JPH06254545A - Purification of reservoir water of golf course and fish farm - Google Patents

Purification of reservoir water of golf course and fish farm

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Publication number
JPH06254545A
JPH06254545A JP3264269A JP26426991A JPH06254545A JP H06254545 A JPH06254545 A JP H06254545A JP 3264269 A JP3264269 A JP 3264269A JP 26426991 A JP26426991 A JP 26426991A JP H06254545 A JPH06254545 A JP H06254545A
Authority
JP
Japan
Prior art keywords
water
added
reservoir
bacteria
protease
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
JP3264269A
Other languages
Japanese (ja)
Inventor
Tomoji Tanaka
友爾 田中
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.)
Individual
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Individual
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Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP3264269A priority Critical patent/JPH06254545A/en
Publication of JPH06254545A publication Critical patent/JPH06254545A/en
Pending legal-status Critical Current

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  • Water Treatment By Sorption (AREA)

Abstract

PURPOSE:To sterilize water and to prevent its putrefaction by charging liquid, which is prepd. by adding prescribed decomposition bacteria to a specific surfactant and mixing protease, etc., therewith, to the water to flocculate and settle pollutants and adding a peroxide and zeolite having a radiation property, etc., thereto. CONSTITUTION:The liquid which is prepd. by using nonsteroid type saponin as the surfactant, adding chitonic acid active carbon and humic acid thereto and adding the decomposition bacteria, such as Lactobacillus, Bulgariscus, Lytobacillus and Andococillus, thereto, is first charged together with protease, lipase, etc., into a reservoir 1b, at the time of purifying the reservoir 1b. As a result, the pollutants in the reservoir are flocculated and settled. The putrefaction of the water is suppressed by converting the anaerobic water to aerobic water by the effect of a peroxide, UV lamp 3b and ozone generator 4b and charging the zeolite, silicate, magnetite, etc., having the radiation property thereto. Further, denitrification, denitration and dephosphorization are effected by planting papyrus and hotei-aoi in the reservoir.

Description

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

この発明は、ゴルフ場、養魚場の溜池の水が二次公害排
水の要因となっているのを改善する為に、先ず界面活性
剤のサポニンとフミン酸、発酵木材繊維、硅酸塩活性
灰、ゼオライト等をビフィズ菌、酵母、リパーゼ、プロ
テアーゼと共に混合して水中に添加して汚濁物を凝集沈
下せしめて、有効菌定住地を作り次ぎに四季に応じて生
ずる嫌気性菌の有害菌の増殖を押えて農薬を分解するに
必要な処理法として、過酸化物や紫外線殺菌、オゾンガ
ス殺菌を行って嫌気性水液を変換して好気性とし、これ
にラヂエーション硅酸塩や石灰岩(サンゴ化石)磁鉄鉱
石を溜池に投入して、ラヂエーションによる水の腐敗を
押え脱燐、脱硝、脱硫、脱窒作用をパピロスやホテイ草
を増殖せしめて吸着せしめる様にして溜池の水を浄化、
持続せしめる様にした水の浄化法にかかる内容である。
この発明は、ゴルフ場、養魚場の溜池の水を浄化する事
を目的としたもので、家庭排水や便所の排水や農業肥料
の他に落ち葉物等の多く存在するゴルフ場の溜池の水は
常に放流に際して、二次、三次公害汚染として問題とな
っていた。特に之れ等は冬期に水質が嫌気性菌の繁殖に
よって悪臭を放ち、水質は酸性で農業の存在は地下水の
汚染の要因となりその改善が望まれいた。特に、ゴルフ
場に隣接する養魚場は餌付けによる飼育が一般的である
為に、過剰餌が水質を汚染し活性化した水は得られず、
嫌気性菌の繁殖によって死魚を増加する結果となってい
た。そこで本願は、水中の大腸菌、腸球菌、ウエルシン
菌、バクテロイデス、ニウバクテリウム嫌気性連鎖球菌
等の有害菌を抑制するビフィズ菌のラクトバチルス、ブ
ルガリリスクス、ラクトバチルスアンドワイルスやラク
トバチルスアンドワイルスヤ乳酸菌のミクロコッカスラ
クテノス、サッカロムセスサチを入れて連鎖状球菌やウ
ィルス菌、大腸菌等の繁殖を抑制して好気性菌を適当に
増殖せしめる様にする為には、之れ等を界面活性剤や活
性灰、キトサン、フミン酸、ゼオライト等のラヂエーシ
ョン性硅酸塩、カルシウム塩、磁鉄鉱等を添加して水の
浮遊物を凝集し、又は有害菌を一部に吸着せしめて全般
的水質の汚染を制限し、ラヂエーションによって嫌気性
菌の繁殖せしめ、又、嫌気性菌等の増殖につながる栄養
源の燐酸、アミン、アミノ酸等をパピロスやホテイ草で
吸着して浮かした後排水する時は、ゴルフ場特有の地下
水の汚染を防ぎ、特に過酸化物による水質の酸や紫外線
照射、オゾンガス等の併用による水の酸化とプロテアー
ゼ、リパーゼによる水中の蛋白質の分解を行う時は、農
薬も共に分解して公害を予防し水は活性化し溜池中の魚
類の排泄物の状かを同時に行って、更に、パピロスやホ
テイ草を増殖せしめる時は更に脱硝や脱乳酸、脱硫を行
い水を活性化せしめると共に排水の二次公害性は無く、
B.O.D.5P.P.M以下となり産業の公害性は改
善され魚類の増殖は25%に達するから今後はゴルフ場
溜池の状かに役立ち、地の養水池内の浄化ばかりでなく
芝生の散水を行う時は、ビフィズ菌の添加は連作障害を
改善し、根ぐされ病を予ぐ効果があり線虫の繁殖を防
ぐ。この農薬中の除草剤としての代用として、メチル3
〜4ジイトキシ桂皮酸をベンツアルデヒド、ワニリン、
樹脂液等を添加する時は除草効果が発揮され二次公害毒
性はない。この様に、ゴルフ場の溜池や養魚池の水質浄
化を複合的方法によって行う時は、いつまでも水質浄化
が持続されるが四季に応じて嫌気性の有害菌が増殖する
のが溜池にビフィズ菌やプロアクターゼ、酵母菌、リパ
ーゼをサポニン、活性灰、フミン酸、ゼオライト、硅酸
塩を添加して水の活性化を保つ時は、地下水の汚染は殆
どない。農薬の汚染度も0.001P.P.M以下で推
移し、燐酸、アミン類、窒素塩の増大もないので青粉の
発生も生ぜず管理が容易となり、芝の根ぐされも少ない
から産業上有用な発明である。この発明の実施要領を図
面によって説明すれば次ぎの如くである。
In order to improve the fact that the water in the ponds of golf courses and fish farms is the cause of secondary pollution drainage, this invention firstly describes the surfactants saponin and humic acid, fermented wood fiber, and silicate activated ash. , Zeolite, etc. are mixed with Bifidobacteria, yeast, lipase, protease and added to water to aggregate and settle the contaminants to create an effective colonization site, and then grow harmful anaerobic bacteria according to the four seasons. As a treatment method necessary for decomposing pesticides by holding down, the anaerobic water liquid is converted to aerobic by sterilizing peroxide, ultraviolet rays, ozone gas, and then radiating silicate and limestone (coral fossil). Putting magnetite ore into the pond and purifying the water in the pond by suppressing the decay of water due to radiation, and dephosphorizing, denitrifying, desulfurizing and denitrifying the papyrus and hotei grass by allowing them to grow and adsorb.
It is the content of the purification method of water that can be sustained.
The present invention is intended to purify water in a pond of a golf course or a fish farm, and water in a pond of a golf course in which a lot of fallen leaves and the like exist in addition to domestic drainage, drainage of a toilet and agricultural fertilizer. At the time of discharge, it was a problem as secondary and tertiary pollution pollution. In particular, those who had a bad odor in the winter due to the growth of anaerobic bacteria, the water quality was acidic, and the presence of agriculture caused pollution of groundwater, and its improvement was desired. In particular, since fish farms adjacent to golf courses are generally kept by feeding, excess feed pollutes the water quality, and activated water cannot be obtained.
This resulted in the increase of dead fish due to the reproduction of anaerobic bacteria. Therefore, the present application, Escherichia coli in water, enterococci, bacillus bacillus, Bacteroides, Bifidobacterium lactobacillus that suppresses harmful bacteria such as niubacterium anaerobic streptococcus, Bulgari riskus, Lactobacillus and Weylus lactic acid bacteria Micrococcus lactenos and Saccharomyces satachi are added to suppress the growth of streptococci, viral bacteria, Escherichia coli, etc. and to appropriately grow aerobic bacteria. Radiation silicates such as activated ash, chitosan, humic acid, and zeolite, calcium salts, magnetite, etc. are added to agglomerate the suspended solids of water or to adsorb harmful bacteria to a part to contaminate the overall water quality. Phosphates, amines, and nutrients, which are nutrient sources that limit anaerobic bacteria by radiation and cause anaerobic bacteria to grow. When draining water after adsorbing non-acids etc. with papyrus or hotei grass and then draining it, it prevents pollution of groundwater peculiar to golf courses, especially oxidation of water by acid and UV irradiation of water quality due to peroxide, ozone gas etc. When the protein in water is decomposed by protease and lipase, the pesticide is also decomposed to prevent pollution, the water is activated and the excrement of fish in the pond is performed at the same time. When it is grown, it further denitrates, delacticizes, desulfurizes and activates water, and there is no secondary pollution of wastewater,
B. O. D. 5P. P. Since it becomes less than M, the pollution of the industry is improved and the fish breeding reaches 25%, it will be useful like a golf course pond in the future, and it will not only clean the inside of the water tank of the ground but also spray the lawn with Bifidobacteria. The addition of is effective in improving continuous crop failure, has the effect of predicting rooted disease, and prevents the reproduction of nematodes. As a substitute for the herbicide in this pesticide, methyl 3
~ 4 diitoxycinnamic acid, benzaldehyde, vanillin,
When adding resin solution, etc., the herbicidal effect is exhibited and there is no secondary pollution toxicity. In this way, when water purification of a golf course pond or fishpond is carried out by a complex method, the water purification continues forever, but the anaerobic harmful bacteria grow in the pond depending on the four seasons. When proactase, yeast and lipase are added with saponin, activated ash, humic acid, zeolite and silicate to keep the water activated, there is almost no groundwater pollution. The pesticide contamination level is 0.001P. P. This is an industrially useful invention because the amount of phosphoric acid, amines and nitrogen salts does not increase, the generation of blue powder does not occur, the management is easy, and the rooting of turf is small. The following is a description of the embodiment of the present invention with reference to the drawings.

【図1】に於いて発酵タンク(1)に常法に従って3〜
5%糖液を入れてビフィズ菌を入れて発酵せしめ撹拌機
(5)を回転し、30〜35%の温度で発酵せしめる。
このビフィズ菌には腸内発酵のビフィズ桿菌も使用され
るので発酵タンク(2)で撹拌機(6)で撹拌しながら
30〜35℃の温度で糖液を発酵し脱酸して窒素ガスを
タンク内に吹き込みながら増殖培養せしめる。発酵タン
ク(3)は酵母、即ち酒精酵母を糖液中に移殖して25
〜30℃で常法で発酵し、撹拌機(7)で撹拌しながら
2〜3日管発酵して発泡した炭酸ガスの加減で発酵を止
める。発酵タンク(4)はゼラチン、ブイヨン液に炭酸
ガスを吹き込みながらプロテアーゼを入れて25〜35
℃で加温しながら増殖し、4日間で発酵を終わる。この
プロテアーゼは枯草菌の培養中に副生するプロテアー
ゼ、パパイヤ酵素を利用しても差し支えない。リパーゼ
は昆虫の死体を含む天然腐食枯草繊維の滞積物より抽出
したものを添加して、各発酵タンク中の発酵液は加熱殺
菌せしめたベントナイト粉やゼオライト粉、麦飯石粉の
硅酸塩粉に吸着せしめるが、この硅酸塩は天然赤土粘土
の放射能を1とする時は、1.2〜1.5倍のラヂエー
ション性の硅酸塩を使用する。この様な硅酸粉aに前記
発酵液を加えて乾燥室で常温乾燥せしめ、これを粉砕し
て、100メッシュの石粉とする時は1gの石粉に対し
1億〜10億桿の菌体が混合される様にして各発酵石粉
bを作り使用に際しサポニン、フミン酸、活性灰等を加
えて成型して錠剤を作る。この添加物は充分な水分は脱
水乾燥して除去し、自然発酵による自然活性の減退を防
ぐ為防水性プラスチックスに包装して保存する。過酸化
物と混合するプロテアーゼ、リパーゼは石粉に吸着乾燥
せしめたものを混合して使用するが、前記発酵石粉を粉
体のままで之れ等に混合するのもよいが、米より日本酒
を作る要領で先ず麹菌を練り米飯混合して糖化し、それ
を35〜40℃近くの温度で加温して糖化液を常法に従
って作り、これに乳酸菌を乳酸と共に入れて乳酸発酵を
作った液に酒精酵母を入れて、酒精発酵液を作りこれを
瀘別した液をベントナイト液に含浸せしめて顆粒状に造
粒して無菌状態で乾燥せしめたものをビフィズ菌の溜池
の投入後、翌日にこのものを投入して溜池水中で増殖せ
しめるが、之れ等ビフィズ菌を投入する以前に過酸化
物、リパーゼ、プロテアーゼ酵素を添加すると嫌気性菌
の大腸菌、バクテルイデス、コウバクテリウム等の連鎖
状菌、腸球菌、ウエルシュ菌の蛋白質分を分解せしめた
後に、乳酸発酵して大腸菌等の腐敗性菌を押えて酵母菌
を投入して酵母菌の増殖を行う。しかる時は、水は常に
好気性にあり常に水中の不純物を栄養源として活発に分
解を行い、魚類の排泄物中の分解酵素によって繊維質を
蛋白質と共に分解し、アミノ酸を生成して之れ等が他の
菌の栄養源として作用する様になる。しかし、水中に混
入する人間の排泄物から来る燐酸やアンモニア、アミ
ン、硫化物等は次第に濃化されるばかりでなく、養魚類
がより以上に増大した養魚池では過剰の飼料や排泄物に
よって脱硝、脱燐、脱硫、脱窒を必要とするもので水中
にパピロスやホテイ草を根つけて之れ等過剰の栄養源を
吸収せしめる時は、農業用水に支障を生ずる燐酸や窒素
肥料成分や硫化物や亜硝酸類は過剰乳酸と共に吸着分離
されるので、異状な線粉の発生が抑制され透明度が70
糧〜1米に及ぶ清澄液が得られる。農薬については、有
機燐教虫液は過酸化物で分解して燐酸塩となりダイアジ
ノンの様な除草剤は過酸化物で分解し、中和され硅酸塩
やパピロスに吸収されて特にリグニン分解酵素を使用す
る時は、リグニン分解物と吸着してダイアジノンに対し
ても球菌性があり、これを分解吸着する作用がある。
又、キトサンもダイアジノンを吸着する作用がある。サ
ポニンの定住性を示すデーターとして86〜80コロニ
ーであったものが613〜585ぐらいに増大し又、
[Fig. 1] In the fermentation tank (1), 3 to
A 5% sugar solution is added and Bifidobacteria are added and fermented, and the agitator (5) is rotated to ferment at a temperature of 30 to 35%.
Bifidobacillus of intestinal fermentation is also used for this Bifidobacteria, so while fermenting the sugar solution at a temperature of 30 to 35 ° C while stirring with a stirrer (6) in the fermentation tank (2), deoxidizing and deoxidizing nitrogen gas. Propagation culture is performed while blowing into the tank. Fermentation tank (3) transfers yeast, ie sake yeast into sugar solution to
Fermentation is carried out in the usual manner at -30 ° C, and the fermentation is stopped by adjusting the amount of carbon dioxide gas foamed by tube fermentation for 2-3 days while stirring with a stirrer (7). Fermentation tank (4) contains gelatin and broth with 25 to 35 by adding protease while blowing carbon dioxide.
It grows while heating at ℃ and finishes fermentation in 4 days. This protease may utilize the protease and papaya enzyme that are by-produced during the culture of Bacillus subtilis. Lipase was added from the deposit of natural decayed hay fiber containing insect carcass, and the fermentation solution in each fermentation tank was heat-sterilized bentonite powder, zeolite powder, and silicate powder of barley stone powder. This silicate is used as a silicate having a radiation property of 1.2 to 1.5 times when the radioactivity of natural red clay is set to 1. The fermented liquor is added to the silicate powder a, dried at room temperature in a drying room, and crushed to make 100 mesh stone powder. Each fermented stone powder b is prepared so as to be mixed, and at the time of use, saponin, humic acid, activated ash, etc. are added and molded into tablets. This additive is dehydrated and dried to remove sufficient water, and stored in waterproof plastics in order to prevent the natural activity from being deteriorated by natural fermentation. Protease and lipase mixed with peroxide are used by mixing stone powder adsorbed and dried, but it is also possible to mix the fermented stone powder as it is with powder, but make sake from rice. According to the procedure, koji mold is first kneaded and mixed with saccharified rice, which is then heated at a temperature of about 35 to 40 ° C. to make a saccharified solution according to a conventional method. After adding sake yeast, making a fermented liquor and separating it, impregnating this solution into bentonite liquid, granulating it into granules, and aseptically drying it was put into the reservoir of Bifidobacterium, I put things and let them grow in the reservoir water, but if I add peroxide, lipase, protease enzyme before adding bifidobacteria etc. Enterococcus After allowed degrade protein content of Clostridium perfringens, performs yeast growth by introducing the yeast by pressing the spoilage bacteria such as Escherichia coli and lactic acid fermentation. At that time, water is always aerobic and constantly decomposes using impurities in the water as a nutrient source to decompose the fiber together with protein by degrading enzymes in fish excrement to produce amino acids. Will act as a nutrient source for other bacteria. However, not only is phosphoric acid, ammonia, amines, sulfides, etc. coming from human excrement mixed in water gradually enriched, but denitrification is also caused by excessive feed and excrement in fish ponds where fish production has increased even more. , Which requires dephosphorization, desulfurization, and denitrification, when rooting papyrus or hotei grass in water to absorb excess nutrients such as water, phosphoric acid or nitrogen fertilizer components or sulfur Since substances and nitrites are adsorbed and separated together with excess lactic acid, generation of abnormal wire powder is suppressed and the transparency is 70%.
A clarified liquid ranging from food to 1 rice is obtained. Regarding pesticides, organophosphorus fluids are decomposed with peroxides into phosphates, and herbicides such as diazinon are decomposed with peroxides, neutralized and absorbed by silicates and papyros, especially lignin-degrading enzymes. When is used, it is adsorbed with a lignin degradation product and is coccus against diazinon, and has an action of decomposing and adsorbing this.
Chitosan also has an action of adsorbing diazinon. Data showing the sedentary habitability of saponins, which had 86 to 80 colonies, increased to about 613 to 585, and

【図6】は汚泥消化反応テストの特性を示し、サポニン
添加(A)はSSの減少が増大している事が明らかで無
添加のもの(B)は低い結果となっている。
FIG. 6 shows the characteristics of the sludge digestion reaction test, and it is clear that the saponin addition (A) increases the decrease in SS, and the one without addition (B) has a low result.

【図7】は返送汚泥濃度の特性を示すもので、返送汚泥
濃度は常に変化しているがサポニンを投入したものは安
定している。
[Fig. 7] shows the characteristics of the returned sludge concentration. The returned sludge concentration is constantly changing, but the one with saponin added is stable.

【図8】は微生物の増殖曲線を示す。FIG. 8 shows a growth curve of microorganisms.

【図9】はサポニン使用のB.O.D特性(A)は源水
(B)A槽(C)はB槽(d)はC槽を示している。
FIG. 9 shows B. cerevisiae using saponin. O. D characteristic (A) shows source water (B) A tank (C) shows B tank (d) shows C tank.

【図10】はCODの特性である。サポニン添加のB
槽、C槽に於いても600P.P.M程度に減少してい
る事が認められる。特にサポニン効果を高めるには、キ
トサン水液の添加は10%もその効果を増大するので、
併用するのがよい結果を得る。この
FIG. 10 is a characteristic of COD. B with saponin added
600P in tank C and tank C P. It is confirmed that the amount has decreased to about M. In particular, in order to enhance the saponin effect, addition of chitosan water solution increases the effect by 10%, so
Good results are obtained when used together. this

【図6】〜[Fig. 6]

【図10】の添加土壌菌はバチルス、ビフィズ菌、シュ
リドモナス混合菌によるものである。これに過酸化物、
プロテアーゼ、リポーゼを添加したものは悪臭性が改善
される。これは発生大腸菌やウィルス菌や連鎖状球菌を
押える為である。しかし、ゴルフ場の様に食堂の残飯や
し尿類、風呂水等の入った排水を終始排泄する溜池では
特にこの過酸化物、プロテアーゼ、リパーゼの添加は悪
臭発生を防ぐと共に、農薬の加水分解を促進するので特
に重要である。しかし、之れ等で分解しても遊離した燐
酸や亜硝酸やアンモニア、硫酸イオンは除去は困難であ
り、之れ等はパピロスやホテイ草の植物の根付けによっ
て吸収せしめて浄化する時は、常にBODが源水で80
0P.P.Mのものでも本処理にによって、5P.P.
Mまで低下し、アンモニアイオンも0.001P.P.
M以下となり石灰石、磁鉄鉱、硅酸塩の添加によってそ
の表面に硝酸や乳酸イオンは吸着し、ラヂエーションを
常に発生しているので悪臭性の水質は無く、緑粉の発生
も生じないのでポンプによる湯気やオゾンガスの発生、
紫外線による殺菌を行えば、水質常法が容易となる。
The soil bacteria added in FIG. 10 are due to Bacillus, Bifidobacteria, and Shridomonas mixed bacteria. Peroxide,
The malodor is improved by adding protease and lipose. This is to suppress the developing Escherichia coli, virus bacteria and streptococcus. However, especially in a pond that excretes wastewater such as leftover meals, night soil, bath water, etc. in a restaurant like a golf course, the addition of peroxides, proteases, and lipases prevents the generation of foul odors and hydrolyzes pesticides. It is especially important because it promotes. However, it is difficult to remove free phosphoric acid, nitrous acid, ammonia, and sulfate ions even if they are decomposed by spores, and spores are always absorbed and purified by rooting plants of papyrus and hotei grasses. BOD is source water 80
0P. P. Even with M, 5P. P.
M, and the amount of ammonia ions is 0.001 P.M. P.
It becomes M or less, and nitric acid and lactate ions are adsorbed on the surface by the addition of limestone, magnetite, and silicate, and since radiation is always generated, there is no malodorous water quality and no generation of green powder, so steam from a pump And the generation of ozone gas,
If the sterilization by ultraviolet rays is performed, the conventional water quality method becomes easy.

【図11】は活性汚泥法による工程図を示すものであ
る。図に於いて原液600〜700/日BOD1,50
0〜2,000 P.P.Mを先ず、スクリーン(1
a)に掛けてスラヂを分離したものを第1曝気槽(2
a)1,600mの容量で曝気し第2曝気槽(3a)
に送り上澄液をとり、排水し、下部の濃縮液を沈殿槽
(4a)容量250mに入れて上澄液を排水沈殿槽
(4a)の底部の濃縮液は遠心分離器(5a)で脱水し
てスカムケーキを分離し、脱水液はNO.1の曝気槽に
ポンプ(6a)で送水して再使用する。この水質の変化
は次ぎの如くである。
FIG. 11 shows a process chart by the activated sludge method. In the figure, undiluted solution 600-700 / day BOD 1,50
0-2,000 P.I. P. M first, screen (1
The sludge separated from the first aeration tank (2)
a) The second aeration tank (3a) with aeration of 1,600 m 3
The supernatant liquid is sent to and drained, the lower concentrated liquid is put in a sedimentation tank (4a) with a capacity of 250 m 3 , and the supernatant liquid is drained and the concentrated liquid at the bottom of the sedimentation tank (4a) is separated by a centrifuge (5a). It is dehydrated to separate scum cake, and the dehydrated liquid is NO. Water is sent to the aeration tank No. 1 by the pump (6a) for reuse. This change in water quality is as follows.

【図3】はゴルフ場の溜池(1b)の中央に噴水機(2
b)を固定しその下部に紫外線ランプ(3b)を固定し
その上部にオゾン発生機(4b)を固定する。吸入り口
(5b)から入った水は(3b)を通りオゾン発生機
(4b)でオゾン化された後、噴射(6b)で噴射され
て循環する。水に添加する微生物、サポニン、活性灰、
アミン酸、キトサンは成型して又は、粉末状に加工して
溜池(1a)に均等に散布する。
[Fig. 3] shows a fountain (2) in the center of the reservoir (1b) of the golf course.
b) is fixed, the ultraviolet lamp (3b) is fixed to the lower part, and the ozone generator (4b) is fixed to the upper part. The water that has entered from the inlet (5b) passes through (3b), is ozoned by the ozone generator (4b), and then is injected by the injection (6b) and circulates. Microorganisms added to water, saponin, activated ash,
Aminic acid and chitosan are molded or processed into a powder form and evenly distributed over the reservoir (1a).

【図2】はサポニンの分子構造図である。FIG. 2 is a molecular structure diagram of saponin.

【図4】は成型微生物混合錠剤の正面図である。FIG. 4 is a front view of a molded microbial mixed tablet.

【図5】はその側面図である。この錠剤は 3糧4 原
2 3糧 重量10g〜20gである。この加工は次ぎ
の配合による10g〜20g中にビフィズ菌、バチルス
菌(酵母菌)シコドモナス菌10億桿、PH70、サポ
ニン、非ステロイド系、形成タブレット状10g〜20
g錠剤中の成分
FIG. 5 is a side view thereof. This tablet weighs 3 rations, 4 originals, 2 rations, and weighs 10 g to 20 g. This processing is based on the following formulation: Bifidobacteria, Bacillus (yeast) Sycodomonas 1 billion, PH70, saponin, nonsteroidal, formed tablets in 10 to 20 g.
Ingredients in tablets

【例1】 多糖類 60% 微生物吸着剤 10% サポニン 10% 酵素栄養源 2.5% リン酸アモン 2.5% リン酸カリ その他 2.5% ラヂエーションサンゴ化石粉(石灰石) その他磁鉄鉱粉 11.5% キトサン液 0.5%[Example 1] Polysaccharide 60% Microbial adsorbent 10% Saponin 10% Enzyme nutrient 2.5% Ammon phosphate 2.5% Potassium phosphate Other 2.5% Radiation coral fossil powder (limestone) Other magnetite powder 11.5% Chitosan solution 0.5%

【例2】 添加物粉末 過酸化物 70% 過炭酸カルシウム、過炭酸ソーダー プロテアーゼ、パパイヤ 10% リパーゼ 酵母、粉ゼオライト吸着 10% 栄養素 10% この様にこの発明の特徴は、従来化学的酸化剤や酵素を
それぞれ単独で添加処理して、浄化を行って来たが科学
的酸化剤のみにては常時し尿や残飯の混入した水の浄化
困難であり、従来の曝気による活性汚泥法処理では充分
でなかった。特にアンモニア、燐酸、亜硝酸、亜硫酸、
イオンの処理については複合的処理を行わないと解決出
来ず、夏場ではB.O.Pの原水濃度が高いので本願の
様な複合的処理によって水を浄化する事が出来、オゾン
水や紫外線殺菌では部分的効果が得られない事は分配の
定律によっても充分考えられる事であり、本願の処理に
よって始めて達成されるものでB.O.Pが5P.P.
M以下にする為にはどうしても複合的処理が必要であり
悪臭を除去する事は困難であり、産業上有用な発明であ
る。
[Example 2] Additive powder Peroxide 70% Calcium percarbonate, sodium percarbonate protease, papaya 10% lipase yeast, powder zeolite adsorption 10% Nutrients 10% Thus, the features of the present invention are Although the enzyme has been added separately to purify it, it is difficult to purify water containing urine and leftover foods only with a scientific oxidizer at all times, and conventional activated sludge method treatment by aeration is sufficient. There wasn't. Especially ammonia, phosphoric acid, nitrous acid, sulfurous acid,
Regarding the treatment of ions, it cannot be solved without complex treatment. O. Since the raw water concentration of P is high, it is possible to purify the water by the complex treatment as in the present application, and it is fully conceivable that the partial effect cannot be obtained by ozone water or ultraviolet sterilization, according to the distribution rule. This is achieved only by the processing of the present application. O. P is 5P. P.
In order to reduce the amount to M or less, it is necessary to perform a complex treatment, and it is difficult to remove a bad odor, which is an industrially useful invention.

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

【図1】 発酵処理の工程図[Figure 1] Process diagram of fermentation treatment

【図2】 ゴルフ場、養魚場の溜池の側面図[Figure 2] Side view of a pond on a golf course or fish farm

【図3】 微生物混合配剤の成型錠の正面図[Fig. 3] Front view of molded tablet of mixed microbial mixture

【図4】 その側面図[Figure 4] Side view

【図5】 顆粒粉状の(例2)配合の添加剤の包装袋の
正面図
FIG. 5 is a front view of a packaging bag of an additive compounded in a granular powder form (Example 2).

【図6】 活性汚泥浄化の特性Fig. 6 Characteristics of activated sludge purification

【図7】 返送汚泥濃度特性[Fig. 7] Return sludge concentration characteristics

【図8】 微生物増殖曲線Fig. 8 Microbial growth curve

【図9】 サポニン使用のB.O.P変化の特性FIG. 9: B. saponin used O. Characteristics of P change

【図10】 C.O.Dの特性FIG. 10 C. O. Characteristics of D

─────────────────────────────────────────────────────
─────────────────────────────────────────────────── ───

【手続補正書】[Procedure amendment]

【提出日】平成5年11月5日[Submission date] November 5, 1993

【手続補正2】[Procedure Amendment 2]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】図11[Name of item to be corrected] Figure 11

【補正方法】追加[Correction method] Added

【補正内容】[Correction content]

【図11】 活性汚泥法による工程図FIG. 11: Process diagram by activated sludge method

───────────────────────────────────────────────────── 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 9/00 R 7446−4D 503 C 7446−4D 504 A 7446−4D ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 5 Identification number Internal reference number FI Technical indication C02F 9/00 R 7446-4D 503 C 7446-4D 504 A 7446-4D

Claims (1)

【特許請求の範囲】[Claims] 後文記載の如く界面活性剤として非ステロイド系サポニ
ンを使用してキトサン活性炭、フミン酸を加えてこれに
ラクトバチルス、ブルガリリスクスやライトバチルス、
アンドコチルス、ミクロコッカス、ラクテノス、サッカ
ロムセスサチ、バチルス、アンドラクテクス等の分解菌
を添加して、これにプロテアーゼー、リパーゼ等を混合
した液を水に添加して養魚場の栄養源を更に添加して、
酸素ガス、又は過酸化物を添加して放置する時は、サポ
ニンは活性炭、フミン酸は凝集作用と各種菌の定住場所
として作用し菌体の群集化を促進して有害菌の繁殖を抑
制して水を浄性化し、これに少量のラヂエーション性の
ゼオライト、麦飯石、べントナイト浮石のカルシウム、
マグネシウム、硅酸イオン等の溶解物を添加する時は水
は腐敗する事がなく、これにパピロスの一年生植物を植
え付けて燐酸やアミン類を繁殖せしめて脱燐、脱アミン
を行う様にしてゴルフ場や養魚場の水を浄化する事を特
徴とした水の浄化法。
As described later, using non-steroidal saponin as a surfactant, added chitosan activated carbon and humic acid to it, lactobacillus, bulgariliskus and light bacillus,
Decomposing bacteria such as andcoccus, micrococcus, lactenos, saccharomyces sachi, bacillus, andractex are added, and a mixture of protease and lipase is added to the water to further add nutrients to the fish farm. do it,
When oxygen gas or peroxide is added and left to stand, saponin acts as activated carbon and humic acid acts as an aggregating and settlement site for various bacteria, promoting the colonization of bacterial cells and suppressing the growth of harmful bacteria. Water to purify water, and a small amount of radiant zeolite, barley stone, calcium bentonite fluff,
When adding a dissolved substance such as magnesium or silicate ion, the water does not decompose, and a papyrus annual plant is planted on this to grow phosphoric acid and amines for dephosphorization and deamination. Water purification method characterized by purifying water from farms and fish farms.
JP3264269A 1991-07-09 1991-07-09 Purification of reservoir water of golf course and fish farm Pending JPH06254545A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3264269A JPH06254545A (en) 1991-07-09 1991-07-09 Purification of reservoir water of golf course and fish farm

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3264269A JPH06254545A (en) 1991-07-09 1991-07-09 Purification of reservoir water of golf course and fish farm

Publications (1)

Publication Number Publication Date
JPH06254545A true JPH06254545A (en) 1994-09-13

Family

ID=17400826

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3264269A Pending JPH06254545A (en) 1991-07-09 1991-07-09 Purification of reservoir water of golf course and fish farm

Country Status (1)

Country Link
JP (1) JPH06254545A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE19542742B4 (en) * 1995-02-16 2005-09-01 Bakelite Ag Process for the immobilization of pollutants in soils, sediments or sludges
JP2009291668A (en) * 2008-06-02 2009-12-17 Hiroshima Univ Water area environment improving material and its use
CN106673299A (en) * 2016-12-06 2017-05-17 广州富生源环保工程有限公司 Sewage step-by-step dephosphorization and purification process
CN111115850A (en) * 2020-01-09 2020-05-08 河北旺鲲生物科技有限公司 Columnar sinking water-modifying agent for aquaculture and production process thereof
CN111573851A (en) * 2020-05-21 2020-08-25 郑州慧泽生化科技有限公司 Microorganism water regulating and purifying agent and preparation method thereof

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE19542742B4 (en) * 1995-02-16 2005-09-01 Bakelite Ag Process for the immobilization of pollutants in soils, sediments or sludges
JP2009291668A (en) * 2008-06-02 2009-12-17 Hiroshima Univ Water area environment improving material and its use
CN106673299A (en) * 2016-12-06 2017-05-17 广州富生源环保工程有限公司 Sewage step-by-step dephosphorization and purification process
CN111115850A (en) * 2020-01-09 2020-05-08 河北旺鲲生物科技有限公司 Columnar sinking water-modifying agent for aquaculture and production process thereof
CN111573851A (en) * 2020-05-21 2020-08-25 郑州慧泽生化科技有限公司 Microorganism water regulating and purifying agent and preparation method thereof

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