cutaway sectional view showing still another example of a porous material used for carrying out the present invention.

【図7】発明の別の実施例を示す破断斜視図FIG. 7 is a cutaway perspective view showing another embodiment of the invention.

【図8】本発明を下水管の浄化用に適用する場合の一例
を示す部分破断側面図
FIG. 8 is a partially cutaway side view showing an example in which the present invention is applied to purification of a sewer pipe.

【図9】本発明を猫用トイレの脱臭に利用した例を示す
部分断面図
FIG. 9 is a partial cross-sectional view showing an example in which the present invention is used for deodorizing a cat litter box.

【符号の説明】[Explanation of symbols]

1 多孔質材(疎水性合成繊維製織布) 2 多孔質材(疎水性合繊繊維製筒状編組物) 3 多孔質材(疎水性合成繊維製編組布) 4 多孔質材(疎水性合成繊維製丸編みニット) 5 微生物用担体(合成綿・ゼオライト混合物) 5' 微生物用担体(ウレタンフォーム) 5'' 微生物用担体(合成綿) 6 ゴムチューブ 7 6の小孔 8 レンズ 9 8の透孔 10 球状フロート 10' ドーナッツ状フロート 11 造花 12 鳩目 A 碇 P 杭 SD 砂 T 溝渠 TT 猫用トイレ W 水 1 Porous material (hydrophobic synthetic fiber woven fabric) 2 Porous material (cylindrical braid made of hydrophobic synthetic fiber) 3 Porous material (hydrophobic synthetic fiber braided cloth) 4 Porous material (circular knitting made of hydrophobic synthetic fiber) 5 Microorganism carrier (mixture of synthetic cotton and zeolite) 5'Microorganism carrier (urethane foam) 5 '' microbial carrier (synthetic cotton) 6 rubber tube 7 6 small holes 8 lenses 98 through holes 10 spherical float 10 'donut-shaped float 11 artificial flowers 12 eyelet A anchor P pile SD sand T ditch TT cat litter W water

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.5 識別記号 庁内整理番号 FI 技術表示箇所 C02F 3/10 Z 6647−4D 3/34 101 D 7158−4D ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 5 Identification code Office reference number FI technical display location C02F 3/10 Z 6647-4D 3/34 101 D 7158-4D

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 好気性微生物を担持し又は担持しうる疎
水性の多孔質材を対象水と接触させることを特徴とする
水質改善法。
1. A method for improving water quality, which comprises bringing a hydrophobic porous material supporting or capable of supporting aerobic microorganisms into contact with target water.
【請求項2】 多孔質材がシート状である請求項1の方
法。
2. The method according to claim 1, wherein the porous material is in the form of a sheet.
【請求項3】 多孔質材が筒状である請求項1の方法。3. The method of claim 1, wherein the porous material is tubular. 【請求項4】 多孔質材が袋状である請求項1の方法。4. The method according to claim 1, wherein the porous material has a bag shape. 【請求項5】 多孔質材が微生物用担体を含む請求項1
〜4のいづれかの方法。
5. The porous material contains a carrier for microorganisms.
~ Any one of 4 methods.
【請求項6】 多孔質材に微生物用栄養源を供給する請
求項1〜5のいづれかの方法。
6. The method according to claim 1, wherein a nutrient source for microorganisms is supplied to the porous material.
JP4286691A 1991-02-14 1991-02-14 Water quality improvement method Expired - Fee Related JP2599834B2 (en)

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JP4286691A JP2599834B2 (en) 1991-02-14 1991-02-14 Water quality improvement method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4286691A JP2599834B2 (en) 1991-02-14 1991-02-14 Water quality improvement method

Publications (2)

Publication Number Publication Date
JPH05293A true JPH05293A (en) 1993-01-08
JP2599834B2 JP2599834B2 (en) 1997-04-16

Family

ID=12647959

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2599834B2 (en)

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0672697U (en) * 1993-04-01 1994-10-11 好一 山崎 Circulating contact back toilet
US5516687A (en) * 1994-04-08 1996-05-14 Interbio, Inc. Device and method for maintaining bacterial levels within an organic waste collection container
JP2006166741A (en) * 2004-12-14 2006-06-29 Taiho Ind Co Ltd Denitrification method of water for rearing aquatic animal, denitrification apparatus and filter medium for denitrification
WO2010067788A1 (en) * 2008-12-10 2010-06-17 Fujita Takurou Nitrate-removing bioreactor, method for forming nitrate-removing biofilm, and nitrate-removing method
JP2010253421A (en) * 2009-04-27 2010-11-11 Daiwa House Industry Co Ltd Activated carbon mat and method for purifying soil contaminated with hydrocarbon
KR101064738B1 (en) * 2011-05-06 2011-09-14 주식회사 현진기업 Screen module for purifying water and air using effective microoganims, method for purifying and apparatus for purifying water of fish-raising farm
JP2012125741A (en) * 2010-12-17 2012-07-05 Komatsu Seiren Co Ltd Water purification material
JP2015211933A (en) * 2014-05-01 2015-11-26 角川建設株式会社 Sewage purification device and sewage purification method
WO2016098711A1 (en) * 2014-12-15 2016-06-23 大谷 洋 Purification system, purification method using same, algal-proliferation controlling method, water-flow generation device, and purification device
JP2020048447A (en) * 2018-09-26 2020-04-02 信濃建設株式会社 Water quality purification agent for aquarium fish
JP2021065834A (en) * 2019-10-23 2021-04-30 トリゼンオーシャンズ株式会社 Bottom sediment environmental improvement material
JP2022055516A (en) * 2020-09-29 2022-04-08 和光技研株式会社 Culture service water sterilization tool

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4964261A (en) * 1972-10-23 1974-06-21
JPS51150871A (en) * 1975-06-19 1976-12-24 Kobe Steel Ltd Process for the purificati on of sewage
JPS54149254A (en) * 1978-05-13 1979-11-22 Seisan Gijiyutsu Kaihatsu Kenk Highhgrade preetreatment purifying method of service water and highhgrade preetreatment purifier that utilize said method
JPS5867395A (en) * 1981-09-17 1983-04-21 リンデ・アクチエンゲゼルシヤフト Method and apparatus for biologically purifying waste water
JPS63310696A (en) * 1987-06-11 1988-12-19 Taisei Corp Biological membrane support for treating waste water
JPH0283006U (en) * 1988-12-16 1990-06-27

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4964261A (en) * 1972-10-23 1974-06-21
JPS51150871A (en) * 1975-06-19 1976-12-24 Kobe Steel Ltd Process for the purificati on of sewage
JPS54149254A (en) * 1978-05-13 1979-11-22 Seisan Gijiyutsu Kaihatsu Kenk Highhgrade preetreatment purifying method of service water and highhgrade preetreatment purifier that utilize said method
JPS5867395A (en) * 1981-09-17 1983-04-21 リンデ・アクチエンゲゼルシヤフト Method and apparatus for biologically purifying waste water
JPS63310696A (en) * 1987-06-11 1988-12-19 Taisei Corp Biological membrane support for treating waste water
JPH0283006U (en) * 1988-12-16 1990-06-27

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0672697U (en) * 1993-04-01 1994-10-11 好一 山崎 Circulating contact back toilet
US5516687A (en) * 1994-04-08 1996-05-14 Interbio, Inc. Device and method for maintaining bacterial levels within an organic waste collection container
JP2006166741A (en) * 2004-12-14 2006-06-29 Taiho Ind Co Ltd Denitrification method of water for rearing aquatic animal, denitrification apparatus and filter medium for denitrification
WO2010067788A1 (en) * 2008-12-10 2010-06-17 Fujita Takurou Nitrate-removing bioreactor, method for forming nitrate-removing biofilm, and nitrate-removing method
JP2010137157A (en) * 2008-12-10 2010-06-24 Takuro Fujita Nitric acid removal bioreactor, method for generating nitric acid removal biofilm, and method for removing nitric acid
JP2010253421A (en) * 2009-04-27 2010-11-11 Daiwa House Industry Co Ltd Activated carbon mat and method for purifying soil contaminated with hydrocarbon
JP2012125741A (en) * 2010-12-17 2012-07-05 Komatsu Seiren Co Ltd Water purification material
KR101064738B1 (en) * 2011-05-06 2011-09-14 주식회사 현진기업 Screen module for purifying water and air using effective microoganims, method for purifying and apparatus for purifying water of fish-raising farm
JP2015211933A (en) * 2014-05-01 2015-11-26 角川建設株式会社 Sewage purification device and sewage purification method
WO2016098711A1 (en) * 2014-12-15 2016-06-23 大谷 洋 Purification system, purification method using same, algal-proliferation controlling method, water-flow generation device, and purification device
JP2020048447A (en) * 2018-09-26 2020-04-02 信濃建設株式会社 Water quality purification agent for aquarium fish
JP2021065834A (en) * 2019-10-23 2021-04-30 トリゼンオーシャンズ株式会社 Bottom sediment environmental improvement material
JP2022055516A (en) * 2020-09-29 2022-04-08 和光技研株式会社 Culture service water sterilization tool

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