JP2599834B2 - Water quality improvement method - Google Patents
Water quality improvement methodInfo
- Publication number
- JP2599834B2 JP2599834B2 JP4286691A JP4286691A JP2599834B2 JP 2599834 B2 JP2599834 B2 JP 2599834B2 JP 4286691 A JP4286691 A JP 4286691A JP 4286691 A JP4286691 A JP 4286691A JP 2599834 B2 JP2599834 B2 JP 2599834B2
- Authority
- JP
- Japan
- Prior art keywords
- water
- microorganisms
- water quality
- porous
- porous capillary
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Farming Of Fish And Shellfish (AREA)
- Biological Treatment Of Waste Water (AREA)
- Treatment Of Biological Wastes In General (AREA)
Description
【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。The present invention relates to a method for improving water quality which can be used in a wide variety of applications such as purification of rivers and drains having reduced water quality, prevention of water quality deterioration in fish ponds, fish cages, live fish transport tanks, aquariums and the like. About.
【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 that water quality in rivers and lakes will decline. The decrease in water quality is one of the manifestations of the environmental destruction of the earth macroscopically. Has significant effects on human life. Originally, a wide variety of aerobic microorganisms exist on the earth, and feed on nitrogen, carbon, and phosphorus compounds contained in spoiled food, human waste, animal carcasses, and domestic wastewater, which are the main causes of water quality degradation. As a source, it ultimately reduces these to nitrogen, carbon dioxide, etc., and river water is naturally purified by the self-cleaning action of these microorganisms.However, the concentration of population in cities, destruction of vegetation, Changes in the ecosystem, such as by spraying, have slowed the growth of these microorganisms and, consequently, their self-purification, 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。[0003] Problems of the prior art [0003] The fundamental means for water purification is to restore the ecosystem by dispersing the population, providing sewers, restoring forests, stopping the use of pesticides, and completely purifying industrial wastewater. is there. However, the implementation of these measures has taken many years and is not immediately urgent, and there are also economically difficult issues such as complete purification of industrial wastewater and suspension of use of pesticides. is there. In particular, complete sewerage is the most important issue, but currently available sewage treatment facilities include the trickling filter method, the rotating disk method, the surface aeration activated sludge method, the immersion filter method, the fluidized bed method, and the suspended bed method. Regardless of which suspended particle activated sludge method, diffused activated sludge method, deep shaft method, etc. are employed, large-scale equipment and large amounts of energy are required for pumps, compressors, etc. It is practically impossible to run a pipe from a wastewater source to a sewage treatment plant everywhere in Japan. In addition, the activated sludge discharged from the apparatus according to the processing amount has an extremely strong odor, and prevention of the odor around the treatment plant and disposal of the sludge are also problems for 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 which can be applied to any river or drainage by utilizing the activity of microorganisms, and is simple, inexpensive, and low in equipment cost. The purpose is to do. Another object of the present invention is to provide a water quality improvement method that is useful not only for rivers and drains, but also for preventing deterioration of water quality in fishponds, fish cages, live fish transport tanks, and aquariums (breeding tanks for goldfish and tropical fish). .
【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] Concept The chemical ability of microorganisms is outstanding compared to other organisms. For example, the amount of oxygen consumed per kg of body weight is about 200 ml per hour at 30 ° C. for humans, but it is azotobacter (G.Az.
tobacter) consumes 1,200,000 ml of oxygen (see Iwanami Shinsho 827, Tsutomu Hattori, “Earth Microorganisms” p. 58). Therefore, by utilizing the oxidizing ability of such microorganisms, organic compounds that are the main cause of pollution can be converted into CO 2 , N 2 , water, or
If it can be changed to a harmless inorganic substance such as NO 3 , a decrease in water quality can be prevented. However, the supply of oxygen to river water is limited to the interface with the atmosphere, so if the supply amount of oxygen is small, the function of the microorganisms of the present invention cannot be exhibited. In addition, even if the microorganisms are simply sprayed into the water, they are washed away by the water current and cannot exert their ability as a group. In addition, because there are a great variety of microorganisms in river water, the growth of preferred useful microorganisms may be hindered by other microorganisms.
However, whether or not the microorganisms are segregating, and furthermore, whether or not the microorganisms compete with each other for survival as seen in higher plants and animals have not yet been sufficiently confirmed, but at least aggregates in the soil It has been confirmed that the tissue serves as a habitat for soil bacteria, produces antibiotics found in certain species of actinomycetes, antagonizes fungi and bacteria, or has bacterial predatory properties such as Buderovibrio and bacteriosomes. The discovery of phage suggests that there must be some sort of order in the microbial world.
【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 inventor of the present invention made an invention according to Japanese Patent Application Laid-Open No. 62-186730, in which the amount of dissolved oxygen in water was increased by floating a non-water-absorbing material composed of non-water-absorbing chemical fibers on the water surface. However, recently, one step forward from the earlier invention,
Given 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 reached.
【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合成繊維のマルチフィラメントか
らなる多孔質毛管材を対象水と接触させることを特徴と
する水質改善方法を要旨とする。以下、これについて詳
しく説明する。SUMMARY Based on the above concept, the present invention provides a water quality improvement characterized by contacting a porous capillary material comprising multifilaments of hydrophobic synthetic fibers capable of carrying or carrying an aerobic microorganism with target water. The method is summarized. Hereinafter, this will be described in detail.
【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。[0008] The term "aerobic microorganism" in the present invention refers to an aerobic or facultatively anaerobic organic or inorganic substance that grows aerobically or facultatively regardless of whether it is vegetable or animal. A microscopic organism with assimilating properties. Here, the substance serving as the electron donor of the microorganism is usually an organic substance, but in some cases, hydrogen sulfide, nitrate, ammonia or the like can also be a nutrient source. In particular, facultative anaerobic microorganisms can grow even under anaerobic conditions, and therefore have the advantage that they can grow in places where the amount of dissolved oxygen is low, such as high-temperature water or water bottoms.
【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Vol
ticella,Carchesium,Zootha
minium,Opercularia,Episty
isなどの微生物が、一般的に有用である。また、Zo
ogloes,Spaerotilusなどの細菌も有
効に利用される。この他、Nitorosomona
s,Azotobacter,Rhizobiumなど
の硝化菌類,Erythrobacter,Rho−d
ospirilum,Rhodopseudomona
sなどの光合成細菌および藍藻類も好気性微生物として
利用できる。とりわけ、藍藻類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、
本発明の趣旨の一つは、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、要旨でなく、次項で説明する特殊な
多孔質毛管材が水と接触したとき、当該水中に存在した
好気性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、本発明の特殊
な多孔質毛管材を海棲養殖魚介類用の生簀材料として利
用するときは、好気生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 uniquely identify the types of aerobic microorganisms suitable for the practice of the present invention, Vol. Belonging to sessile flagellates as a protozoan which is a priority species in activated sludge
ticella, Carchesium, Zootha
minium, Operacularia, Episty
Microorganisms such as is generally useful. Also, Zo
Bacteria such as ogloes and Sparetilus are also effectively used. In addition, Nitrosomona
Nitrifying bacteria such as s, Azotobacter, Rhizobium, Erythrobacter, Rho-d
ospirilum, Rhodopseudomona
Photosynthetic bacteria such as s and cyanobacteria can also be used as aerobic microorganisms. In particular, since the oxygen generating ability of cyanobacteria is very large, it is particularly effective in reducing BOD. However,
One of the spirits of the present invention is to provide oxygen required for growth and a home for aerobic organic matter decomposing bacteria, so the use of specific microorganisms is not a gist, but a special porous material described in the next section. When the porous capillary material comes into contact with water, the aerobic microorganisms present in the water spontaneously grow on the material or the carrier for microorganisms carried by the material. When the special porous capillary material of the present invention is used as a cage material for marine cultured fish and shellfish, it is necessary to select a salt-resistant or salt-tolerant aerobic microorganism.
【0010】 担体 本発明における微生物を保持する担体としては、疎水性
合成繊維のマルチフィラメントからなる多孔質毛管材が
使用される。ここで、疎水性合成繊維のマルチフィラメ
ントからなる多孔質毛管材とは、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,ポリウレタン等の疎水性
合成繊維から作られた編組物,織成物,不織布等をい
う。このなかで、本発明の所定の効果が優れるという理
由から、疎水性が特に高いポリオレフィン系繊維から作
られた編組物,織成物,不織布等が好ましい。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 As a carrier for holding microorganisms in the present invention, a porous capillary material composed of multifilaments of hydrophobic synthetic fibers is used. Here, the porous capillary material composed of multifilaments of hydrophobic synthetic fibers is made of, for example, hydrophobic synthetic fibers such as polypropylene, polyethylene, polyethylene terephthalate, polyamide, polyvinyl chloride, polyvinylidene chloride, polyacrylonitrile, and polyurethane. Braided, woven or non-woven fabric. Among them, a braid, a woven fabric, a nonwoven fabric, and the like made of a polyolefin fiber having particularly high hydrophobicity are preferable because the predetermined effect of the present invention is excellent. The color may be generally colorless, but in order to assist the growth of microorganisms, it is preferable that the color is colored yellow, orange-yellow, or red, so as to block ultraviolet rays.
【0011】以上の多孔質毛管材は、シート状,管状
(筒状)又は袋状の形態をとることが好ましく、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,ピートモース,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。
本担体もなるべく水で膨潤しない性質のものが好まし
い。The above-mentioned porous capillary material is preferably in the form of a sheet, a tube (tubular) or a bag. If desired, the inside of the tube or bag is formed into cotton, cotton, cotton, cotton, cotton, or the like. Sawdust, mulch, Kanuma soil, charcoal, peat moose, akadama, vermiculite, perlite, water moss, stalk end, bark end, agar,
Microbial carriers such as glucomannan, carboxymethylcellulose, alginic acid, zeolites, alumina, silica gel or sponge gum, viscose sponges, urethane foam or polystyrene scraps can be included.
It is preferable that the carrier does not swell 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。Further, if desired, various sugars or modified products thereof (eg, glucose, stachyose, melibiose,
Sucrose fatty acid esters, etc.), urea, ammonium sulfate, poorly soluble phosphates, amino acids (eg, glycine), various vitamins (eg, thiamine, nicotinamide, folic acid, biotin, etc.), malt extract, molasses, yeast extract It may contain nutrients for microorganisms such as foods, corn steep liquor, meat extract, trace essential elements and the like. Of these components, those that are readily soluble in water, for example, transform thiamine into nitrate form,
Or inclusion in dextrin (preferably cyclodextrin) or silica gel, zeolite, activated carbon,
It is desirable to carry it on an adsorbent such as alumina. However, in many cases, the target water itself has a high BOD.
In other words, since it is nutrient water for microorganisms, it is generally unnecessary to supplement a special nutrient source, and occasionally it is sufficient to supplement an essential amino acid, biotin and the like.
【0013】上記多孔質毛管材は、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。The above-mentioned porous capillary material is generally lighter than water, and thus floats on the water surface when applied to target water. Therefore, if it is desired to apply the method to the water bottom or between the water surface and the water bottom, it is preferable to appropriately use a carrier heavier than water.
【0014】 適用形態 本発明において、多孔質毛管材を対象水に適用する方法
には、種々の形式がある。最も簡単な方法は、シート状
の多孔質毛管材に適当なアンカーを付して又は該材を岸
辺から繁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、シート状の多孔質毛管材自身は多
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
管状の多孔質毛管材を懸垂するのがよい。或いは、シー
ト状多孔質毛管材を溝渠の上縁からその側壁から底部お
よび対向する側壁にそ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。In the present invention, there are various types of methods for applying the porous capillary material to the target water. The simplest method is to attach an appropriate anchor to the sheet-like porous capillary material or to float the material on the water surface using a traditional rope from the shore. Although this method is simple, since the sheet-like porous capillary material itself does not have a space for supporting a large amount of microorganisms, the sheet is also used as a float and the microorganism carrier (desired) is internally contained from the material. (Including a more permanent source of microbial nutrients). Alternatively, a sheet-like porous capillary material may be straddled from the upper edge of the culvert to its upper edge along the side wall from the side wall to the bottom and the opposing side wall, or may be attached along one or both side walls, or There is also a method of laying only at the bottom.
【0015】また、別の形式として多孔質毛管材を管状
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。いずれの形式も多
孔質毛管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。In another form, a porous capillary material is formed in a tubular or bag-like form, and a carrier containing microorganisms such as vinylon cotton is placed inside the float, submerged in the water bottom, or suspended in water. There is a way to make it happen. Both types have the advantage that a large amount of BOD load can be processed because the porous capillary material can support a large amount of microorganism carriers. In particular, in the case of a tube, the purifying efficiency can be further increased by positively supplying air and nutrients for microorganisms from one end of the tube drawn into the atmosphere, if desired.
【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。As a further special method, there is a method of condensing light on the bacterial flora with a lens. This method is suitably used for photosynthetic microorganisms such as many 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。Uses 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, reservoirs, etc., whose water quality has deteriorated, and for preventing the deterioration of the water quality of fish ponds, fish cages, and aquariums for aquarium fish. .
【0018】[0018]
【作用】本発明を構成する多孔質毛管材は、それ自体大
きな表面積を有し、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。この結果、毛細管作
用により空気/水界面間のガス交換を活発にし、前記無
数の空間は、該微生物を捕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、該菌の菌勢が活発になるにつれ、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抑えられ、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が増殖する。さら
にある種の光合成細菌は、水底のヘドロから発生する硫
化水素を脱水素して硫黄へ変化させるから、これら微生
物の総合作用により水質が向上する。なお、多孔質毛管
材は、深層への酸素供給を活性化するため、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 porous capillary material constituting the present invention has a large surface area by itself, and provides a dwelling house suitable for underwater aerobic microorganisms in a myriad of spaces. As a result, the gas exchange between the air / water interface is activated by the capillary action, and the innumerable spaces protect the microorganisms from plankton and the like that prey on the microorganisms. Therefore, the microorganisms proliferate actively by the enriched oxygen. Actively decompose and mineralize organic matter in water. In addition, as the virulence of the bacterium becomes active, it spreads in all directions while forming a colony, and the contact area between the bacterium and water increases, thereby exhibiting a large purification ability. In this way, as the growth of aerobic microorganisms becomes more active, the growth of anaerobic bacteria that cause the generation of offensive odors is suppressed, and the sludge on the bottom of the water gradually decreases. In particular, blue-green algae provide oxygen to the water, so the underlying organic assimilating bacteria proliferate. Furthermore, some photosynthetic bacteria dehydrogenate hydrogen sulfide generated from sludge on the bottom of the water and convert it to sulfur. Therefore, the combined action of these microorganisms improves water quality. In order to activate the oxygen supply to the deep layer, it is preferable that the porous capillary material is distributed vertically from the water surface to the water bottom as much as possible.
【0019】以上の作用に加え、この発明で用いられる
疎水性合成繊維のマルチフィラメントからなる多孔質毛
管材は、クロマトグラフ的作用を持ち、この作用により
水中に溶存する塩類を系外に排出することが可能とな
る。すなわち、生活排水等の流入や養殖魚類等の排泄物
により、ナトリウム塩等の塩類が、河川や湖沼等の水中
に溶存状態で蓄積されるようになる。この塩類の蓄積も
河川や湖沼の汚染の原因の一つである。そして、本発明
の上記多孔質毛管材は、材質が、疎水性合成繊維のマル
チフィラメントであること、および多孔質であることの
二つの構成により、上記溶存塩類をクロマトグラフ的作
用で析出させるのである。したがって、例えば、この多
孔質毛管材の全体を水中に沈めるのではなく、その一部
を水中外に出せば、この水中外の部分から水中の塩類が
析出するようになる。また、この多孔質毛管材の全体を
水中に沈め、その表面に塩類を析出させ、ついでこれを
引き上げることにより、河川や湖沼の溶存塩類の除去が
可能となる。そして、この溶存塩類の除去により、一層
水質の向上に貢献することが可能となる。なお、微生物
として、対象水中に分布するものに代え、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
択し、これを上記多孔質毛管材に担持させれば、一層の
浄水効果を期待できる。In addition to the above functions, the porous capillary material comprising multifilaments of hydrophobic synthetic fibers used in the present invention has a chromatographic function, and discharges salts dissolved in water out of the system by this function. It becomes possible. That is, salts such as sodium salts are accumulated in a dissolved state in water such as rivers and lakes due to the inflow of domestic wastewater and the excrement of cultured fish and the like. This accumulation of salts is also one of the causes of pollution of rivers and lakes. The porous capillary material of the present invention is characterized in that the dissolved salts are precipitated by a chromatographic action due to the two configurations of the material being a multifilament hydrophobic synthetic fiber and being porous. is there. Therefore, for example, if the entire porous capillary material is not submerged in water but a part thereof is taken out of the water, salts in the water will be precipitated from the part outside the water. In addition, the entirety of the porous capillary material is submerged in water, and salts are precipitated on the surface of the porous capillary material. Then, by pulling up the salts, it is possible to remove dissolved salts from rivers and lakes. And, by removing the dissolved salts, it is possible to further contribute to the improvement of water quality. In addition, as a microorganism, instead of those distributed in the target water, a highly organic or harmful inorganic substance decomposable substance suitable for the quality of the target water is selected, and this is supported on the porous capillary material. Water purification effect can be expected.
【0020】以上要するに、本発明は、自然の炭素,窒
素およ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,窒素ガス,硫黄などへ変化す
る自浄作用を、疎水性合成繊維のマルチフィラメントか
らなる多孔質毛管材の大きな接触面積および多孔質とを
利用して促進,助成しようとするものである。さらに、
上記多孔質毛管材の毛管作用(クロマトグラフ的作用)
により、溶存塩類を積極的に除去して、水質の総合的な
向上に寄与するものである。そして、本発明の水質改善
方法では、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で経済的な方法である。In short, the present invention relates to a process for harmless carbon dioxide, nitrogen and the like, which is caused by the action of microorganisms, such as organic matter, ammonia, hydrogen sulfide and the like, which are polluting components such as river water, in the natural elemental circulation system of carbon, nitrogen and sulfur. The purpose of the present invention is to promote and promote the self-cleaning action of changing to gas, sulfur, etc. by utilizing the large contact area and the porous nature of the porous capillary material composed of multifilaments of hydrophobic synthetic fibers. further,
Capillary action (chromatographic action) of the above porous capillary material
As a result, dissolved salts are positively removed, thereby contributing to the overall improvement of water quality. Since the method for improving water quality of the present invention essentially does not require power, it is a reasonable and economical method for purifying contaminated water.
【0021】[0021]
【実施例】以下、実施例について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。また、以下、「疎水性
合成繊維のマルチフィラメントからなる多孔質毛管材」
を、単に「多孔質材」と略す。The embodiments of the present invention will be described below with reference to examples, but the examples are merely for explanation and do not mean the limitation or limitation of the inventive idea. Further, hereinafter, "porous capillary material composed of multifilaments of hydrophobic synthetic fibers"
Is simply abbreviated as “porous material”.
【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 fabric was immersed in a flooded paddy field (including abundant cyanobacteria) and attached to the narrow side surface of a 50-liter goldfish aquarium to contaminate river water ( Slightly odor)
And the condition 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, almost no odor was felt, and sludge peeled off from the stone surface. In contrast, 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。Embodiment 2 FIG. 1 shows an example in which a sheet-like woven fabric 1 as a porous material is applied to river purification. In this example, the polypropylene woven fabric 1 is braided with a polypropylene multifilament filled with a mixed carrier 5 of cotton-like polypropylene and zeolite (adsorbed in advance of Epistytis culture cells) from the bottom to the inside. A large number of cylindrical bodies 2 (see FIG. 2 for details) are suspended and anchored to the water bottom 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 embodiment, fresh air is constantly applied to the woven fabric 1.
Is supplied to the inside of the tubular body through a fiber bundle constituting the tubular body 2, so that the microflora that grows in the inside always use the abundant oxygen to actively perform the action of organic matter decomposition, nitrification, and the like. Run. Since the microorganism used, Epistis, forms flocs as it grows and clogs the weave, it is difficult to exfoliate even if the speed of the water flow 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。Embodiment 3 FIG. 3 shows an example in which the present invention is applied to purification of a drainage ditch or an irrigation waterway of a golf course or the like. In this example, the rectangular woven fabric 1 made of polypropylene is provided along the bottom and the other side wall from the side wall of the groove from one edge to the other edge of the groove T using the anchors A and A, and 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 embodiment, the aerobic microorganisms naturally settled on the woven fabric 1 are promoted by the air supplied through the weave of the woven fabric 1 to reduce the BOD in the water. Since the water flow velocity is extremely reduced on the side wall and the bottom surface, 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。Embodiment 4 FIG. 4 shows that the porous material 1 in the previous example is changed to a tubular body 2 made of a braid made of polypropylene fiber, and the inside of the tubular body is filled with a cotton-like polypropylene fiber (carrier) 5. And
Further, an example is shown in which a rubber tube 6 with fine small holes 7, 7,...
【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 embodiment serves to supply a microorganism culture solution, a liquid nutrient for microorganisms or air through the tube as required. Therefore, this example is convenient for changing the type of the priority microorganism and changing the degree of growth according to 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。Embodiment 5 FIG. 5 shows another example of a porous material. The porous material of this example is
A bag-shaped jacket made of a knitted fabric (knit) 3 made of polypropylene is filled with urethane foam 5 '.
【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 the present embodiment is floated in, for example, an aquarium fish tank, fresh air is constantly supplied from the jacket 1 'to the sponge 5' to promote the growth of the aerobic microorganisms that have settled. It is preferable 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 a special case in which the porous material has a condensing lens itself.
Spherical float 10 inside through hole 9 drilled in the center of
The circular knitted knit 4 made of polypropylene fiber protrudes so as to wrap around, and the same weight / tubular porous material as in Example 2 is suspended below.
【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 embodiment, air is constantly supplied from the tip 4a of the knit 4 protruding from the water surface to the inside of the cylindrical body 2, and the strong light beam condensed by the lens 9 is below the water surface. Therefore, the growth of photosynthetic bacteria and blue-green algae is especially excellent in cold weather. Therefore, if many of them are floated on the water surface such as a fish pond, oxygen in the water is enriched, which has a favorable effect on fish and shellfish, and at the same time suppresses water pollution.
【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 facultatively anaerobic bacterium (Pseudomonas sp.) Adsorbed on a bran on the same orange bag-like porous material (60 mm × 25 mmφ; filled with cotton-like polypropylene) as in Example 2 Each 1g is accommodated, and this is aerated or not aerated beforehand in three plastic containers (130 x 150 x 200 mm) each containing 2 l of river water of Yamato River (Kagaoka-cho, Sakai City). Five samples were stored each (However, Sample B was placed on the water surface, Sample C was settled on the bottom of the water, and was not added to Sample A). The water quality change for 9 days from January 13 to 21, 1991 was observed. PH and oxygen content (DO) of test water
Measured by change. Table 1 shows the results.
【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 apparent from Table 1, the pH and the dissolved oxygen content of the sample to which the porous material was added tended to be higher than those of the control. However, no significant difference was observed between floating the porous material on the surface of the water to be treated and submerging it on the water floor.
【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 present invention. In this example, a doughnut-shaped expanded polyurethane core material (carrier) 5 ′, which also adsorbs aerobic microorganisms, is inserted into a 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,
An artificial flower 11 for decoration is inserted into 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 an aquarium for appreciation fish, the microorganisms inside the core material gradually grow to purify the water in the aquarium, and at the same time, float on the water surface with the activity of the fish and the human eye To entertain. Incidentally, it is possible to freely expand the porous material of this example using the above-mentioned woven cloth made of polypropylene or the like as a jacket and float it as an artificial island on a golf course pond or the like. Use a large tree or a natural tree for the 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 broken 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 ′ into a tubular body 4 made of a woven fabric made of polypropylene yarn.
【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 the present example is inserted into a sewer pipe through, for example, a drainage basin, the wastewater comes into contact with irregularities on the outer surface of the porous material and becomes turbulent (Tf). Since abundant oxygen is supplied to the proliferating microorganisms, an active wastewater purification action is performed. The replacement is performed by pulling a string or a wire tied to the eyelet 12 provided 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 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 a cotton-like polypropylene fiber 5 '' carrying a pure culture of Rhizobium, Azotobacter and Nitrosomonas and a root extract of legumes between polypropylene woven fabrics 1 and 1. This 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-mentioned sheet is laid on the litter M of the cat litter TT and the sand SD is placed on the upper surface, ammonia generated from urea and the like in the invading urine is oxidized to nitrate by the action of microorganisms. Odorless state can be maintained for a long time only by removing sand to which feces adhere.
【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。As described above, the present invention utilizes the activity of microorganisms, is simple and inexpensive, can be applied to any river or drain, and can be used only for purification of rivers and drains. In addition, by providing a water quality improvement method that can help prevent water quality deterioration in fish ponds, fish cages, live fish transport tanks, and aquariums (water tanks for breeding goldfish and tropical fish) and purify urine from pet animals, Can contribute to
【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 cylindrical 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 still 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 broken side view showing an example in which the present invention is applied for purifying 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 sectional view showing an example in which the present invention is used for deodorizing a cat litter box.
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 DESCRIPTION OF SYMBOLS 1 Porous material (woven fabric made of hydrophobic synthetic fiber) 2 Porous material (tubular braid made of hydrophobic synthetic fiber) 3 Porous material (braided fabric made of hydrophobic synthetic fiber) 4 Porous material (hydrophobic synthetic fiber) 5) Microorganism carrier (synthetic cotton / zeolite mixture) 5 'Microorganism carrier (urethane foam) 5' 'Microorganism carrier (synthetic cotton) 6 Rubber tube 7 6 Small hole 8 Lens 9 8 Through hole 10 Spherical float 10 'Donut float 11 Artificial flower 12 Eyelet A Anchor P Pile SD Sand T Ditch TT Cat toilet W Water
Claims (6)
水性合成繊維のマルチフィラメントからなる多孔質毛管
材を対象水と接触させることを特徴とする水質改善方
法。1. A porous capillary comprising multifilaments of hydrophobic synthetic fibers that carry or can carry aerobic microorganisms.
A method for improving water quality, comprising bringing wood into contact with target water.
項1記載の水質改善方法。2. The method for improving water quality according to claim 1, wherein said porous capillary material is in the form of a sheet.
記載の水質改善方法。3. The porous capillary material according to claim 1, wherein said porous capillary material is cylindrical.
Water quality improvement method described .
記載の水質改善方法。4. The method according to claim 1, wherein said porous capillary material has a bag shape.
Water quality improvement method described .
む請求項1〜4のいずれか一項に記載の水質改善方法。5. The method for improving water quality according to claim 1, wherein the porous capillary material contains a carrier for microorganisms.
給する請求項1〜5のいずれか一項に記載の水質改善方
法。6. The method for improving water quality according to claim 1, wherein a nutrient source for microorganisms is supplied to the porous capillary material .
Priority Applications (1)
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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 JPH05293A (en) | 1993-01-08 |
JP2599834B2 true JP2599834B2 (en) | 1997-04-16 |
Family
ID=12647959
Family Applications (1)
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JP4286691A Expired - Fee Related JP2599834B2 (en) | 1991-02-14 | 1991-02-14 | Water quality improvement method |
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JP (1) | JP2599834B2 (en) |
Families Citing this family (12)
Publication number | Priority date | Publication date | Assignee | Title |
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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 |
JP5324201B2 (en) * | 2008-12-10 | 2013-10-23 | 拓朗 藤田 | Nitric acid removal bioreactor, nitric acid removal biofilm generation method and nitric acid removal method |
JP5227486B2 (en) * | 2009-04-27 | 2013-07-03 | 大和ハウス工業株式会社 | Method for remediation of soil contaminated with hydrocarbons |
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 |
JP5947332B2 (en) * | 2014-05-01 | 2016-07-06 | 角川建設株式会社 | Sewage purification apparatus and sewage purification method |
JP2016112506A (en) * | 2014-12-15 | 2016-06-23 | 大谷 洋 | Purification system and purification method using the same, algae growth inhibition method, water flow generation device, and purification device |
JP7166608B2 (en) * | 2018-09-26 | 2022-11-08 | 信濃建設株式会社 | Aquarium fish water purification agent |
JP7276850B2 (en) * | 2019-10-23 | 2023-05-18 | トリゼンオーシャンズ株式会社 | Sediment environment 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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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 |
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JPH0283006U (en) * | 1988-12-16 | 1990-06-27 |
-
1991
- 1991-02-14 JP JP4286691A patent/JP2599834B2/en not_active Expired - Fee Related
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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 |
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