JP2007326090A - Water purifying and activating method in closed water area putting natural material to practical use and construction method therefor - Google Patents

Water purifying and activating method in closed water area putting natural material to practical use and construction method therefor Download PDF

Info

Publication number
JP2007326090A
JP2007326090A JP2006184925A JP2006184925A JP2007326090A JP 2007326090 A JP2007326090 A JP 2007326090A JP 2006184925 A JP2006184925 A JP 2006184925A JP 2006184925 A JP2006184925 A JP 2006184925A JP 2007326090 A JP2007326090 A JP 2007326090A
Authority
JP
Japan
Prior art keywords
water
decomposition
zeolite
sludge
wood vinegar
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
JP2006184925A
Other languages
Japanese (ja)
Inventor
Yoshihiro Sawada
吉宏 澤田
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
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP2006184925A priority Critical patent/JP2007326090A/en
Publication of JP2007326090A publication Critical patent/JP2007326090A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Treatment Of Biological Wastes In General (AREA)
  • Treatment Of Sludge (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a water purifying and activating method for purifying and improving the water quality caused by phenomenon that the abnormality of pH occurs in a closed water area with an excess of unstable nitrogen component, increase in the amount of phosphorus, non-transparency of water by eutrophication, and the growth of a malodor sludge, and to provide a construction method therefor. <P>SOLUTION: A water activating material is constituted so that the pH adjustment, deodorization or sterilization of water is performed by wood vinegar, flocculation and sedimentation is performed using diatomaceous soil, the aeration, ion exchange and membrane treatment of sludge is performed by zeolite and water or soil is purified only using a natural material. The water activating material is composed of wood vinegar, zeolite, vegetable broken pieces and microorganisms. The water activating material is scattered over the closed water area to perform pH adjustment, flocculation and sedimentation, aeration, ion exchange, chlorine removal, oxidative catalytic reaction, the decomposition of a malodorous substance by oxidative reaction, the decomposition of putrefaction odor of protein, excrement of an animal, etc., adsorptive decomposition of nitrogen, phosphoric acid, etc. the adsorption of a harmful substance such as outflow oil or the like, the adsorption and decomposition of residual agricultural chemicals or heavy metals and the development of microbial action due to the repairing of a living environment of effective microorganisms due to antibacterial action and pH adjustment. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、天然資材を使用し閉鎖的水域の水質の低下に係る富栄養化、汚泥化等の環境修復、水質の浄化、改善方法とその工法に関するものである。  The present invention relates to an environmental restoration such as eutrophication and sludge reduction related to the deterioration of water quality in a closed water area using natural materials, a method for purifying and improving water quality, and a method for the same.

湖、沼、池、堀、貯水池、湾内等の閉鎖的水域において水質汚染が環境問題となっている。
生活排水(し尿等の窒素分、お風呂の水、食べ物のカス、洗剤等)、農業排水(肥料等)、産業排水(化学物質)、周辺環境(車からのオイル漏れ)が流れ込む事により水質の悪化が進んでいる。景観、臭気、魚類、植物の生息に問題が起きている。また、水質汚水及び重金属の水質浄化が河川に放出され自然汚染や二次製品による環境破壊、水質汚染、悪臭に問題があった。
Water pollution is an environmental problem in closed water areas such as lakes, swamps, ponds, moats, reservoirs, and bays.
Water quality due to the flow of domestic wastewater (nitrogen such as human waste, bath water, food waste, detergent, etc.), agricultural wastewater (fertilizer, etc.), industrial wastewater (chemical substances), and the surrounding environment (oil leakage from the car) Deterioration is progressing. There are problems with the landscape, odor, fish and plant habitat. Moreover, water sewage and water purification of heavy metals were released into rivers, causing problems with natural pollution, environmental destruction due to secondary products, water pollution, and foul odors.

近年、下水道が都市部以外にも広まっており、流入の観点からは救いが見通せるものの、現状では水域周辺への導入は数年から十数年先になる。  In recent years, sewerage has become widespread in areas other than urban areas, and although salvation can be expected from the viewpoint of inflow, the introduction to the water area is currently several to ten years ahead.

閉鎖的水域は、他の水域(河川、海)に比べ大幅に環境基準の基準達成を実現できていない。  Closed water areas have not achieved environmental standards significantly compared to other water areas (rivers, seas).

対策として設備、機材が投入されているものの、ヘドロの除去を繰り返されており十分な酸素溶存の処理水対策にいたっていない。
水質浄化については、数多くの提案がなされ実用化されているものの、設備投資額と多大なる費用と人力を必要としたが、生態系に汚染を引き起こしていた。
Although equipment and equipment have been introduced as countermeasures, sludge removal has been repeated and measures for treated water with sufficient oxygen dissolution have not been achieved.
As for water purification, many proposals have been made and put to practical use, but it required capital investment, great expense and human power, but it caused pollution to the ecosystem.

浄化剤の製造にコストがかかり、かつ化学物質が添加されている。  The production of the cleaning agent is costly and chemical substances are added.

浚渫工事による生態系破壊。  Ecosystem destruction by dredging work.

現状行われている被膜処理は、30cmから100cmと貯水量に負担をかけている。  The coating treatment currently being performed places a burden on the amount of water stored, from 30 cm to 100 cm.

閉鎖水域の汚染メカニズムは、流入汚染による富栄養化、植物性微生物の増殖、動物性微生物の増殖、水中溶存酸素の消費、死滅した動物性微生物の沈降、枯死した植物性微生物の浮遊、底部におけるバクテリア分解、底部溶存酸素の消費、底部の汚泥化、リン酸、窒素の溶出、水域全体の富栄養化、と進行し悪循環をおこしている。  Contamination mechanisms in closed water are: eutrophication due to inflow pollution, growth of plant microorganisms, growth of animal microorganisms, consumption of dissolved oxygen in water, sedimentation of dead animal microorganisms, floating of dead plant microorganisms, at the bottom A vicious cycle occurs with bacterial decomposition, consumption of dissolved oxygen at the bottom, sludge formation at the bottom, elution of phosphoric acid and nitrogen, and eutrophication of the entire water area.

酸化反応により、窒素分からアンモニウムイオン、アンモニウムイオンから亜硝酸イオン、亜硝酸イオンから硝酸イオンへ移行し、その反対が還元反応でおこる。その際、富栄養化の不安定な状況では、アンモニウムイオンが水質のアルカリ化によって毒性のあるアンモニアに、さらに毒性のある亜硝酸への酸化還元の往復による酸素の大量消費を引き起こす。  Due to the oxidation reaction, nitrogen is transferred to ammonium ions, ammonium ions to nitrite ions, and nitrite ions to nitrate ions, and the opposite occurs in the reduction reaction. At that time, in an unstable state of eutrophication, ammonium ions cause toxic ammonia by water alkalinization, and also cause large consumption of oxygen by reciprocating redox to toxic nitrous acid.

本発明は、閉鎖的水域に起きる、pHの異常、不安定窒素分の過多、リンの増加これら富栄養化による不透明化、悪臭、汚泥化の抜本的改善を課題とする。  An object of the present invention is to drastically improve opacification, malodor, and sludge generation due to eutrophication due to abnormal pH, increased excessive nitrogen content, and increased phosphorus in closed waters.

天然資材を使用するため低コストで提供でき、かつ確実に改善することを課題とする。
さらに、低コストで良好な工法を提供することを課題とする。
Since natural materials are used, it is possible to provide them at low cost and to improve them reliably.
Furthermore, it aims at providing a favorable construction method at low cost.

本発明は、珪藻土、ゼオライト、植物質破片の機能、性能と木酢液、微生物の有用性の組み合せを環境改善材としての提供を目的とする。  An object of the present invention is to provide a combination of the function and performance of diatomaceous earth, zeolite, and plant fragments and the utility of pyroligneous acid and microorganisms as an environmental improvement material.

本発明は、組み合わせ、作業手順、量の調整によって個々の問題を持つ閉鎖的水域に合わせた改善を図ることが出来る。(汚染改善、絶滅危惧種保護の水質、土壌改善等)  The present invention can be improved for a closed water area having individual problems by adjusting the combination, work procedure, and quantity. (Contamination improvement, water quality of endangered species protection, soil improvement, etc.)

富栄養化で異常発生した植物、植物プランクトンの光合成のために弱酸性成分の炭酸等が消費され、強アルカリ性pH10±1を示すようになった水域の改善方法については、木酢液を2000倍溶液になる量で投入する。pHを7±1に調整することが出来、アンモニアの発生をなくす。長い期間アルカリ性になっていた水中では、アルカリ性に対応した微生物や化合物が大量に発生していることから迅速なpH調整のできる木酢液でpHをさげ偏りを解消する。また、木酢液の成分により消臭、殺菌の効果を得る。着色反応で珪藻土の凝集沈澱効果を補助する効果がある。
pHの数値によっては珪藻土のみで下げることも出来る。
For the improvement method of water areas where weakly acidic components such as carbonic acid are consumed for photosynthesis of eutrophication plants and phytoplankton, a 2000 times solution of wood vinegar is used. In the amount to become. The pH can be adjusted to 7 ± 1, eliminating the generation of ammonia. In water that has been alkaline for a long period of time, a large amount of microorganisms and compounds corresponding to alkalinity are generated. In addition, deodorizing and sterilizing effects are obtained by the components of the wood vinegar solution. The coloring reaction has an effect of assisting the coagulating sedimentation effect of diatomaceous earth.
Depending on the pH value, it can be lowered only with diatomaceous earth.

微生物の死骸や化合物、水中塵(SS)の処理をし、透明度を上げるには、珪藻土2μ粉末を水量1t当たり1kg水面に散布する。超多孔質構造を利用した凝集沈澱効果により3時間から6時間で透明化し12時間では完全に沈下する。汚水透明度10cm以下が水道水と同じ透明度になる。
また、珪藻土による底汚泥の被膜処理が出来るとともに、微生物分解の促進良好な多孔質土壌が与えられ汚泥低減する。
In order to increase the transparency by treating microbial carcasses and compounds and underwater dust (SS), diatomaceous earth 2μ powder is sprayed on the surface of 1 kg of water per 1 ton of water. It becomes transparent in 3 to 6 hours due to the coagulation precipitation effect utilizing a superporous structure, and completely settles in 12 hours. Sewage transparency of 10 cm or less is the same transparency as tap water.
Moreover, the bottom sludge can be coated with diatomaceous earth, and the porous soil with good microbial degradation can be given to reduce sludge.

酸素溶存量の増加、イオン交換の為にゼオライト1〜5mmを水量1t当たり2kg投入し瀑気する。多孔質から微細な気泡(マイクロバブル・モスキート)を発生し汚染物質を吸着、反応させる。イオン交換を行い水質を浄化する。また、ゼオライトによる底汚泥の被膜処理が出来るとともに、微生物分解の促進良好な多孔質土壌が与えられ汚泥低減する。  In order to increase the amount of dissolved oxygen and perform ion exchange, 2 kg of zeolite 1 to 5 mm is introduced per 1 ton of water and aerated. Microbubbles (microbubbles / mosquitoes) are generated from the porous material to adsorb and react with contaminants. Ion exchange to purify water quality. In addition, the bottom sludge can be coated with zeolite, and the porous soil with good acceleration of microbial degradation can be provided to reduce sludge.

流入口への汚染物質流入を防ぐには、ゼオライト5〜15mmを農業用ネットにいれ排水溝にしきつめる。濾過効果、反応、イオン交換、酸素溶存、pH調整をおこなう。実施例を[図1]に示す。
一定期間使用した後は[0020]の方法で微生物分解し再利用できる。
To prevent the inflow of pollutants to the inflow port, place zeolite 5-15mm in an agricultural net and tighten it in the drain. Perform filtration effect, reaction, ion exchange, oxygen dissolution, pH adjustment. An example is shown in FIG.
After being used for a certain period, it can be decomposed and reused by the method of [0020].

水質活性材、補助改善材として、珪藻土、ゼオライトの一方もしくは両方を木酢液に12時間以上浸し乾燥させることにより木酢液の成分を含浸し優れた作用を複合した浄化材となる。  As a water quality active material and an auxiliary improving material, one or both of diatomaceous earth and zeolite is immersed in a wood vinegar solution for 12 hours or more and dried to impregnate the components of the wood vinegar solution and become a purification material that combines excellent actions.

水質活性材、補助改善材として、多孔質構造にした植物質破片に、好気性、嫌気性の土壌菌、乳酸菌、中間菌、光合成菌等の有効菌類を培養し、珪藻土、ゼオライトの一方もしくは両方と混合し1ヶ月程水分量68%温度20℃〜40℃で培養し、培養の進んだところで水分量30%以下にすることで多孔質内に微生物を複合した浄化材となる。  As a water quality active material and auxiliary improvement material, aerobic and anaerobic soil bacteria, lactic acid bacteria, intermediate bacteria, photosynthetic bacteria, and other effective fungi are cultured on a porous plant structure, and one or both of diatomaceous earth and zeolite And the mixture is cultured for about one month at a water content of 68% at a temperature of 20 ° C. to 40 ° C., and when the culture proceeds, the water content is reduced to 30% or less to provide a purification material in which microorganisms are combined in the porous material.

水質活性剤、補助改善材として、有効菌類を培養した水溶液を珪藻土、ゼオライトの一方もしくは両方に1ヶ月含浸させることで、多孔質内に微生物を複合した浄化材となる。  By impregnating one or both of diatomaceous earth and zeolite for one month with an aqueous solution in which effective fungi are cultured as a water quality activator and auxiliary improving material, a purification material in which microorganisms are combined in a porous material is obtained.

前記[0019][0020][0021]に使用する木酢液濃度、微生物選択、珪藻土、ゼオライトの大きさ、量、配合割合、手順は、生態系、周辺環境等の個々の問題をもつ閉鎖的水域に合わせてサンプル・パターン検証を行うことで容易に求められる。  [0019] [0020] [0020] [0021] Concentration of wood vinegar, microorganism selection, diatomaceous earth, zeolite size, amount, blending ratio, procedure is a closed water area having individual problems such as ecosystem and surrounding environment It is easily obtained by performing sample pattern verification according to the above.

前記[0019][0020][0021]の補助浄化材は、工程途中や終了後の調整散布に用いる。他、汎用性があるので、少量の貯水の水域に散布するのであればパターン検証を用いないで安価に水質改善処理をすることが可能である。  The auxiliary purification material of the above [0019] [0020] [0021] is used for adjustment spraying during or after the process. In addition, because of its versatility, it is possible to perform water quality improvement at low cost without using pattern verification if it is applied to a small amount of stored water.

実験池の水質に対し、本工法[0015][0016][0017]の手順で行われた実験の結果、本工法は即時的効果を発揮し、分解促進による継続効果をみせた。工法の安全性と確実性をみせた。実験結果を[図2]に示す。  As a result of experiments conducted on the water quality of the experimental pond according to the procedure of this construction method [0015] [0016] [0017], this construction method showed an immediate effect and showed a continuous effect by promoting decomposition. Shows the safety and certainty of the construction method. The experimental results are shown in FIG.

pHは、中性域に安定した。  The pH was stable in the neutral range.

透明度は、水道水と差が無く、これ以上無い改善をみせる。  Transparency is not different from tap water and shows no further improvement.

CODは、実験時数値上増加をみせたが他の改善状況、周辺状況から本資材の成分が水中に溶存したことによる。生態系サイクルにより安定する。  Although COD showed an increase in numerical values during the experiment, it was due to the fact that the components of this material were dissolved in water due to other improvements and surrounding conditions. Stable by ecosystem cycle.

残留塩素は、無化された。  Residual chlorine was eliminated.

窒素体は、実験の結果から植物に取り入れられる硝酸イオンにスムーズに移行したことが分かる。  It can be seen from the results of the experiment that the nitrogen body smoothly migrated to nitrate ions incorporated into the plant.

酸素溶存は、硝酸値が安定していることから、酸素溶存が増加していることが分かる。  It can be seen that oxygen dissolution is increased because the nitric acid value is stable.

リン酸が減少したことから富栄養化の改善がみられる。  Improved eutrophication is seen due to the decrease in phosphate.

本工法実験時の被膜効果による貯水量への影響は1cmから3cmと少なく済み、時間経過とともに汚泥低減が観られる。  The effect on the amount of water stored by the coating effect during this construction method experiment is as small as 1 to 3 cm, and sludge reduction is observed over time.

天然資源が有する特性から、独自効果の大きい作用が発見された。超微細、超多孔質の天然素材は残留農薬や重金属を吸着分解し、塩素除去、酸化触媒反応をおこさせ、臭気物質を酸化分解させることにより、酸化触媒し反応する臭気物質を分解させる。蛋白質の腐敗臭、動物の排泄物質等の分解。チッソ、リンサン等の残留農薬の吸着分解、流失油等の有害物質の吸着、静菌作用、酸度調整による有効微生物の生息環境を整え優れた効果を発揮する。においの二次発生源である雑菌の繁殖を防止し脱臭効果がある。さらに、アンモニア、チッソの除去。重金属イオンの吸着除去、硬水の軟水化をする。アンモニアガスの吸着もあり、ガス体の分離として酸素、チッソの分離をする。アンモニア、チッソの吸着による脱臭作用がある。  Due to the characteristics of natural resources, a unique action was discovered. Ultrafine and ultraporous natural materials adsorb and decompose residual pesticides and heavy metals, remove chlorine, cause oxidation catalytic reactions, and oxidatively decompose odorous substances, thereby oxidizing and decomposing odorous substances that react. Decomposition of protein rotten odor, animal excrement, etc. Adsorbs and decomposes residual pesticides such as Chisso and Rinsan, adsorbs harmful substances such as oil loss, bacteriostatic action, and adjusts the acidity to adjust the habitat of effective microorganisms and exerts excellent effects. Prevents the growth of bacteria that are secondary sources of odors and has a deodorizing effect. Furthermore, removal of ammonia and nitrogen. Adsorbs and removes heavy metal ions and softens hard water. There is also adsorption of ammonia gas, and oxygen and nitrogen are separated as gas bodies. Deodorized by adsorption of ammonia and nitrogen.

天然素材の木酢液、珪藻土、ゼオライト、植物質破片の有用な特徴と細孔部に吸着保持された微生物の相乗効果によってこれまでにない優れた環境改善材を得ることができた。  Due to the useful characteristics of natural materials such as wood vinegar, diatomaceous earth, zeolite, and plant fragments, and the synergistic effect of microorganisms adsorbed and retained in the pores, we were able to obtain an unprecedented environmental improvement material.

多孔質体気孔に木酢液を含浸させることにより気孔部分の相互流通作用により木酢液成分を徐々に放散させ脱臭、水の浄化、腐敗防止の効果がある。  By impregnating the porous body pores with the wood vinegar liquid, the wood vinegar liquid components are gradually diffused by the mutual circulation action of the pores, and there is an effect of deodorization, water purification and anti-corruption.

さらに環境改良材として、持続的効果の得られることが発見された。  Furthermore, it was discovered that a sustainable effect can be obtained as an environmental improvement material.

有用な微生物が多孔質体に付着、接着、植え付け、浸透することにより汚泥の有機物を分解し生態系サイクルしやすい環境とする。  Useful microorganisms adhere to, adhere to, plant, and permeate the porous material to decompose sludge organic matter and create an environment that is easy to cycle through the ecosystem.

本発明による汚泥分解、水質浄化剤は、安全性・経済性ともに優れ、低コストでしかも実用に優れた水質、汚泥の改善を特徴とする環境用材に関する。  The sludge decomposition and water purification agent according to the present invention relates to an environmental material characterized by improved water quality and sludge which is excellent in safety and economy, low in cost and excellent in practical use.

本発明の浄化材は汚泥、水質の汚染を吸収分解する環境浄化材であり環境汚染はなく散布することにより水深、水域、沼、湖の微生物が流されず維持管理費の少ない水質浄化材です。  The purification material of the present invention is an environmental purification material that absorbs and decomposes sludge and water pollution, and it is a water quality purification material that has low maintenance costs because it is free from environmental pollution and the microorganisms in the water depth, water area, swamp, and lake are not washed away. .

汚染の原因であるチッソやリン等の物質浄化と水質浄化について微生物作用による水質浄化作用がある。使用後は土壌改良剤として還元され資源循環型社会の推進とする。  There is a water purification effect by microbial action for purification of substances such as nitrogen and phosphorus and water purification that are the cause of pollution. After use, it is reduced as a soil conditioner and promotes a resource recycling society.

珪藻土は、秋田県北秋田市より産出する珪藻土。ゼオライトは秋田県能代市二ツ井より産出する鉱物、焼成しモリブデンゼオライト構造にしたものが望ましい。前記珪藻土の組成分析結果を[図3]に、前記ゼオライトの組成分析結果を[図4]に示す。木酢液については、北秋田市産地品を活用し、日本木竹酢液協会の方法で分析し、木酢液の企画に定められた品質でもっての使用であり、フェノール類を含む効果から消毒、消臭、脱臭、防菌等に効果がある。(木酢液は日本木竹酢液協会の認定協議会の認定品を使用)  Diatomaceous earth is diatomaceous earth produced from Kitaakita City, Akita Prefecture. Zeolite is preferably a mineral produced from Futatsui, Noshiro City, Akita Prefecture, and calcined into a molybdenum zeolite structure. The composition analysis result of the diatomaceous earth is shown in [FIG. 3], and the composition analysis result of the zeolite is shown in [FIG. 4]. For wood vinegar, use Kitaakita City local products, analyze it by the method of the Japan Wood Bamboo Vinegar Association, and use it with the quality specified in the plan for wood vinegar, disinfecting from the effects including phenols, Effective for deodorization, deodorization, antibacterial effect, etc. (For wood vinegar, use a certified product of the Japan Wood Bamboo Vinegar Association)

木酢液でpH調整を迅速に行い、珪藻土で凝集沈澱、ゼオライトで瀑気、イオン交換を行い組成成分効果、皮膜効果で水質、土壌の浄化を天然資材のみで行う浄化方法。  A purification method that quickly adjusts pH with wood vinegar, coagulates and precipitates with diatomaceous earth, aerated and ion-exchanged with zeolite, and uses only natural materials to purify water and soil with compositional effects and film effects.

珪藻土を水面から散布する際、凝集沈澱しやすい水分量にする。  When diatomaceous earth is sprayed from the surface of the water, the water content should be easy to coagulate and settle.

水面から散布することにより、汚水及び有害物質のアンモニア、硫化水素、硫黄化合物、硝酸、亜硝酸を本水質浄化材により水質の安定化とイオン交換作用によって除去する。  By spraying from the surface of the water, sewage and harmful substances such as ammonia, hydrogen sulfide, sulfur compounds, nitric acid and nitrous acid are removed by this water purification material by stabilization of water quality and ion exchange action.

本発明の水質浄化活性方法、浄化材は天然多孔質物質をベースとしており無害を特徴とする。  The water purification activity method and purification material of the present invention are based on natural porous materials and are harmless.

本発明に係る水質浄化材はバイオ浄化システムによって汚泥分解することから汚染池、沼に散布することにより微生物の有機物の分解作用によるバイオ技術によって汚泥を低減分解する。  Since the water purification material according to the present invention decomposes sludge by a bio-purification system, the sludge is reduced and decomposed by biotechnology based on the decomposition action of organic substances of microorganisms by spraying it on a contaminated pond and swamp.

絶滅危惧種にあわせた環境改善をすることで保護する。  Protect by improving the environment to suit endangered species.

流入口への浄化材設置の実施例である。It is an Example of the purification | cleaning material installation to an inflow port. 本工法の水質浄化実験結果。Results of water purification experiments using this method. 珪藻土の組成分析表である。It is a composition analysis table | surface of diatomaceous earth. ゼオライトの組成分析表である。3 is a composition analysis table of zeolite.

Claims (3)

木酢液、珪藻土、ゼオライト、植物質破片、微生物の天然資材からなる水質活性材料。  Water quality active material consisting of wood vinegar, diatomaceous earth, zeolite, plant debris, microbial natural materials. 木酢液、珪藻土、ゼオライト、植物質破片、微生物の組み合せからなる水質活性材料。  Water quality active material consisting of a combination of wood vinegar, diatomaceous earth, zeolite, plant fragments, and microorganisms. 請求項1、2を使用する水質浄化活性方法と工法。  The water purification activity method and construction method using Claims 1 and 2.
JP2006184925A 2006-06-06 2006-06-06 Water purifying and activating method in closed water area putting natural material to practical use and construction method therefor Pending JP2007326090A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2006184925A JP2007326090A (en) 2006-06-06 2006-06-06 Water purifying and activating method in closed water area putting natural material to practical use and construction method therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2006184925A JP2007326090A (en) 2006-06-06 2006-06-06 Water purifying and activating method in closed water area putting natural material to practical use and construction method therefor

Publications (1)

Publication Number Publication Date
JP2007326090A true JP2007326090A (en) 2007-12-20

Family

ID=38926947

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2006184925A Pending JP2007326090A (en) 2006-06-06 2006-06-06 Water purifying and activating method in closed water area putting natural material to practical use and construction method therefor

Country Status (1)

Country Link
JP (1) JP2007326090A (en)

Cited By (17)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2010103624A1 (en) * 2009-03-11 2010-09-16 浦野 哲一 System for water purification
CN103626306A (en) * 2013-12-05 2014-03-12 慈溪市宗汉弘盛塑料制品厂 Method for comprehensive application treatment of heavy metal ion wastewater
CN103951000A (en) * 2014-04-18 2014-07-30 安徽省中日农业环保科技有限公司 Powdered cyanobacteria treatment agent with antibacterial property and manufacturing method thereof
CN105130007A (en) * 2015-08-17 2015-12-09 太仓市璜泾大文特种水产养殖专业合作社 Soft-shelled turtle culture water quality conditioning agent
CN105668738A (en) * 2016-02-29 2016-06-15 济南大学 Biomass coupling coagulant synthesized by vinegar residue
CN105731621A (en) * 2016-02-29 2016-07-06 济南大学 Biomass coupling coagulant aid synthesized by fungus chaffs and plantasan
CN106082386A (en) * 2016-07-30 2016-11-09 铜仁市万山区龙门山泉饮用水有限公司 A kind of pure natural water purification filtrate
JP2017507769A (en) * 2015-01-16 2017-03-23 シャントウ チェンネンリャン ハーベイシャス プランツ リサーチ インスティテュート Sewage activated particles and method for preparing the same
CN107265660A (en) * 2017-06-27 2017-10-20 兰溪市普润斯水产养殖技术有限公司 Eutrophication water quality cleanser
CN107601799A (en) * 2017-11-09 2018-01-19 中建水务环保有限公司 River bottom mud administering method on the spot
KR20180029131A (en) * 2016-09-09 2018-03-20 이미영 Ceramic substrate manufacturing method that includes natural polymer material algae removal and water purification
CN108275785A (en) * 2018-01-23 2018-07-13 刘牧 The application method of micro- oxygen particle of in situ environment microbial acclimation is modified through EM
CN109761451A (en) * 2019-03-19 2019-05-17 广西科学院 A kind of administering method of petroleum-contaminated water containing algae
CN110104779A (en) * 2019-03-29 2019-08-09 浙江农林大学 A kind of construction method of farmland nitrogen phosphorus ecological intercepting sewerage
CN110950460A (en) * 2019-12-20 2020-04-03 何亚婷 Multi-function pretreatment and double-membrane filtration coupling strengthening treatment process and method
CN111762838A (en) * 2020-06-24 2020-10-13 安徽百和环保科技有限公司 Water body algae treatment method
CN114686474A (en) * 2022-04-19 2022-07-01 上海艾尔天合环境科技有限公司 Preparation method of multi-strain solidified mycelium pellet, multi-strain solidified mycelium pellet and application

Cited By (22)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2010103624A1 (en) * 2009-03-11 2010-09-16 浦野 哲一 System for water purification
CN103626306A (en) * 2013-12-05 2014-03-12 慈溪市宗汉弘盛塑料制品厂 Method for comprehensive application treatment of heavy metal ion wastewater
CN103626306B (en) * 2013-12-05 2015-04-22 慈溪市宗汉弘盛塑料制品厂 Method for comprehensive application treatment of heavy metal ion wastewater
CN103951000A (en) * 2014-04-18 2014-07-30 安徽省中日农业环保科技有限公司 Powdered cyanobacteria treatment agent with antibacterial property and manufacturing method thereof
CN103951000B (en) * 2014-04-18 2015-06-03 安徽省中日农业环保科技有限公司 Powdered cyanobacteria treatment agent with antibacterial property
JP2017507769A (en) * 2015-01-16 2017-03-23 シャントウ チェンネンリャン ハーベイシャス プランツ リサーチ インスティテュート Sewage activated particles and method for preparing the same
CN105130007A (en) * 2015-08-17 2015-12-09 太仓市璜泾大文特种水产养殖专业合作社 Soft-shelled turtle culture water quality conditioning agent
CN105668738A (en) * 2016-02-29 2016-06-15 济南大学 Biomass coupling coagulant synthesized by vinegar residue
CN105731621A (en) * 2016-02-29 2016-07-06 济南大学 Biomass coupling coagulant aid synthesized by fungus chaffs and plantasan
CN106082386A (en) * 2016-07-30 2016-11-09 铜仁市万山区龙门山泉饮用水有限公司 A kind of pure natural water purification filtrate
KR20180029131A (en) * 2016-09-09 2018-03-20 이미영 Ceramic substrate manufacturing method that includes natural polymer material algae removal and water purification
CN107265660A (en) * 2017-06-27 2017-10-20 兰溪市普润斯水产养殖技术有限公司 Eutrophication water quality cleanser
CN107601799A (en) * 2017-11-09 2018-01-19 中建水务环保有限公司 River bottom mud administering method on the spot
CN108275785A (en) * 2018-01-23 2018-07-13 刘牧 The application method of micro- oxygen particle of in situ environment microbial acclimation is modified through EM
CN109761451A (en) * 2019-03-19 2019-05-17 广西科学院 A kind of administering method of petroleum-contaminated water containing algae
CN110104779A (en) * 2019-03-29 2019-08-09 浙江农林大学 A kind of construction method of farmland nitrogen phosphorus ecological intercepting sewerage
CN110950460A (en) * 2019-12-20 2020-04-03 何亚婷 Multi-function pretreatment and double-membrane filtration coupling strengthening treatment process and method
CN110950460B (en) * 2019-12-20 2022-06-28 巴东水务建设工程有限公司 Multi-function pretreatment and double-membrane filtration coupling strengthening treatment process and method
CN111762838A (en) * 2020-06-24 2020-10-13 安徽百和环保科技有限公司 Water body algae treatment method
CN111762838B (en) * 2020-06-24 2023-08-04 安徽百和环保科技有限公司 Water algae treatment method
CN114686474A (en) * 2022-04-19 2022-07-01 上海艾尔天合环境科技有限公司 Preparation method of multi-strain solidified mycelium pellet, multi-strain solidified mycelium pellet and application
CN114686474B (en) * 2022-04-19 2023-08-15 上海艾尔天合环境科技有限公司 Preparation method of multi-strain solidified mycelium pellet, multi-strain solidified mycelium pellet and application

Similar Documents

Publication Publication Date Title
JP2007326090A (en) Water purifying and activating method in closed water area putting natural material to practical use and construction method therefor
CN107555498B (en) Integrated in-situ remediation and treatment agent for black and odorous water body and bottom mud on ground surface as well as preparation method and application of integrated in-situ remediation and treatment agent
OB et al. Bioremediation of polluted wastewater influent: Phosphorus and nitrogen removal
US20050142096A1 (en) Product for and method of controlling odor in open waste water treatment environments
CN105217802A (en) A kind of water quality cleansing agent
KR101355178B1 (en) Water treating agent of food wastewater and for removing green algae, red algae and odors
JP3820180B2 (en) Purification method for contaminated soil
CN107311315B (en) Black and odorous water body purification method based on biological-ecological coupling
AU2003234901B2 (en) Water clarifying agent inducing catalytic reaction and method of clarifying water through activation of microorganism
JP2011212653A (en) Water purifying filter medium and method of producing the same
CN107935098A (en) A kind of method for handling organic wastewater
KR20240047343A (en) A device for purifying the water quality of reservoirs and removing green algae using anionic radical circulation ceramics
KR100785849B1 (en) Manufacture methods of fertilizer about organic waste in excrements of livestock
Borah et al. Leakage of surfactants in greywater: Environmental impact, mitigation, and their circular economy
JP2012176390A (en) Filter and method of manufacturing the same
Moussavi et al. The removal of H2S from process air by diffusion into activated sludge
JP2004034008A (en) Harmful organic material removal method using quick lime, hydrogen peroxide, and heat treatment
CN103663695B (en) A kind of method removing nitrogen phosphorus in waste water
JP2011036843A (en) Culture of bacteria carrier, stuck body thereof, and method for producing the same
CN102139964A (en) Method for effectively controlling algal blooms by utilizing microbes
JP2004275949A (en) Excreta decomposing treating agent and decomposing treating method for excreta by activation of microorganism
KR20000016879A (en) Water-Catalyst Treating Apparatus Using Function Ceramic, Liquid Discharging System Using Water-Catalyst Treating Apparatus, and Water-Catalyst Using Method
KR101355177B1 (en) Water treating agent for removing green algae, red algae and odors in water
JP2007301543A (en) Water purifying agent and method therefor
JP2011050318A (en) Water with purification function and method for utilizing the same