WO2001028930A1 - Water quality improving agent and method of manufacturing the same - Google Patents

Water quality improving agent and method of manufacturing the same Download PDF

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Publication number
WO2001028930A1
WO2001028930A1 PCT/JP1999/005752 JP9905752W WO0128930A1 WO 2001028930 A1 WO2001028930 A1 WO 2001028930A1 JP 9905752 W JP9905752 W JP 9905752W WO 0128930 A1 WO0128930 A1 WO 0128930A1
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Prior art keywords
water quality
water
improving agent
quality improving
enzyme
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PCT/JP1999/005752
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French (fr)
Japanese (ja)
Inventor
Seiya Nishio
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Seiya Nishio
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Application filed by Seiya Nishio filed Critical Seiya Nishio
Priority to PCT/JP1999/005752 priority Critical patent/WO2001028930A1/en
Publication of WO2001028930A1 publication Critical patent/WO2001028930A1/en

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/68Treatment of water, waste water, or sewage by addition of specified substances, e.g. trace elements, for ameliorating potable water

Definitions

  • the present invention is intended to improve various types of pollution related to sewage, odor, and other water in rivers, lakes, marshes, dams, sewers, septic tanks, recirculating flush toilets, temporary toilets, night soil treatment plants, the sea, factory drainage, etc.
  • the present invention relates to a water quality improving agent capable of decomposing sludge and a method for producing the same. Background art
  • An object of the present invention is to provide a water quality improving agent capable of easily improving water quality and decomposing organic sludge in rivers, lakes, marshes, ponds, dams, etc. without impairing the surrounding landscape, and a method for producing the same. Is to do. Disclosure of the invention
  • the water quality improving agent of the present invention The enzyme is obtained by adding the extracted enzyme and minerals extracted from minerals containing magnesium and calcium containing silicon as a main component to water and stirring at a predetermined temperature for 30 to 90 minutes.
  • Vitamin B ⁇ 10 mg
  • the enzyme used in the water quality improving agent of the present invention is not limited to the above composition, and may be prepared by mixing pineapple with orange. [1-2. Preparation of Mineral Extract]
  • 100 cc of the stock solution of the enzyme extracted from orange prepared as described above is diluted 20-fold with water, and the above mineral extract is added to the extract at 1 to 10 cc. After stirring for about 30 minutes, the mixture is further diluted 200 to 250 times with water and stirred.
  • the stirring time for producing the water quality improving agent of the present invention in 500 liters is usually 60 minutes, but depending on the conditions of the water to be improved and the cause of contamination, etc. It can be changed arbitrarily in 90 minutes.
  • the stirring time can be appropriately changed depending on the production amount of the water quality improver and the stirring capacity of the stirrer. Therefore, when the stirring capacity of the stirrer is large, a large amount of the water quality improving agent can be produced in a short time.
  • Enzymes that can be used in the water quality improver of the present invention can be obtained not only from the above-described enzymes extracted from oranges, but also from fruits such as pineapples, Pomegranate, and other plants.
  • pineapple can be used alone as in the above orange, and the extraction method is also the same.
  • orange and pineapple may be used in a one-to-one mixture.
  • Pseudomonas radiata has an effect of promoting extraction.
  • the minerals extracted from the above minerals are magnesium, It is a shim or other composite, preferably in a liquid form, but may be in a granular form.
  • these minerals generate bioelectricity and active potential in the living organisms of the aquatic organisms that make up the biological circulation chain to improve ionization, activate cells, and improve hormonal balance. It is thought that this has the effect of promoting the propagation of aquatic organisms that constitute the biological cycle.
  • the mixing ratio of the above enzymes and minerals is usually in the range of 10 to 16 minerals per enzyme in terms of mass, but the mixing ratio is optional according to the conditions of water to be improved and the cause of contamination. Can be changed. For example, if the cause of contamination is high oil content, it is effective to increase the mineral ratio, such as 30 or more minerals per enzyme. Either enzyme or mineral may be used, and minerals may not be used in ordinary rivers and ponds.
  • the drip interval and dose are determined based on the daily flow rate (for example, if the daily flow rate is 10,000 tons, the drip interval is every 1 second, and the input rate is 67 liters / Days are preferred).
  • the daily flow rate for example, if the daily flow rate is 10,000 tons, the drip interval is every 1 second, and the input rate is 67 liters / Days are preferred.
  • dams, etc. the water at the bottom is always stagnant, so it is effective to inject directly into the bottom of the dam.
  • a water quality improving agent is stored in a storage tank 1 having an anti-freezing function, a pump 2 is connected to the storage tank 1, and a pump 2 is connected via a common pipe 3 to a knee. Connected to dollar nozzle 4. Then, a required amount of the water quality improving agent is sent to the common pipe 3 by the pump 2, and the water quality improving agent is discharged from the needle nozzle 4 provided at the end of the common pipe 3.
  • the 21 dollar nozzle 4 has a flow rate
  • An adjuster is provided so that the drip interval can be adjusted as appropriate.In the drip method as described above, the needle nozzle needs to be adjusted according to the size of the river and the type of purification target such as a pond or dam.
  • the amount of water quality improver can be adjusted by increasing or decreasing the number of installations. Needless to say, the method can be combined with an intermittent method in which charging is performed at predetermined time intervals.
  • a spraying nozzle 5 is attached to the tip of the common pipe 3.
  • the spray nozzle 5 is also provided with a flow rate adjuster, so that the spray interval can be appropriately adjusted.
  • the other configuration is the same as that of the infusion method, and the description is omitted.
  • the direct injection method is applied to deep ponds.
  • the purification efficiency can be increased by submerging the common pipe to a desired depth and directly charging the water quality improving agent into the common pipe.
  • a round or straight fountain type nozzle 6 is attached to the tip of the common pipe 3.
  • the fountain-type nozzle 6 is also provided with a flow rate regulator so that the discharge interval can be adjusted appropriately.
  • the other configuration is the same as that of the infusion method, and the description is omitted.
  • the fountain method is used when the water flow is weak, such as in a pond.
  • the injection method such as drip injection, intermittent injection, spraying, direct injection, etc. is determined according to various conditions such as the type of the object to be improved. Also, multiple systems can be used together, and can be used with existing facilities.
  • FIG. 1 is a diagram showing a method of feeding a water quality improving agent according to the present invention, wherein (A) is a drip method, (B) is a spray method, (C) is a fountain method, and FIG. in example 1 of the present invention, a diagram showing a pond became experimental subject, FIG. 3, in the second embodiment of the present invention, the c invention illustrates two ponds became experimental subjects Best mode to implement
  • the test object is a 500-liter pond as shown in Fig. 2.
  • the water in Pond c where many carps are grown, is circulated by a pump.
  • the visibility of the water in the pond is so turbid that you can't see the bottom of the pond at all and you can't even see the carp swimming scenery. Therefore, in the first embodiment, the purpose of the experiment was to “improve the degree of transparency”.
  • the water quality improving agent of the present invention was instilled in an amount of 20 liters each.
  • the interval between the infusions was every 7 seconds:
  • 20 liters of the water quality improver of the present invention was directly injected from the container at point C in FIG.
  • about 10 liters were directly injected into points D and E, respectively. That is, a total of 80 liters were injected using both infusion and direct injection.
  • the experimental period was about 2 months.
  • the object of the experiment was two ponds with a circumference of about 150 m and a water depth of about 50 cm as shown in Fig. 3, both of which were about 3 ⁇ !
  • the 3 this pond you are away ⁇ 5 m is transplanted aquatic plants, have been made education.
  • the water in the two ponds is spring water that springs from the bottom of the ponds.
  • the ranch's pastures around the pond are rich in nutrients, so that amidro breed enough to cover the water surface of the pond and hinder the growth of aquatic plants. Therefore, in Example 2, the purpose of the experiment was set as “suppression of the propagation of ambero.”
  • one of the two ponds with a surrounding area of about 150 m and a water depth of about 50 cm was treated, and the other was left untreated and compared.
  • the water quality improving agent of the present invention by appropriately adding the water quality improving agent of the present invention, effects such as reduction of BOD, COD, turbidity, chromaticity, etc., improvement of odor, and decomposition of chlorine compounds, organic substances, etc. can be obtained.
  • rivers, lakes and marshes improved by the water quality improver of the present invention it is considered that this will lead to the activation of an effective self-cleaning action for preserving ecosystems.
  • the application range of the agent is very wide.
  • the water quality improving agent of the present invention is excellent in safety and large-scale because it is composed of an enzyme extracted from at least one of orange and pineapple and at least one of predetermined minerals. Since it does not require simple plant equipment, it can greatly contribute to improving the water environment.

Abstract

A water quality improving agent which is obtained by adding, in predetermined quantities, an enzyme extracted from vegetable, such as an orange, and minerals extracted from mineral containing silicon, as a main component, magnesium and calcium to water, and by agitating for 30-90 minutes the mixture. A suitable quantity of this water quality improving agent is poured in droplets or directly into desired places, such as rivers, lakes and marshes, ponds and sewage purifying tanks.

Description

明 細 書 水質改善剤及びその製造方法 技術分野  Description Water quality improving agent and its production method
本発明は、 河川、 湖沼、 ダム、 下水道、 浄化槽、 循環式水洗トイレ、 仮設トイレ、 し尿 処理場、 海、 工場排水等の汚水及び臭気、 その他の水に関する各種汚染の改善を図り、 有 機物汚泥を分解することができる水質改善剤及びその製造方法に関する。 背景技術  The present invention is intended to improve various types of pollution related to sewage, odor, and other water in rivers, lakes, marshes, dams, sewers, septic tanks, recirculating flush toilets, temporary toilets, night soil treatment plants, the sea, factory drainage, etc. The present invention relates to a water quality improving agent capable of decomposing sludge and a method for producing the same. Background art
従来、 河川等では、各種の汚染に対処するため、 紫外線等を利用した汚水処理 プラントが設置され、 また、 一般家庭や工場では、 その排水等に対処するため、 濾過や沈降分離等を利用した浄化槽が用いられている。 また、 自治体等による終 末処理場においては、 炭素やその他薬品を投与したり、 浚渫等によって汚泥等を 取り除いている。  Conventionally, rivers, etc., have been equipped with sewage treatment plants that use ultraviolet light, etc., to deal with various types of pollution, and ordinary households and factories have used filtration, sedimentation, etc. to deal with the wastewater. Septic tanks are used. In addition, at landfills by local governments, carbon and other chemicals are injected, and sludge is removed by dredging.
しかしながら、 汚水処理プラント等の設備は非常に高価であり、 処理水量が許 容量を超えればその対応も非常に難しい。 また、 薬品等を使用した場合には、 副 作用等の弊害が考えられる。 さらに、 浚渫等で取り除いた汚泥は、 別の場所に運 送されて処理されるため厳重な管理が必要であり、 また、 別途処理プラン トが必 要となる。 さらに、 現状では、 このような事業と共に、 水環境を改善するための 法的規制の強化が施されているため、 かかる規制に適合する水質改善剤の開発が 切望されている。  However, facilities such as sewage treatment plants are very expensive, and it is very difficult to deal with them if the amount of treated water exceeds the allowable capacity. When chemicals are used, adverse effects such as side effects are considered. Furthermore, the sludge removed by dredging etc. is transported to another place for treatment, so strict management is required, and a separate treatment plant is required. Furthermore, at present, along with such projects, legal regulations for improving the water environment are being strengthened, and there is an urgent need to develop water quality improvers that comply with such regulations.
本発明の目的は、 周囲の景観を損なうことなく、 河川、 湖沼、 池、 ダム等にお いて、 簡単に水質を改善でき、 有機物汚泥を分解することができる水質改善剤及 びその製造方法を提供することにある。 発明の開示  An object of the present invention is to provide a water quality improving agent capable of easily improving water quality and decomposing organic sludge in rivers, lakes, marshes, ponds, dams, etc. without impairing the surrounding landscape, and a method for producing the same. Is to do. Disclosure of the invention
本発明者は、 上記目的を達成するため、 鋭意検討を重ねた結果、 本発明を完成 するに至ったものである。 すなわち、 本発明の水質改善剤は、 オレンジ等の植物 より抽出した酵素と、 ケィ素を主成分としマグネシウム及びカルシウムを含む鉱 物より抽出したミネラルを水に添加し、 所定の温度で 3 0〜 9 0分攪拌して得ら れるものである。 The inventors of the present invention have made intensive studies to achieve the above object, and as a result, have completed the present invention. That is, the water quality improving agent of the present invention The enzyme is obtained by adding the extracted enzyme and minerals extracted from minerals containing magnesium and calcium containing silicon as a main component to water and stirring at a predetermined temperature for 30 to 90 minutes.
[ 1 . 水質改善剤の調製方法]  [1. Preparation of water quality improver]
[ 1 - 1 . 植物から抽出した酵素の調製法]  [1-1. Preparation of enzymes extracted from plants]
(組成)  (Composition)
オレンジ 4 0 0 g  Orange 400 g
ケイセィダサの葉 3 0 0 g  Keaseidasa leaves 300 g
真砂土 5 0 0 c c  Masago soil 5 0 0 c c
粘土 2 0 0 c c  Clay 2 0 0 c c
ビタ ミ ン B丄 1 0 m g  Vitamin B 丄 10 mg
ビタ ミ ン B 2 6 m g  Vitamin B 26 mg
ビタ ミ ン B 6 8 m g Vitamin B 6 8 mg
ビタ ミ ン B 12 1 2 μ g Vitamin B 12 1 2 μg
パン トテン酸カルシウム 3 0 g  Calcium pantothenate 30 g
炭酸カルシウム 2 3 0 m g  Calcium carbonate 230 mg
*真砂土と粘土は、 水分を含んでいるため計量は容積で行う。  * Since sand and clay contain moisture, measurement is performed by volume.
(調製法)  (Preparation method)
オレンジは皮付きのまま適当な大きさに切り、 上記の各成分と共に 5 リ ッ トル の容器に入れ、 全体量が 5 リ ッ トルとなるまで水を加え、 沸騰するまで加熱する。 この容器に入れたまま、 常温で約 6ヶ月間放置して熟成させる。 その後、 水を 5 リ ッ トルの目盛りまで入れ、 8 0 °C〜 1 0 0 °Cで約 9 0分加熱する。 その後放置 して常温とし、 上澄み液を採取することによって約 3 リ ツ トルの抽出液を得る。 この抽出液 1 0 c c と乾燥した真砂土 3 0 0 gを 1 0 リ ツ トルの水に混ぜ、 密 封状態で約 2〜 3週間おき、 その上澄み液を取り出す。 これがオレンジから抽出 した酵素の原液水となる。  Cut the oranges into the appropriate size with the skin on, put in a 5 liter container with the above ingredients, add water until the total volume is 5 liters, and heat to boiling. Leave it in this container and let it mature at room temperature for about 6 months. Then add water to the 5 liter scale and heat at 80 ° C to 100 ° C for about 90 minutes. Then, let it stand at room temperature and collect the supernatant to obtain about 3 liters of extract. This extract (10 cc) and 300 g of dried masago are mixed with 10 liters of water, kept in a sealed state for about 2 to 3 weeks, and the supernatant is taken out. This is the undiluted water of the enzyme extracted from orange.
なお、 本発明の水質改善剤に用いられる酵素は、 上記の組成に限定されず、 ォ レンジと共にパイナップルを混ぜて調製することもできる。 [ 1 - 2 . ミネラル抽出液の調製法] The enzyme used in the water quality improving agent of the present invention is not limited to the above composition, and may be prepared by mixing pineapple with orange. [1-2. Preparation of Mineral Extract]
(組成)  (Composition)
真砂土 1 0 0 0 g  Masago 1 0 0 0 g
角閃石 1 0 0 g  Amphibolite 100 g
クェン酸 2 5 0 g  Cunic acid 250 g
(調製法)  (Preparation method)
上記の各成分を水 1 0 リ ッ トルに溶き、 沸点近傍で約 9 0分加熱する。 その後 放置して常温とし、 上澄み液を取り出す。 これがミネラル抽出液となる- [ 1 一 3 . 水質改善剤の調製]  Dissolve each of the above components in 10 liters of water and heat for about 90 minutes near the boiling point. Then leave it at room temperature and remove the supernatant. This is the mineral extract-[13. Preparation of water quality improver]
上記のようにして調製したオレンジから抽出した酵素の原液水 1 0 0 c c を水 で 2 0倍に希釈し、 これに上記ミネラル抽出液を 1〜 1 0 c c力 [)える。 約 3 0分 攪拌した後、 さらに水で 2 0 0倍〜 2 5 0倍に希釈し、 攪袢する。  100 cc of the stock solution of the enzyme extracted from orange prepared as described above is diluted 20-fold with water, and the above mineral extract is added to the extract at 1 to 10 cc. After stirring for about 30 minutes, the mixture is further diluted 200 to 250 times with water and stirred.
なお、 本発明の水質改善剤を 5 0 0 リ ツ トル製造するための攪拌時間は、 通常 6 0分であるが、 改善対象となる水の条件と汚染原因等に応じて、 3 0分〜 9 0 分に任意に変更することが可能である。 また、 水質改善剤の製造量及び攪拌機の 攪拌容量により攪拌時間は適宜変更することができる。 したがって、 攪拌機の攪 拌容量が大きい場合には、 短時間に大量の水質改善剤を製造することができる。 [ 2 . 酵素について]  The stirring time for producing the water quality improving agent of the present invention in 500 liters is usually 60 minutes, but depending on the conditions of the water to be improved and the cause of contamination, etc. It can be changed arbitrarily in 90 minutes. The stirring time can be appropriately changed depending on the production amount of the water quality improver and the stirring capacity of the stirrer. Therefore, when the stirring capacity of the stirrer is large, a large amount of the water quality improving agent can be produced in a short time. [2. Enzymes]
本発明の水質改善剤に用いることができる酵素は、 上記のオレンジから抽出し た酵素だけでなく、 パイナップル等の果実、 ドクダミソゥ、 その他の植物より抽 出して得ることができる。 この場合、 パイナップルは、 上記オレンジと同様に単 独で用いることができ、 抽出方法も同様である。 また、 オレンジとパイナップル を 1対 1に混合して用いても良い。 なお、 ドクダミ ソゥは抽出を促進する効果が あると考えられる。  Enzymes that can be used in the water quality improver of the present invention can be obtained not only from the above-described enzymes extracted from oranges, but also from fruits such as pineapples, Pomegranate, and other plants. In this case, pineapple can be used alone as in the above orange, and the extraction method is also the same. Alternatively, orange and pineapple may be used in a one-to-one mixture. In addition, it is considered that Pseudomonas radiata has an effect of promoting extraction.
[ 3 . ミネラルについて] [3. Minerals]
上記鉱物より抽出したミネラルは、 ケィ素を主成分としたマグネシウム、 カル シゥムその他の複合物であって、 液状であることが望ましいが、 粒状でも良い。 なお、 これらのミネラルは、 生物循環連鎖を構成する水中生物の生体内に生物 電気や活性電位を生じさせてイオン化の働きを良く し、 細胞を活性化させると共 にホルモンバランスを良く し、 これによつて生物循環連鎖を構成する水中生物の 繁殖を促進する効果があると考えられる。 The minerals extracted from the above minerals are magnesium, It is a shim or other composite, preferably in a liquid form, but may be in a granular form. In addition, these minerals generate bioelectricity and active potential in the living organisms of the aquatic organisms that make up the biological circulation chain to improve ionization, activate cells, and improve hormonal balance. It is thought that this has the effect of promoting the propagation of aquatic organisms that constitute the biological cycle.
[ 4 . 酵素と ミネラルの配合割合について] [4. Enzyme and Mineral Mixing Ratio]
上記の酵素と ミネラルの配合割合は、 質量にして、 酵素 1 に対してミネラル 1 0〜 1 6を通常とするが、 改善対象となる水の条件と汚染原因等に応じて、 配合 割合を任意に変更し対応することができる。 例えば、 汚染原因が油分が多い場合 は、 酵素 1に対してミネラルを 3 0以上というように、 ミネラルの割合を多くす ると効果的である。 また、 酵素と ミネラルのいずれか一方のみを用いても良く、 通常の河や池ではミネラルを用いなくても良い。  The mixing ratio of the above enzymes and minerals is usually in the range of 10 to 16 minerals per enzyme in terms of mass, but the mixing ratio is optional according to the conditions of water to be improved and the cause of contamination. Can be changed. For example, if the cause of contamination is high oil content, it is effective to increase the mineral ratio, such as 30 or more minerals per enzyme. Either enzyme or mineral may be used, and minerals may not be used in ordinary rivers and ponds.
[ 5 . 適用方法] [5. Application method]
例えば、 河川等では上流から下流に水が流れているため、 水が停滞することは ほとんどない。 このように流れのある状況の中で水質の改善処理をしなければな らない場合には、 点滴による投入が望ましい。 また、 河川等では、 一日の流量に より点滴間隔と投入量を決定する (例えば、 一日の流量が 1万トンの場合、 点滴 間隔は 1秒おき、 投入量は 6 7 リ ツ トル/日が望ましい) 。 一方、 ダム等では、 底の水が常に停滞している場合が多いため、 ダム底に直接注入すると効果的であ る。  For example, in rivers, etc., water flows from upstream to downstream, so there is almost no stagnant water. If the water quality needs to be improved in such a flowing situation, it is desirable to use drip injection. Also, in rivers, etc., the drip interval and dose are determined based on the daily flow rate (for example, if the daily flow rate is 10,000 tons, the drip interval is every 1 second, and the input rate is 67 liters / Days are preferred). On the other hand, in the case of dams, etc., the water at the bottom is always stagnant, so it is effective to inject directly into the bottom of the dam.
ここで、 本発明の水質改善剤の投入方式について、 図面を参照して説明する。 ( a ) 点滴方式  Here, the method of introducing the water quality improving agent of the present invention will be described with reference to the drawings. (a) Infusion method
第 1図 (A ) に示したように、 凍結防止機能を備えた貯蔵タンク 1に水質改善 剤が貯留され、 この貯蔵タンク 1にポンプ 2が接続され、 ポンプ 2は共通管 3を 介してニー ドルノズル 4に接続されている。 そして、 ポンプ 2によって、 共通管 3に水質改善剤を必要量送り、 共通管 3の先端に設けられたニードルノズル 4よ り水質改善剤が吐出するようになっている。 なお、 二一ドルノズル 4には、 流量 調整器が設けられており、 点滴間隔を適宜調整することが可能な構成となってい 上述したような点滴方式では、 川幅の大小、 池やダム等の浄化対象物の種類に よって、 ニー ドルノズルの設置数を増減させることによって、 水質改善剤の投入 量を調節することができる。 また、 所定の時間間隔をおいて投入する間欠方式と 組み合わせることができることは言うまでもない。 As shown in Fig. 1 (A), a water quality improving agent is stored in a storage tank 1 having an anti-freezing function, a pump 2 is connected to the storage tank 1, and a pump 2 is connected via a common pipe 3 to a knee. Connected to dollar nozzle 4. Then, a required amount of the water quality improving agent is sent to the common pipe 3 by the pump 2, and the water quality improving agent is discharged from the needle nozzle 4 provided at the end of the common pipe 3. The 21 dollar nozzle 4 has a flow rate An adjuster is provided so that the drip interval can be adjusted as appropriate.In the drip method as described above, the needle nozzle needs to be adjusted according to the size of the river and the type of purification target such as a pond or dam. The amount of water quality improver can be adjusted by increasing or decreasing the number of installations. Needless to say, the method can be combined with an intermittent method in which charging is performed at predetermined time intervals.
( b ) 噴霧方式  (b) Spray method
第 1図 (B ) に示したように、 噴霧方式においては、 共通管 3の先端に噴霧式 ノズル 5が取り付けられている。 なお、 噴霧式ノズル 5にも流量調整器が設けら れており、 噴霧間隔を適宜調整することが可能な構成となっている。 その他の構 成は点滴方式と同様であるので説明は省略する。  As shown in FIG. 1 (B), in the spraying method, a spraying nozzle 5 is attached to the tip of the common pipe 3. Note that the spray nozzle 5 is also provided with a flow rate adjuster, so that the spray interval can be appropriately adjusted. The other configuration is the same as that of the infusion method, and the description is omitted.
( c ) 直接投入方式  (c) Direct injection method
直接投入方式は、 深さのある池等に適用される。 すなわち、 直接投入方式にお いては、 共通管を所望の深さまで沈め、 その共通管内に水質改善剤を直接投入す ることにより、 浄化効率を上げることができるように構成されている。  The direct injection method is applied to deep ponds. In other words, in the direct injection method, the purification efficiency can be increased by submerging the common pipe to a desired depth and directly charging the water quality improving agent into the common pipe.
( d ) 噴水方式  (d) Fountain method
第 1図 (C ) に示したように、 噴水方式においては、 共通管 3の先端に、 丸形 あるいは直線型の噴水式ノズル 6が取り付けられている。 なお、 噴水式ノズル 6 にも流量調整器が設けられており、 喷出間隔を適宜調整することが可能な構成と なっている。 その他の構成は点滴方式と同様であるので説明は省略する。  As shown in FIG. 1 (C), in the fountain method, a round or straight fountain type nozzle 6 is attached to the tip of the common pipe 3. The fountain-type nozzle 6 is also provided with a flow rate regulator so that the discharge interval can be adjusted appropriately. The other configuration is the same as that of the infusion method, and the description is omitted.
なお、 噴水方式は、 池などで水流が弱い場合に用いられる。  The fountain method is used when the water flow is weak, such as in a pond.
このよ うに、 改善対象の種頹等、 さまざまな条件に応じて、 点滴投入、 間欠投 入、 噴霧散布、 直接注入等の投入方式を決定する。 また、 複数方式を併用するこ ともでき、 既存の設備と併用することもできる。  In this way, the injection method such as drip injection, intermittent injection, spraying, direct injection, etc. is determined according to various conditions such as the type of the object to be improved. Also, multiple systems can be used together, and can be used with existing facilities.
[ 6 . 作用 ·効果] [6. Action / Effect]
本発明の水質改善剤を適宜投入することによって、 B O D、 C O D , 濁度、 色 度等の降下、 臭気の改善、 及び塩素化合物、 有機物等の分解等の効果が得られた。 この作用は、 能動的な作用であって、 本発明の水質改善剤によって改善された河 川、 湖沼等では、 生態系を保全するために有効な自浄作用の活性化に結びつく と 考えられる。 図面の簡単な説明 By appropriately adding the water quality improving agent of the present invention, effects such as a decrease in BOD, COD, turbidity, and chromaticity, an improvement in odor, and a decomposition of chlorine compounds and organic substances were obtained. This action is an active action, and the river improved by the water quality improving agent of the present invention. In rivers, lakes and marshes, it is thought that this will lead to the activation of self-cleaning, which is effective for preserving ecosystems. BRIEF DESCRIPTION OF THE FIGURES
第 1図は、 本発明に係る水質改善剤の投入方式を示す図であって、 (A ) は点 滴方式、 (B ) は噴霧方式、 (C ) は噴水方式であり、 第 2図は、 本発明の実施 例 1において、 実験対象となった池を示す図であり、 第 3図は、 本発明の実施例 2において、 実験対象となった 2つの池を示す図である c 発明を実施するための最良の形態 FIG. 1 is a diagram showing a method of feeding a water quality improving agent according to the present invention, wherein (A) is a drip method, (B) is a spray method, (C) is a fountain method, and FIG. in example 1 of the present invention, a diagram showing a pond became experimental subject, FIG. 3, in the second embodiment of the present invention, the c invention illustrates two ponds became experimental subjects Best mode to implement
以下、 実施例に基づいて本発明をさらに詳細に説明する。  Hereinafter, the present invention will be described in more detail with reference to examples.
【実施例 1】  [Example 1]
[実験方法]  [experimental method]
実験対象は、 第 2図に示したような 5 0 0 ΐの池で、 鯉が多数育成されている c 池の水はポンプによる循環水である。 池の水の透視度は、 池底がまったく見えな いばかり力 、 鯉の泳景等も見えないほど濁っている。 そこで、 実施例 1 において は、 実験の目的を 「透視度の向上」 とした。 The test object is a 500-liter pond as shown in Fig. 2. The water in Pond c , where many carps are grown, is circulated by a pump. The visibility of the water in the pond is so turbid that you can't see the bottom of the pond at all and you can't even see the carp swimming scenery. Therefore, in the first embodiment, the purpose of the experiment was to “improve the degree of transparency”.
実験方法としては、 第 2図の Α点及び Β点において、 本発明の水質改善剤をそ れぞれ 2 0 リ ッ トルずつ点滴投入した。 なお、 点滴投入の間隔は 7秒おきである: また、 実験開始直後に、 第 2図の C点に、 本発明の水質改善剤を 2 0 リ ッ トル、 容器から直接投入し、 その 1 ヶ月後に、 D点及び E点にそれぞれ約 1 0 リ ッ トル ずつ直接投入した。 すなわち、 点滴投入及び直接投入を併用して、 合計 8 0 リ ッ トル投入した。 なお、 実験期間は約 2ヶ月であった。  As an experimental method, at points 改善 and の in FIG. 2, the water quality improving agent of the present invention was instilled in an amount of 20 liters each. The interval between the infusions was every 7 seconds: Immediately after the start of the experiment, 20 liters of the water quality improver of the present invention was directly injected from the container at point C in FIG. Later, about 10 liters were directly injected into points D and E, respectively. That is, a total of 80 liters were injected using both infusion and direct injection. The experimental period was about 2 months.
[実験結果]  [Experimental result]
実験開始後、 約 1 ヶ月で、 透視度の向上が確認された。 また、 実験開始後、 約 2ヶ月で、 池底まではっきり見えるほど、 透視度は向上し、 鯉等の生物に異常も なかつた。  About one month after the start of the experiment, it was confirmed that the degree of transparency had improved. About two months after the start of the experiment, the degree of transparency improved as the pond bottom was clearly visible, and there were no abnormalities in living things such as carps.
【実施例 2】 [実験方法] [Example 2] [experimental method]
実験対象は、 第 3図に示したような周囲約 1 5 0 m、 水深約 5 0 c mの 2つの 池であり、 両者は約 3 π!〜 5 m離れている 3 この池には水生植物が移植され、 育 成されている。 また、 2つの池の水は池底よ り湧き出ている湧き水である。 池の 周辺に牧場の牧草地があり、 栄養に富んでいるため、 池の水面を覆う程のァォミ ドロが繁殖し、 水生植物育成の妨げとなっている。 そこで、 実施例 2においては, 実験の目的を 「ァォミ ドロの繁殖抑制」 とした。 The object of the experiment was two ponds with a circumference of about 150 m and a water depth of about 50 cm as shown in Fig. 3, both of which were about 3π! The 3 this pond you are away ~ 5 m is transplanted aquatic plants, have been made education. The water in the two ponds is spring water that springs from the bottom of the ponds. The ranch's pastures around the pond are rich in nutrients, so that amidro breed enough to cover the water surface of the pond and hinder the growth of aquatic plants. Therefore, in Example 2, the purpose of the experiment was set as “suppression of the propagation of ambero.”
実験方法としては、 周囲約 1 5 0 m、 水深約 5 0 c mの 2つの池の一方を処理 し、 他方は未処理として、 対比観察した。  As an experimental method, one of the two ponds with a surrounding area of about 150 m and a water depth of about 50 cm was treated, and the other was left untreated and compared.
まず、 実験開始直後に、 処理対象とした池の周囲を図中矢印方向に歩きながら、 本発明の水質改善剤 4 0 リ ッ トルを池の水面に散布し、 1週間後に、 さらに 4 0 リ ッ トル同様の方法で散布し、 合計 8 0 リ ッ トル投入した。 なお、 実験期間は約 1 ヶ月である。  First, immediately after the start of the experiment, 40 liters of the water quality improver of the present invention were sprayed on the surface of the pond while walking around the pond to be treated in the direction of the arrow in the figure, and a week later, an additional 40 liters were applied. They were sprayed in the same manner as in the case of a little, and a total of 80 liters were introduced. The experiment period is about one month.
[実験結果]  [Experimental result]
実験開始後、 約 4 日〜 5 日 目で、 未処理の池ではァォミ ドロが繁殖し、 処理し た池ではァォミ ドロの繁殖が抑制されていることが確認された。 実験開始後 1 0 日目に、 2つの池から各々水を採取し、 計量したところ、 未処理の池の水の p H 7 . 8、 濁度 3 . 8に対し、 処理した池の水の ρ Η 7 . 1、 濁度 1 . 6 と改善し ていた。 また、 水生植物の育成も順調であった。  Approximately 4 to 5 days after the start of the experiment, it was confirmed that aomidro breeding in untreated ponds and that vegetation was suppressed in the treated ponds. On day 10 after the start of the experiment, water was collected from each of the two ponds and weighed. The pH of the untreated ponds was 7.8 and the turbidity was 3.8. ρ Η 7.1 and turbidity 1.6 were improved. The growth of aquatic plants was also successful.
【実施例 3】 [Embodiment 3]
[実験方法]  [experimental method]
2つの循環式水洗トイ レの第 1槽から、 本発明の水質改善剤を一日当たり 0 . 6 7 リ ッ トル、 点滴投入したところ、 第 1表に示すように、 河川放流基準を大幅 にクリア一した結果が得られた。 また、 透明度が向上し、 汚泥の分解も認められ、 循環式水洗トイ レの洗浄水として再利用することができることが判明した。 第 1表 0.67 liters of the water-improving agent of the present invention was instilled per day from the first tank of two circulating water-washing toilets, and as shown in Table 1, it greatly cleared the river discharge standards. A consistent result was obtained. In addition, the transparency was improved, and the decomposition of sludge was also observed, indicating that the water could be reused as washing water for the recirculating flush toilet. Table 1
Figure imgf000009_0001
Figure imgf000009_0001
産業上の利用可能性 Industrial applicability
以上説明したように、 本発明の水質改善剤を適宜投入することによって、 B O D、 C O D、 濁度、 色度等の降下、 臭気の改善、 及び塩素化合物、 有機物等の分 解等の効果が得られることが明らかとなり、 また、 本発明の水質改善剤によって 改善された河川、 湖沼等では、 生態系を保全するために有効な自浄作用の活性化 に結びつく と考えられるため、 本発明の水質改善剤の適用範囲は非常に広い。 さらに、 本発明の水質改善剤は、 オレンジ又はパイナップルの少なく ともいず れか一方より抽出した酵素と、 所定のミネラルの少なく ともいずれか一方より構 成されているので、 安全性に優れ、 大規模なプラント設備を必要としないので、 水環境の向上に大きく貢献することができる。  As described above, by appropriately adding the water quality improving agent of the present invention, effects such as reduction of BOD, COD, turbidity, chromaticity, etc., improvement of odor, and decomposition of chlorine compounds, organic substances, etc. can be obtained. In rivers, lakes and marshes improved by the water quality improver of the present invention, it is considered that this will lead to the activation of an effective self-cleaning action for preserving ecosystems. The application range of the agent is very wide. Furthermore, the water quality improving agent of the present invention is excellent in safety and large-scale because it is composed of an enzyme extracted from at least one of orange and pineapple and at least one of predetermined minerals. Since it does not require simple plant equipment, it can greatly contribute to improving the water environment.

Claims

請 求 の 範 囲 The scope of the claims
1 . 所定の酵素と、 所定のミネラルの少なく ともいずれか一方を水に溶解し、 3 0〜 9 0分攪拌して得られる水質改善剤。 1. A water quality improver obtained by dissolving at least one of a predetermined enzyme and a predetermined mineral in water and stirring for 30 to 90 minutes.
2 . 前記酵素が、 オレンジ又はパイナップルの少なく ともいずれか一方より抽 出したものであることを特徴とする請求の範囲第 1項に記載の水質改善剤。  2. The water quality improver according to claim 1, wherein the enzyme is extracted from at least one of orange and pineapple.
3 . 前記ミネラルが、 鉱物より抽出したものであることを特徴とする請求の範 囲第 1項又は第 2項に記載の水質改善剤。  3. The water quality improving agent according to claim 1 or 2, wherein the mineral is extracted from a mineral.
4 . 前記ミネラルが、 少なく ともケィ素、 マグネシウム及びカルシウムを含む ことを特徴とする請求の範囲第 1項乃至第 3項のいずれか一に記載の水質改善剤 c 4. The water quality improving agent c according to any one of claims 1 to 3, wherein the mineral contains at least silicon, magnesium, and calcium.
5 . 所定の酵素と所定のミネラルを、 前記酵素 1 に対してミネラル 1 0〜 1 6 の割合で水に溶解し、 3 0〜 9 0分攪拌することを特徴とする水質改善剤の製造 方法。 5. A method for producing a water quality improving agent, comprising dissolving a predetermined enzyme and a predetermined mineral in water at a ratio of 10 to 16 minerals to 1 enzyme and stirring for 30 to 90 minutes. .
6 . 前記酵素が、 オレンジ又はパイナップルの少なく ともいずれか一方より抽 出したものであることを特徴とする請求の範囲第 5項に記載の水質改善剤の製造 方法。  6. The method for producing a water quality improving agent according to claim 5, wherein the enzyme is extracted from at least one of orange and pineapple.
PCT/JP1999/005752 1999-10-19 1999-10-19 Water quality improving agent and method of manufacturing the same WO2001028930A1 (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009226280A (en) * 2008-03-21 2009-10-08 Tadayoshi Yoshida Method for purificating circulating water and circulation system

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Publication number Priority date Publication date Assignee Title
JPH07275841A (en) * 1994-04-13 1995-10-24 Green Karuchiyaa:Kk Method for improving quality of bottom and water contacting the bottom
JPH0819774A (en) * 1994-07-06 1996-01-23 Ube Chem Ind Co Ltd Magnesia type modifier of water quality and bottom material
JPH10118663A (en) * 1996-10-18 1998-05-12 New Bio Sangyo Kk Treatment of stockbreeding waste water
JPH10165825A (en) * 1996-10-11 1998-06-23 Komatsu Tatsutoshi Cleaning agent for contaminated waste water
JPH10235338A (en) * 1997-02-25 1998-09-08 Kuretsusendo Corp:Kk Water purifying material of rivers and lakes and marshes by liquid composite enzyme

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07275841A (en) * 1994-04-13 1995-10-24 Green Karuchiyaa:Kk Method for improving quality of bottom and water contacting the bottom
JPH0819774A (en) * 1994-07-06 1996-01-23 Ube Chem Ind Co Ltd Magnesia type modifier of water quality and bottom material
JPH10165825A (en) * 1996-10-11 1998-06-23 Komatsu Tatsutoshi Cleaning agent for contaminated waste water
JPH10118663A (en) * 1996-10-18 1998-05-12 New Bio Sangyo Kk Treatment of stockbreeding waste water
JPH10235338A (en) * 1997-02-25 1998-09-08 Kuretsusendo Corp:Kk Water purifying material of rivers and lakes and marshes by liquid composite enzyme

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009226280A (en) * 2008-03-21 2009-10-08 Tadayoshi Yoshida Method for purificating circulating water and circulation system

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