JPH0365296A - Water purifying apparatus - Google Patents
Water purifying apparatusInfo
- Publication number
- JPH0365296A JPH0365296A JP1202509A JP20250989A JPH0365296A JP H0365296 A JPH0365296 A JP H0365296A JP 1202509 A JP1202509 A JP 1202509A JP 20250989 A JP20250989 A JP 20250989A JP H0365296 A JPH0365296 A JP H0365296A
- Authority
- JP
- Japan
- Prior art keywords
- water
- bacteria
- stirring
- air bubbles
- sewage
- 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
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims description 74
- 241000894006 Bacteria Species 0.000 claims abstract description 59
- 238000003756 stirring Methods 0.000 claims abstract description 24
- 238000002156 mixing Methods 0.000 claims abstract description 20
- 239000007788 liquid Substances 0.000 claims description 25
- 238000000746 purification Methods 0.000 claims description 18
- 239000003344 environmental pollutant Substances 0.000 claims description 17
- 231100000719 pollutant Toxicity 0.000 claims description 17
- 239000002351 wastewater Substances 0.000 claims description 14
- 241000251468 Actinopterygii Species 0.000 claims description 10
- IOVCWXUNBOPUCH-UHFFFAOYSA-M Nitrite anion Chemical compound [O-]N=O IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 claims description 2
- 235000015170 shellfish Nutrition 0.000 claims 1
- 239000010865 sewage Substances 0.000 abstract description 12
- 239000000356 contaminant Substances 0.000 abstract description 4
- 235000015097 nutrients Nutrition 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- 230000000694 effects Effects 0.000 description 6
- 230000001105 regulatory effect Effects 0.000 description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 5
- 229910052760 oxygen Inorganic materials 0.000 description 5
- 239000001301 oxygen Substances 0.000 description 5
- 241000894007 species Species 0.000 description 4
- IMQLKJBTEOYOSI-GPIVLXJGSA-N Inositol-hexakisphosphate Chemical compound OP(O)(=O)O[C@H]1[C@H](OP(O)(O)=O)[C@@H](OP(O)(O)=O)[C@H](OP(O)(O)=O)[C@H](OP(O)(O)=O)[C@@H]1OP(O)(O)=O IMQLKJBTEOYOSI-GPIVLXJGSA-N 0.000 description 3
- IMQLKJBTEOYOSI-UHFFFAOYSA-N Phytic acid Natural products OP(O)(=O)OC1C(OP(O)(O)=O)C(OP(O)(O)=O)C(OP(O)(O)=O)C(OP(O)(O)=O)C1OP(O)(O)=O IMQLKJBTEOYOSI-UHFFFAOYSA-N 0.000 description 3
- 238000013019 agitation Methods 0.000 description 3
- 239000010842 industrial wastewater Substances 0.000 description 3
- 238000000034 method Methods 0.000 description 3
- 229940068041 phytic acid Drugs 0.000 description 3
- 239000011148 porous material Substances 0.000 description 3
- 230000004083 survival effect Effects 0.000 description 3
- 210000002700 urine Anatomy 0.000 description 3
- IIZPXYDJLKNOIY-JXPKJXOSSA-N 1-palmitoyl-2-arachidonoyl-sn-glycero-3-phosphocholine Chemical compound CCCCCCCCCCCCCCCC(=O)OC[C@H](COP([O-])(=O)OCC[N+](C)(C)C)OC(=O)CCC\C=C/C\C=C/C\C=C/C\C=C/CCCCC IIZPXYDJLKNOIY-JXPKJXOSSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- IOVCWXUNBOPUCH-UHFFFAOYSA-N Nitrous acid Chemical compound ON=O IOVCWXUNBOPUCH-UHFFFAOYSA-N 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000010840 domestic wastewater Substances 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 238000007667 floating Methods 0.000 description 2
- 239000012530 fluid Substances 0.000 description 2
- 239000000787 lecithin Substances 0.000 description 2
- 235000010445 lecithin Nutrition 0.000 description 2
- 229940067606 lecithin Drugs 0.000 description 2
- 239000011859 microparticle Substances 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 239000000467 phytic acid Substances 0.000 description 2
- 235000002949 phytic acid Nutrition 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 241000590020 Achromobacter Species 0.000 description 1
- 244000068988 Glycine max Species 0.000 description 1
- 235000010469 Glycine max Nutrition 0.000 description 1
- 241000187654 Nocardia Species 0.000 description 1
- 240000007594 Oryza sativa Species 0.000 description 1
- 235000007164 Oryza sativa Nutrition 0.000 description 1
- 241000607598 Vibrio Species 0.000 description 1
- 241001148470 aerobic bacillus Species 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 230000001580 bacterial effect Effects 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- TWFZGCMQGLPBSX-UHFFFAOYSA-N carbendazim Chemical compound C1=CC=C2NC(NC(=O)OC)=NC2=C1 TWFZGCMQGLPBSX-UHFFFAOYSA-N 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000000593 degrading effect Effects 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 238000007865 diluting Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 235000020774 essential nutrients Nutrition 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000003925 fat Substances 0.000 description 1
- 238000000855 fermentation Methods 0.000 description 1
- 230000004151 fermentation Effects 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 239000008235 industrial water Substances 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 229920005610 lignin Polymers 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 230000003472 neutralizing effect Effects 0.000 description 1
- 235000019645 odor Nutrition 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 239000001814 pectin Substances 0.000 description 1
- 235000010987 pectin Nutrition 0.000 description 1
- 229920001277 pectin Polymers 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- WTJKGGKOPKCXLL-RRHRGVEJSA-N phosphatidylcholine Chemical compound CCCCCCCCCCCCCCCC(=O)OC[C@H](COP([O-])(=O)OCC[N+](C)(C)C)OC(=O)CCCCCCCC=CCCCCCCCC WTJKGGKOPKCXLL-RRHRGVEJSA-N 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 229920002635 polyurethane Polymers 0.000 description 1
- 239000004814 polyurethane Substances 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 235000009566 rice Nutrition 0.000 description 1
- 239000013535 sea water Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 239000000271 synthetic detergent Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Abstract
Description
【発明の詳細な説明】 〔産業上の利用分野〕 本発明は汚水等を浄化する水浄化装置に間する。[Detailed description of the invention] [Industrial application field] The present invention relates to a water purification device for purifying sewage and the like.
家庭排水や工場排水は、そのままあるいはある程度浄化
されて下水や河川に流されている。これら排水が汚泥や
悪臭の原因となったり、水中に含まれる酸素の含有量を
少な(し、魚等の生物を汚染し、またその生存を危う(
している。Domestic and industrial wastewater is discharged into sewers and rivers either as is or after being purified to some extent. These wastewaters cause sludge and bad odors, reduce the oxygen content in the water, contaminate fish and other living things, and endanger their survival.
are doing.
このような状態を放置すると、河川は単なる家庭や工場
排水の下水路的役割しかな(なり、河川の終点である湖
、沼あるいは海は塵棄場となることは、霞ケ浦や瀬戸内
海等の汚染を報告する新聞をみても明らかなことである
。河川や海に生きている魚等の生存を危うくすることは
、河川や海から食料を得ることができなくなるだけでは
なく、人間を含めた生態系を破壊するものであり、人間
の生存を脅かすものである。If this situation is left unchecked, rivers will only serve as sewage channels for household and industrial wastewater (and the lakes, marshes, or oceans at the end of rivers will become garbage dumps, as is the case in Kasumigaura, the Seto Inland Sea, etc.). It is clear from reading newspapers reporting on pollution. Endangering the survival of fish living in rivers and the sea not only means that they will no longer be able to obtain food from rivers and the sea, but will also harm other people, including humans. It destroys the ecosystem and threatens human survival.
これら環境悪化の原因さなっている工場排水等について
フィルター等で濾過する方法があるが、濾過は物理的に
行うものであり、水溶液やフィルターの目より小さいも
のは通過してしまう、排水に化学薬品を加えて中和する
方法もあるが、中和しても魚等の生物が生息することが
できる水を再生することができるとは限られない。There is a method of filtering factory wastewater, etc., which is a cause of environmental deterioration, but filtration is done physically, and aqueous solutions and substances smaller than the size of the filter will pass through. There is also a method of neutralizing water by adding chemicals, but even with neutralization, it is not always possible to regenerate water that can be inhabited by fish and other creatures.
前記問題点を解決するために汚水の汚染物質を分解する
バクテリアが開発され、これを汚水に攪拌することが行
われている。しかしながら、ブロアー式(水車)やエジ
ェクター式(噴射)等の攪拌装置では充分に攪拌するこ
とができず、一部しか分解することができないという欠
点があった。In order to solve the above-mentioned problems, bacteria that decompose pollutants in wastewater have been developed, and bacteria are stirred into the wastewater. However, a blower-type (water wheel) or ejector-type (injection) type stirring device cannot sufficiently stir, and has the disadvantage that only a portion of the material can be decomposed.
バクテリアの能力を充分に発揮させるためにはバクテリ
アが自己増殖するのに必要な栄養分が必要であり、かつ
このバクテリアが好気性の場合は汚水中に充分な酸素が
含まれていなければならない。しかしながら従来の水浄
化装置ではこれを行うことはできず、汚水が充分に分解
されないままの状態で河川に垂れ流しされて前記公害問
題が生じていたのである。In order for bacteria to fully demonstrate their abilities, they need nutrients necessary for self-replication, and if the bacteria are aerobic, the wastewater must contain sufficient oxygen. However, conventional water purification devices cannot do this, and the sewage is discharged into rivers without being sufficiently decomposed, causing the above-mentioned pollution problem.
本発明は前記問題点を解決するためになされたものであ
って、従来よりもはるかに安価で汚水中の汚染物質を完
全に分解することのできる水浄化装置を提供すること目
的とする。The present invention has been made to solve the above-mentioned problems, and an object of the present invention is to provide a water purification device that can completely decompose pollutants in wastewater at a much lower cost than conventional methods.
前記目的のために本発明は、汚染物質を分解するバクテ
リアを蒔いた汚水中に、細かい空気の気泡と前記バクテ
リアの成長を促すバイオ補助液とを水中に送り込む攪拌
混合装置が設けられ、この攪拌混合装置が駆動されるこ
とにより前記空気の気泡と前記バイオ補助液とが水中に
攪拌される構成としている。For the above purpose, the present invention is provided with an agitation mixing device that feeds fine air bubbles and a bio-auxiliary liquid that promotes the growth of the bacteria into wastewater in which bacteria that decompose pollutants are inoculated, The air bubbles and the bioauxiliary liquid are stirred into the water by driving the mixing device.
以下、本発明を図面に示す実施例に基づき詳細に説明す
る。Hereinafter, the present invention will be explained in detail based on embodiments shown in the drawings.
第2図は、本発明の一実施例である水浄化装置に使用す
る液体と空気との攪拌混合装置の原理を示す断面図であ
る。FIG. 2 is a sectional view showing the principle of a stirring and mixing device for liquid and air used in a water purification device, which is an embodiment of the present invention.
この攪拌混合装置は、円筒のケーシング2内にある間隙
6を隔てて高速で回転する円筒の回転体1が設けられ、
回転体1の先端部には円周面に多数の空気孔10が設け
られた水流の流れる方向を規制する規制部材11が取り
付けられている。This stirring and mixing device is provided with a cylindrical rotating body 1 that rotates at high speed across a gap 6 in a cylindrical casing 2,
A regulating member 11 is attached to the tip of the rotating body 1 and has a large number of air holes 10 on its circumferential surface and regulates the direction of water flow.
以下、第2図に示す攪拌混合装置の動作について説明す
る。The operation of the stirring and mixing apparatus shown in FIG. 2 will be explained below.
ケーシング2の上部は第2図に示すように水面3上に設
けられ、ケーシング2と回転体1との間に形成されてい
る間隙6の上端の空気取り入れ口5が大気4中に突出し
ている。ここで回転体1がモータ(図示せず)により、
例えば7000rpmで回転させられると、回転体1と
ケーシング2との間に形成されている間隙6内の水が斉
速の渦流となり、この渦流が空気取り入れ口5から空気
を水中に取り込む、渦流内に取り込まれた当初の気泡は
相当な大きさがあるが、高速渦流の作用を受けると空気
と液体の粘性や重さ等の物性の相違により、気泡は細か
く砕かれながら間隙ε内を矢印12の方向に進む0間隙
6の下端に設けた出口9では、空気の気泡は10万分の
1〔備〕程度の大きさとなっており、これが水中に放出
される。The upper part of the casing 2 is provided above the water surface 3 as shown in FIG. 2, and the air intake port 5 at the upper end of the gap 6 formed between the casing 2 and the rotating body 1 protrudes into the atmosphere 4. . Here, the rotating body 1 is driven by a motor (not shown).
For example, when rotated at 7000 rpm, the water in the gap 6 formed between the rotating body 1 and the casing 2 becomes a vortex at a uniform speed, and this vortex draws air into the water from the air intake 5. Initially, the bubbles taken in are quite large, but when subjected to the action of high-speed vortices, due to the difference in physical properties such as viscosity and weight between air and liquid, the bubbles are broken into small pieces and move inside the gap ε as shown by the arrow 12. At the outlet 9 provided at the lower end of the zero gap 6, which moves in the direction of , air bubbles have a size of about 1/100,000 and are discharged into the water.
このとき回転体1の内部7に矢印8に示すように空気を
送り込めば、回転体1の下部に設けられている水の流れ
る方向を規制する規制部材11の空気孔10からの気泡
が、図面の左、右、奥、手前と回転体1と90度をなす
全ての方向に水の流れを規制する。At this time, if air is sent into the interior 7 of the rotating body 1 as shown by the arrow 8, air bubbles from the air holes 10 of the regulating member 11 provided at the bottom of the rotating body 1 that regulates the direction of water flow will The flow of water is regulated in all directions forming 90 degrees with the rotating body 1, including to the left, right, back, and front of the drawing.
間隙5の下部に設けられた出口9から放出された細かい
気泡は、その大きさが余りにも小さいために浮力が非常
に少なく、水面3に上昇するまでには長い時間がかかる
。同一容量の空気を水中に放出した場合、気泡が小さい
程空気と水との接触面積は小さい方が大となり、空気が
水中に溶ける度合いが高くなる。気泡の大きさが小さい
程その浮力は少なく水中に漂っている時間が長く、水と
接触する面積が大になることから、空気と水εの攪拌が
充分に行われることになる0本発明者が実験したところ
、出口9から放出された気泡は、あたかも空気中に放出
された煙のように水中に漂うことが確認されている。The fine bubbles released from the outlet 9 provided at the bottom of the gap 5 have very little buoyancy because of their small size, and it takes a long time for them to rise to the water surface 3. When the same volume of air is released into water, the smaller the bubble, the larger the contact area between the air and water, and the higher the degree to which air dissolves in water. The smaller the size of the bubble, the less its buoyancy, and the longer it stays floating in the water, and the larger the area in contact with the water, which results in sufficient agitation of air and water ε. conducted an experiment, and it was confirmed that the bubbles released from the outlet 9 floated in the water just like smoke released into the air.
第1図は、細かい空気の気泡とバイオ補助液とを水中に
攪拌させる攪拌混合装置の一部断面図であり、支持部材
13により固定されている。第2図の攪拌混合装置と異
なる点は、水中に攪拌するバイオ補助液の容器17及び
これに付属する部材並びにケーシング2の上部に水取り
入れ口16が設けられていることである。FIG. 1 is a partial sectional view of a stirring and mixing device for stirring fine air bubbles and a bioauxiliary liquid in water, and is fixed by a support member 13. FIG. The difference from the stirring/mixing device shown in FIG. 2 is that a water inlet 16 is provided at the top of the container 17 for the bioauxiliary liquid to be stirred in water, the members attached thereto, and the casing 2.
以下、この攪拌混合装置の動作について説明する。The operation of this stirring and mixing device will be explained below.
汚水中の汚染物質を分解する仮眠状態の無数のバクテリ
アが付着している多孔性物質20、例えばセラ藁ツクス
やポリウレタン等を水面3に浮かべると、この水分によ
りバクテリアが仮眠状態から覚めて活動を開始し、多孔
性物質20の周辺に漂い始める。モータ15の電源をオ
ンとし、回転体iが回転を開始すると間隙6内には高速
の渦流が発生し、大気中の空気が間隙6の上に設けられ
た空気取り入れ口5から、水がケーシング2に設けられ
た水取り入れ口16から、そしてバイオ補助液が容器i
7からバルブ18を通りパイプ19から各々間隙6内で
生じている渦流に巻き込まれる。水取り入れ口16から
間隙6に吸い込まれる水のなかには、この周辺に漂って
いるバクテリアが多数音まれている。When a porous material 20, to which countless bacteria in a napping state that decompose contaminants in wastewater are attached, such as serastraw or polyurethane, is floated on the water surface 3, the moisture wakes the bacteria from their napping state and makes them active. and begin to float around the porous material 20. When the power of the motor 15 is turned on and the rotating body i starts rotating, a high-speed eddy current is generated in the gap 6, and air from the atmosphere flows from the air intake port 5 provided above the gap 6, and water flows into the casing. From the water inlet 16 provided in 2, and the bioauxiliary liquid enters the container i
7, through the valve 18, and from the pipe 19, each of which is drawn into the vortex generated within the gap 6. The water sucked into the gap 6 from the water intake port 16 contains a large number of bacteria floating around it.
第2図に示す攪拌混合装置で説明したように、高速の渦
流に取り込まれた空気は細か(砕かれるのと同様に、バ
クテリア及びバイオ補助液も非常に細かく細分化されな
がら間隙6内を矢印12に示す方向に進む0間B6の下
端に設けられた出口9から放出される時には、微粒子状
の空気の気泡とバクテリア及びバイオ補助液が十二分に
攪拌され渾然一体となっている。出口9から放出された
空気の気泡等は、コンプレッサー14から回転体1の内
部を通過し規制部材11の空気孔10から出力される空
気の働きにより、水中に撒き散らされる。As explained in the stirring/mixing device shown in Fig. 2, the air taken in by the high-speed vortex flow is broken down into small pieces, and the bacteria and bioauxiliary liquid are also broken down into very fine pieces while moving inside the gap 6. When discharged from the outlet 9 provided at the lower end of the zero chamber B6 moving in the direction shown by 12, the particulate air bubbles, bacteria, and bio-auxiliary liquid are sufficiently agitated and harmoniously integrated. The air bubbles etc. released from the compressor 14 are scattered into the water by the action of the air that passes through the inside of the rotating body 1 from the compressor 14 and is output from the air hole 10 of the regulating member 11.
従来技術の項で説明したように、汚水中の汚染物質を分
解するバクテリアの能力を発揮させるためには、これが
戒長し自己増殖させる環境が整っていなければならない
、このために好気性のバクテリアにあっては水中に酸素
と、戒長し自己増矯するための栄養分が必要なのである
。このことは理解されてはいたが、攪拌手段が不充分の
ためにバクテリアに酸素や栄養分(バイオ補助液)が充
分に供給されず、これが成長あるいは自己増殖すること
を妨げていたのである。As explained in the prior art section, in order for bacteria to demonstrate their ability to decompose pollutants in wastewater, an environment must be in place for bacteria to thrive and self-propagate.For this reason, aerobic bacteria They need oxygen in the water and nutrients to strengthen and self-reinforce. Although this was understood, inadequate agitation means did not provide the bacteria with sufficient oxygen and nutrients (biosupplement), which prevented them from growing or reproducing on their own.
ところが、第2図に示す攪拌混合装置によればバクテリ
ア、微粒子状の空気の気泡及びバイオ補助液が渾然一体
となってとなって水中に漂うことことになり、バクテリ
アが戒長し自己増殖する条件が総て整い、この能力を充
分に発揮させることが可能となるのである。However, with the stirring and mixing device shown in Figure 2, the bacteria, particulate air bubbles, and bio-auxiliary liquid are mixed together and float in the water, causing the bacteria to grow and self-propagate. When all the conditions are met, it becomes possible to fully demonstrate this ability.
なお、空気の気泡がi0万分の1〔03位の微粒子とな
るとこれがイオン化され汚染物質に吸着し易く、これを
分解する働きが生じてくる。Note that when the air bubbles become fine particles of 1/00,000 [03], they are ionized and easily adsorbed to pollutants, and work to decompose them.
従って、このイオン化された微粒子状の空気の気泡とバ
クテリア作用の相乗効果により、汚染物質の分解が促進
され、浄化作用が一層高まる。Therefore, the synergistic effect of the ionized fine air bubbles and the bacterial action promotes the decomposition of pollutants and further enhances the purification effect.
気泡等の出口9を水中の底近くに設ければ、いくら気泡
が小さいからといっても必ず上昇するものであり、気泡
、バイオ補助液が水中の全体に攪拌され、水中全体の浄
化作用を行うことが可能さなる。If the outlet 9 for air bubbles etc. is provided near the bottom of the water, no matter how small the air bubbles are, they will always rise, and the air bubbles and bio-auxiliary liquid will be stirred throughout the water, and will have a purifying effect on the entire water. It becomes possible to do so.
第2図に示す実施例ではバクテリアを多孔性のセラミッ
ク20等に吸着させ、これを水面3上に浮かせていたが
、バイオ補助液と同様に容器に入れ、ここに水を注ぎバ
イブにより間隙6に注入しても、この水の中にはバクテ
リアが多数存在することになり、微粒子の空気の気泡と
バイオ補助液と共に水中に攪拌され、前記実施例と同様
の効果を得ることができる。In the embodiment shown in Fig. 2, bacteria were adsorbed onto a porous ceramic 20, etc., and this was floated on the water surface 3, but in the same way as the bio-auxiliary liquid, it was placed in a container, water was poured there, and a vibrator was used to make the gap 6. Even if the water is injected into the water, there will be a large number of bacteria in the water, which will be stirred into the water together with the microparticle air bubbles and the bio-auxiliary liquid, producing the same effect as in the previous example.
汚水の浄化作用を効果的に促進するには、バクテリアを
、微粒子の空気の気泡とバイオ補助液とにともに、水中
に充分攪拌すればよいのであるから、これらを渦流が生
じている間隙6でな(回転体1内に注入しても、コンプ
レッサー14から送られてくる空気と共に規制部材11
の空気孔10から水中に放出され、このとき間隙6の出
口9からの渦流により攪拌され浄化作用が促進される。In order to effectively promote the purification effect of sewage, it is sufficient to stir the bacteria together with the microparticle air bubbles and the bio-auxiliary liquid into the water. (Even if it is injected into the rotating body 1, the regulating member 11 will be mixed with the air sent from the compressor 14.
It is discharged into the water from the air hole 10 of the air hole 10, and at this time, it is stirred by the vortex flow from the outlet 9 of the gap 6, and the purification effect is promoted.
寒冷地では汚水中の温度が低く、バクテリアが成長し、
自己増殖するのに環境が整備されないこともあるが、水
中に微粒子の空気の気泡が放出されると、この気泡の圧
力が大気中のそれよりも高いために温度が上がり、この
エネルギーが水中に伝達されるために従来バクテリアの
使用することの出来ない寒冷地でもこの装置によれば、
浄化が可能となる。In cold regions, the temperature in wastewater is low, allowing bacteria to grow.
Sometimes the environment is not set up for self-propagation, but when microscopic air bubbles are released into water, the pressure of these bubbles is higher than that in the atmosphere, causing the temperature to rise, and this energy is transferred into the water. According to this device, even in cold regions where conventional bacteria cannot be used due to transmission,
Purification becomes possible.
ここで活魚を飼育し、搬送するときに使用する水槽内の
水を浄化するときについて説明する。活魚が健康な状態
で飼育され、あるいは搬送されるには、水槽内の水に充
分に酸素が含まれており、かつこれらから排出される屋
尿により水槽内の水が汚染されないことが必要である。Here, we will explain how to purify the water in the aquarium used when raising and transporting live fish. In order for live fish to be kept or transported in a healthy condition, the water in the aquarium must contain sufficient oxygen and must not be contaminated by the excreted urine. be.
しかしながら従来は、尿尿から発生する活魚の鮮度を失
わせる亜硝酸を除く手段がなかった。そのため、養魚場
では別の場所から多量の新鮮な水を注いで亜硝酸を薄め
たり、搬送するときには鮮度を保つためにこれに必要な
期間を出来るだけ短縮する他はなかった。そこで、この
水槽内に亜硝酸を分解するバクテリアを多孔性の物質に
吸着させ、第1図に示すように攪拌混合装置を働かせれ
ば、容易にこれを分解することができ、養魚場にあって
は新たな水を多量に注ぐ必要はなく、搬送する場合も従
来より時間がかかっても鮮度を保持することができる。However, in the past, there was no means to remove nitrous acid, which is generated from urine and urine and causes the freshness of live fish to be lost. For this reason, fish farms had no choice but to dilute the nitrous acid by diluting large amounts of fresh water from another location, and to shorten the time required for this as much as possible to maintain freshness during transport. Therefore, if bacteria that decompose nitrite are adsorbed to a porous material in this aquarium and a stirring/mixing device is used as shown in Figure 1, it will be possible to easily decompose the bacteria and eliminate the need for fish farms. There is no need to pour in a large amount of new water, and freshness can be maintained even if it takes longer to transport than before.
つぎに汚水中の汚染物質を分解するバクテリアについて
説明する。汚染物質がどのような化学的性質を有してい
るかによって、これを分解するバクテリアの種類を変え
なければならない、従ってこの水浄化装置を使用する際
には、汚水中の汚染1!FIXの化学的性質を調査し、
これを分解するに効果的なバクテリアを適宜選択する必
要がある。このバクテリアの選択を誤ると、効果的な浄
化をすることができない。Next, we will explain bacteria that decompose pollutants in wastewater. Depending on what kind of chemical properties the pollutants have, the type of bacteria that decompose them must be changed, so when using this water purification device, it is important to avoid contamination in wastewater! Investigate the chemical properties of FIX,
It is necessary to appropriately select bacteria that are effective in degrading this. If this bacteria is selected incorrectly, effective purification will not be possible.
そこで、現在排出されている多数の汚染物質の各々を分
解する多数のバクテリアを混合して、第1図に示すよう
に水中に攪拌すれば、生活環境に通しないバクテリアは
死んでも、適したバクテリアが成長し、自己増殖して汚
染物質を分解するから、選択を誤ることがない、多数の
バクテリアを混合したものとして、(株式会社)大和研
究所が販売している商品名 D−500がある。Therefore, if we mix a large number of bacteria that decompose each of the many pollutants that are currently being discharged and stir it into water as shown in Figure 1, bacteria that cannot pass through the living environment will die, but suitable bacteria will There is a product called D-500 sold by Yamato Institute Co., Ltd., which is a mixture of many bacteria that grows, reproduces on its own, and decomposes pollutants, so you don't have to make the wrong choice. .
このD−500は、
Ps eudomornus 系 18
0種Streptmyces 系 102
種Mi crococeus 系 1
0種Myco b aeterium 系 工
2種Vibrio 系
10種Nocardia 系
45種Flsvobacter 系
15種Achromobacter 系
14種N1trobacter 系
7種Aerobacter 系
9種の各種バクテリアから構成されており、各種廃
棄物中に含まれる油脂、石油、リグニン、セルローズ、
蛋白、ペクチン、各種化学薬品、合成洗剤等を分解する
。これらバクテリアは有機廃棄物を、水+炭酸ガスに分
解するため二次公害の心配がなく安全である。This D-500 is Ps eudomornus series 18
0 species Streptmyces series 102
Species Mi crococeus lineage 1
Type 0 Myco b aetherium type Engineering Type 2 Vibrio type
10 species Nocardia series
45 species of Flsvobacter series
15 species of Achromobacter
14 types of N1trobacter series
7 types of Aerobacter series
It is composed of 9 types of various bacteria, and it is used to treat fats, oils, petroleum, lignin, cellulose, etc. contained in various wastes.
Decomposes proteins, pectin, various chemicals, synthetic detergents, etc. These bacteria decompose organic waste into water and carbon dioxide, making it safe and free from secondary pollution.
次に前記バクテリアが成長し、自己増殖するのを助ける
バイオ補助液について説明する。Next, we will discuss the bio-auxiliary fluid that helps the bacteria grow and self-replicate.
バクテリアは水中の汚染物質を栄養分として成長し自己
増殖する場合もあるが、汚水の環境がバクテリアの成長
や自己増殖を妨げる場合もある。In some cases, bacteria can grow and reproduce by using pollutants in the water as nutrients, but in other cases, the sewage environment can inhibit the growth and self-replication of bacteria.
このような環境下ではバクテリアが汚染物質を分解する
ことはできない、このような環境でもバクテリアの分M
a能を有効に発揮させるには、これらバクテリアが成長
し自己増殖するのに不可欠な栄養分(バイオ補助液)を
供給する必要がある。Bacteria cannot decompose pollutants in such an environment, and even in such an environment bacteria's fraction M
In order for these bacteria to effectively exhibit their ability, it is necessary to supply essential nutrients (bio-auxiliary liquid) for the growth and self-replication of these bacteria.
汚染物質の種類により分解するバクテリアが異なるよう
に、バクテリアの種類により成長や自己増殖を助ける栄
養となるバイオ補助液も異なる。従って、ある汚水中の
汚染物質を分解するバクテリアの成長や自己増殖を助け
るには、そのバクテリア固有のバイオ補助液が不可欠と
なり適宜選択して供給する必要がある。Just as different types of bacteria decompose different types of pollutants, different types of bacteria require different bioauxiliary fluids to provide nutrients that help them grow and reproduce. Therefore, in order to support the growth and self-propagation of bacteria that decompose pollutants in certain sewage water, a bioauxiliary solution specific to the bacteria is essential and must be appropriately selected and supplied.
前記商品名D−500の各種バクテリアについて適した
バイオ補助液については、(株式会社)大和研究所が販
売しているw−iooがある。このバイオ補助液はD〜
500に混合されている各種のバクテリアに適した栄養
分が含まれており、これを用いればバイオ補助液の選択
を誤ることがない。As for the bio-auxiliary liquid suitable for various bacteria with the above-mentioned trade name D-500, there is w-ioo sold by Yamato Institute Co., Ltd. This bio-auxiliary liquid is D~
500 contains nutrients suitable for various bacteria, and if you use this, you will not make a mistake in selecting a bio-auxiliary solution.
バイオ補助液であるW−500は、米糠や大豆からアル
カリ発酵法により抽出したフィチン酸(化学名:イノシ
トール・ヘキサ燐酸エステル)やレシチン(化学名;ホ
スファチジルコリン)が含まれている。W-500, a bio-auxiliary liquid, contains phytic acid (chemical name: inositol hexaphosphate) and lecithin (chemical name: phosphatidylcholine) extracted from rice bran and soybeans using an alkaline fermentation method.
フィチン酸やレシチンは、D−100に混合されている
各種バクテリアが戒長し自己増殖するのに必要な栄養が
充分に含まれており、これを使用すればバクテリアが育
つのに不適当な環境下であっても、汚染物質を分解し浄
化作用を促進する。Phytic acid and lecithin contain sufficient nutrients necessary for the various bacteria mixed in D-100 to grow and self-propagate. It decomposes pollutants and promotes purification even under low temperatures.
以上の説明で明らかなように、この水浄化装置は上水、
生活排水や工場排水等の下水、魚介類の養魚場の水はも
とより、汚れた川、沼、湖あるいは海の水の浄化等あら
ゆる水を浄化するときに使用することができる。As is clear from the above explanation, this water purification device is used for clean water,
It can be used to purify all kinds of water, including sewage such as domestic wastewater and industrial wastewater, and water from fish farms, as well as polluted rivers, swamps, lakes, and seawater.
本発明は、以上説明したように構成することにより、安
価で維持費も安く汚水中の有害成分を完全に分解するこ
とのできる水浄化装置を提供することができる。By having the configuration as described above, the present invention can provide a water purification device that is inexpensive and has low maintenance costs and can completely decompose harmful components in wastewater.
第1図は、バクテリアを浮遊させた水槽の水浄化装置を
示した図、
第2図は、水浄化装置を構成する攪拌混合装置の原理を
示した図、
である。
なお、図面に使用されている符号について、1・・回転
体 2・・ケーシング
3・・水面 4・・大気
5・・空気取り入れ口 6−・間隙
9・・出口 10・・空気孔
11・・規制部材
である。Fig. 1 is a diagram showing a water purification device for an aquarium in which bacteria are suspended, and Fig. 2 is a diagram showing the principle of a stirring and mixing device constituting the water purification device. Regarding the symbols used in the drawings, 1. Rotating body 2. Casing 3. Water surface 4. Atmosphere 5. Air intake 6. Gap 9. Outlet 10. Air hole 11. It is a regulating member.
Claims (3)
、細かい空気の気泡と前記バクテリアの成長を促すバイ
オ補助液とを水中に送り込む撹拌混合装置が設けられ、
この撹拌混合装置が駆動されることにより前記空気の気
泡と前記バイオ補助液とが水中に攪拌されることを特徴
とする水浄化装置。(1) A stirring and mixing device is provided in the wastewater in which bacteria that decompose pollutants have been seeded, which feeds fine air bubbles and a bio-auxiliary liquid that promotes the growth of the bacteria into the water;
A water purification device characterized in that the air bubbles and the bio-auxiliary liquid are stirred into water by driving the stirring and mixing device.
のバクテリアの成長を促すバイオ補助液と、細かい空気
の気泡とを水中に送り込む攪拌混合装置が水中に設けら
れ、この撹拌混合装置が駆動されることにより、前記空
気の気泡と共に前記バクテリアと前記バイオ補助液とが
水中に撹拌されることを特徴とする水浄化装置。(2) A stirring and mixing device is installed in the water that feeds into the water a liquid containing bacteria that decomposes pollutants, a bioauxiliary liquid that promotes the growth of this bacteria, and fine air bubbles, and this stirring and mixing device is driven. A water purification device characterized in that the bacteria and the bioauxiliary liquid are stirred into water together with the air bubbles.
棲む水槽に、前記バクテリアの成長を促すバイオ補助液
と細かい空気の気泡とを水中に送り込む撹拌混合装置が
設けられ、この攪拌混合装置が駆動されることにより、
前記バイオ補助液と前記空気の気泡とが水中に撹拌され
ることを特徴とする水浄化装置。(3) A stirring and mixing device is installed in an aquarium inhabited by fish and shellfish in which bacteria that decomposes nitrite have been sown, and which feeds a bio-auxiliary liquid that promotes the growth of the bacteria and fine air bubbles into the water. By being driven,
A water purification device characterized in that the bioauxiliary liquid and the air bubbles are stirred into water.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1202509A JPH0365296A (en) | 1989-08-04 | 1989-08-04 | Water purifying apparatus |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1202509A JPH0365296A (en) | 1989-08-04 | 1989-08-04 | Water purifying apparatus |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH0365296A true JPH0365296A (en) | 1991-03-20 |
Family
ID=16458662
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP1202509A Pending JPH0365296A (en) | 1989-08-04 | 1989-08-04 | Water purifying apparatus |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0365296A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006043586A (en) * | 2004-08-04 | 2006-02-16 | Kurita Water Ind Ltd | Biological treatment accelerator for wastewater and biological treatment method of wastewater using it |
-
1989
- 1989-08-04 JP JP1202509A patent/JPH0365296A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006043586A (en) * | 2004-08-04 | 2006-02-16 | Kurita Water Ind Ltd | Biological treatment accelerator for wastewater and biological treatment method of wastewater using it |
JP4655535B2 (en) * | 2004-08-04 | 2011-03-23 | 栗田工業株式会社 | Wastewater biological treatment method |
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