JPH10286566A - Wastewater purifying system - Google Patents

Wastewater purifying system

Info

Publication number
JPH10286566A
JPH10286566A JP9731097A JP9731097A JPH10286566A JP H10286566 A JPH10286566 A JP H10286566A JP 9731097 A JP9731097 A JP 9731097A JP 9731097 A JP9731097 A JP 9731097A JP H10286566 A JPH10286566 A JP H10286566A
Authority
JP
Japan
Prior art keywords
tank
purification system
filter
sewage purification
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
Application number
JP9731097A
Other languages
Japanese (ja)
Inventor
Masayuki Nakaya
正行 中家
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 JP9731097A priority Critical patent/JPH10286566A/en
Publication of JPH10286566A publication Critical patent/JPH10286566A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Biological Treatment Of Waste Water (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)
  • Treatment Of Biological Wastes In General (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a recycle type private sewage treatment tank for a temporary lavatory in which the generation of offensive odor is eliminated and the purifying efficiency is improved so that the tank is formed smaller. SOLUTION: A wastewater purifying system is provided with a sedimentation separation tank 3, a contact aeration tank 5 and a sedimentation tank 7 set successively in the order, and is so constituted as to purify wastewater while the wastewater is transferred successively into respective tanks and circulate and utilize purified watstewater. In that case, an activated air generator 10 is attached to the wastewater purifying system, and activated air generated from the device is blown into the contact aeration tank 5, and a porous filter medium 20 composed of humus heaped earth as a main material is disposed on the upper section of an activated air blowing opening, and a means for blowing in the activated air while permeating intermediate purified water having passed the sedimentation tank 7 through a pretreatment filter 14 and a bacteria removing filter 15 is provided. Sludge generated in respective tanks is introduced into a microbial degradation tank 21 and degraded completely, and the purified water is reused as flushing water and degraded matters of generated sludge are reused as a fertilizer.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】この発明は、浄化済み汚水を
循環利用する汚水浄化システムであって、浄化処理槽に
活性エアーを吹き込み、中間浄化水を、前処理フィルタ
ー、除菌フィルターを透過させながら活性エアーを吹き
込むことにより、浄化槽から不快臭が発生するのを防止
するとともに、浄化水準と効率を向上させて小型化し、
浄化水を再利用可能にした汚水浄化システムに関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a sewage purification system that circulates and uses purified sewage, wherein active air is blown into a purification treatment tank to pass intermediate purified water through a pretreatment filter and a sterilization filter. By blowing active air, it is possible to prevent the generation of unpleasant odors from the septic tank, and to improve the purification level and efficiency to reduce the size,
The present invention relates to a sewage purification system in which purified water can be reused.

【0002】[0002]

【従来の技術】汚水の微生物分解反応を利用した浄化方
式が実用化されて久しく、最近では仮設便所として使用
されるもののなかには、そこで発生する水を放流しない
で、浄化された水を、水洗用として再利用する「リサイ
クル形」の仮設便所が求められるようになっている。
2. Description of the Related Art Purification systems utilizing the microbial decomposition reaction of sewage have been in practical use for a long time, and recently, among those used as temporary toilets, purified water is used for flushing without discharging the water generated there. There is a growing need for “recyclable” temporary toilets that can be reused as such.

【0003】このような様式の仮設便所は、その設置条
件、使用目的からして出来るだけ小形であり、汚水の浄
化工程で不快臭が発生しないことが必要である。
[0003] The temporary toilets of this type are as small as possible in view of their installation conditions and purpose of use, and it is necessary that unpleasant odors are not generated during the sewage purification process.

【0004】上記ニーズに応えて開発されたものとし
て、排泄物を圧送ポンプで微生物増殖床に圧送し、この
微生物増殖床で分解ガスと水と分解残渣にしてまう方式
のもの、あるいは沈澱分離槽、接触曝気槽および沈澱槽
をコンパクトにまとめ便所と一体とした仮設便所などが
提案されている。
[0004] As a system developed in response to the above needs, a system in which excreta is pumped to a microorganism growth bed by a pressure pump and the decomposition gas, water and decomposition residue are dispersed in the microorganism growth bed, or a sedimentation separation tank In addition, there has been proposed a temporary toilet having a contact aeration tank and a sedimentation tank compactly integrated with a toilet.

【0005】[0005]

【発明が解決しようとする課題】これら従来形のリサイ
クル仮設便所は、浄化過程で不快臭が発生するため、浄
化槽に別途、脱臭手段を設置する必要があるほか小型化
の限界があった。
However, since these conventional types of temporary toilets generate an unpleasant odor during the purification process, it is necessary to install a separate deodorizing means in the septic tank and there is a limit to miniaturization.

【0006】この発明は、上記従来形のリサイクル仮設
便所の問題、即ち、浄化槽での不快臭の発生を絶つため
に、不快臭の原因物質を分解する新規な手段を採用する
ことによって、浄化過程での不快臭の発生を絶つことは
勿論のこと、浄化効率を向上させることによって小型化
をはかり、上水に匹敵する清透で無臭の浄化水を得るこ
とのできる汚水浄化システムを提供しようとするもので
ある。
SUMMARY OF THE INVENTION The present invention is concerned with the problem of the conventional recycle temporary toilet, that is, in order to eliminate the generation of unpleasant odors in the septic tank, a novel means for decomposing the substances causing the unpleasant odors is employed. Not only to eliminate the generation of unpleasant odors, but also to improve the purification efficiency, to reduce the size, and to provide a sewage purification system capable of obtaining clear and odorless purified water comparable to clean water. Is what you do.

【0007】[0007]

【課題を解決するための手段】上記課題を解決するため
に請求項1の発明は、沈澱分離槽と接触曝気槽と沈澱槽
とを順次配設し、上記各槽を汚水が移行する間に該汚水
を浄化し、浄化された水を循環利用する汚水浄化システ
ムにおいて、上記汚水浄化システムに活性エアー発生装
置を付設し、この装置から発生する活性エアーを上記接
触曝気槽内に吹き込むとともに、上記活性エアーの吹き
込み口の上部に腐植質堆積土を主材とする多孔質濾材を
配置し、沈澱槽をパスした中間浄化水を、前処理フィル
ターと除菌フィルターを透過させながら上記活性エアー
を吹き込む手段を設けてなる請求項2の発明は、上記活
性エアー発生装置が、空気通路に対し磁石を、その磁力
(磁束)線が直交するように配置し、上記空気通路の後
段に帯電域と遠赤外線発生繊維を充填した遠赤外線発生
域を連通状に設けてなる構成を採用したものである。
According to a first aspect of the present invention, a sedimentation separation tank, a contact aeration tank and a sedimentation tank are arranged in order, and the wastewater is transferred to each tank while the sediment is transferred. In the sewage purification system that purifies the sewage and circulates and uses the purified water, an active air generator is attached to the sewage purification system, and active air generated from the device is blown into the contact aeration tank. A porous filter medium mainly composed of humic sediment is placed above the active air blow-in port, and the above-mentioned active air is blown into the intermediate purified water that has passed through the sedimentation tank while passing through the pretreatment filter and the sterilization filter. According to a second aspect of the present invention, the active air generating device includes a magnet disposed in the air passage so that a magnetic force (magnetic flux) line thereof is orthogonal to the air passage, and the magnet is disposed at a stage subsequent to the air passage to the charging area. Red The far-infrared radiation zones filled with line generating fiber is obtained by employing the provided comprising configuration in the communication form.

【0008】請求項3の発明は、上記汚水浄化システム
において、前処理フィルターの透過孔が1乃至3μであ
り、除菌フィルターの透過孔が0.1乃至0.0003
μとしたものである。
According to a third aspect of the present invention, in the sewage purification system, the pretreatment filter has a permeation hole of 1 to 3 μm, and the sterilization filter has a permeation hole of 0.1 to 0.0003.
μ.

【0009】請求項4の発明は、上記除菌フィルターの
透過孔が0.001乃至0.0003μとしたものであ
る。
According to a fourth aspect of the present invention, the bactericidal filter has a permeation hole of 0.001 to 0.0003 μm.

【0010】上記の如く構成する各発明によれば、接触
曝気槽、必要ならば沈澱分離槽に、活性エアーが吹き込
まれることによって、臭気発生物質のメタンガス、アン
モニアガスなどが分解される。また、接触曝気槽内に設
置する腐植堆積土を主成分とする多孔質濾材によって汚
水中のフロックが凝集され速やかに汚水が浄化される。
更に、中間浄化水を前フィルターと除菌フィルターとを
通しながら活性エアーを吹き込むことにより、一層完全
な浄化を可能にしている。
According to each of the inventions configured as described above, odor-generating substances such as methane gas and ammonia gas are decomposed by blowing active air into the contact aeration tank and, if necessary, the precipitation separation tank. In addition, the floc in the sewage is aggregated by the porous filter medium mainly composed of humus sediment installed in the contact aeration tank, and the sewage is quickly purified.
Further, by blowing active air while passing the intermediate purified water through the pre-filter and the sterilization filter, more complete purification is possible.

【0011】請求項5の発明は、上記汚水浄化システム
において、沈澱分離槽と接触曝気槽および沈澱槽で発生
する汚泥を微生物分解処理槽に投入し微生物分解する構
成としたものである。
According to a fifth aspect of the present invention, in the above-mentioned sewage purification system, sludge generated in the sedimentation separation tank, the contact aeration tank and the sedimentation tank is charged into a microbial decomposition treatment tank to decompose microorganisms.

【0012】上記の如く構成するこの発明は、沈澱分離
槽と接触曝気槽と沈澱槽で発生する堆積汚泥および浮遊
汚泥が完全に分解される。
In the present invention configured as described above, the sediment sludge and suspended sludge generated in the sedimentation separation tank, the contact aeration tank and the sedimentation tank are completely decomposed.

【0013】請求項6の発明は、上記汚水浄化システム
において、該システムに使用される水洗便器に排泄物を
圧送するポンプを付設してなる構成としたものである。
According to a sixth aspect of the present invention, in the above-mentioned sewage purification system, a pump for pumping excrement is provided to a flush toilet used in the system.

【0014】上記の如く構成することにより、水洗便器
の水位と浄化槽の水位に関係なく、この発明に係る汚水
浄化システムを設置することができる。
[0014] With the above configuration, the sewage purification system according to the present invention can be installed regardless of the water level of the flush toilet and the water level of the septic tank.

【0015】[0015]

【発明の実施の形態】次にこの発明の実施形態を図面を
参照しながら説明する。図1において、配管1によって
送られてきた汚水2は、沈澱分離槽3に流入する。この
沈澱分離槽3は、連続して2基据えられていて、第一沈
澱分離槽3aと第2沈澱分離槽3bとの間の上部には移
流管4aが設けられて第1沈澱分離槽3aでスカムとフ
ロックを概ね除去した汚水は第二沈澱分離槽3bに流入
する。第二沈澱分離槽3bではさらにスカムとフロック
が除去され、オーバーフローした汚水は移流管4bを経
て接触曝気槽5に流入する。
Next, an embodiment of the present invention will be described with reference to the drawings. In FIG. 1, sewage 2 sent by a pipe 1 flows into a sedimentation separation tank 3. Two sedimentation / separation tanks 3 are installed continuously, and an advection pipe 4a is provided at an upper portion between the first sedimentation / separation tank 3a and the second sedimentation / separation tank 3b to provide the first sedimentation / separation tank 3a. The sewage, from which scum and flocs have been substantially removed, flows into the second settling tank 3b. In the second sedimentation separation tank 3b, scum and flocs are further removed, and the overflowed sewage flows into the contact aeration tank 5 via the advection pipe 4b.

【0016】接触曝気槽5は、上記沈澱分離槽3と同様
に2基据えられ第一接触曝気槽5aの下部に設けられた
連通管6aを通過した汚水は第二接触曝気槽5bに流入
し、第二接触曝気槽5bの上部から沈澱槽7に向けて延
びる連通管6bとその先に連設されたフロック沈降促進
筒23を経て沈澱槽7に流入する。
Two contact aeration tanks 5 are provided in the same manner as the sedimentation / separation tank 3, and sewage passing through a communication pipe 6a provided below the first contact aeration tank 5a flows into a second contact aeration tank 5b. Then, it flows into the precipitation tank 7 through the communication pipe 6b extending from the upper part of the second contact aeration tank 5b toward the precipitation tank 7 and the floc sedimentation promoting cylinder 23 connected to the end thereof.

【0017】この沈澱槽7では接触曝気処理された汚水
中のフロックを沈澱させ、フロックを沈澱除去した汚水
は浮遊物除去堰Gを経て溢水路4cを経て中間浄化水槽
8に流入する。中間浄化水槽8に溜積された中間浄化水
はポンプ16aでポンプアップされ送水管17aを経て
前処理フィルター14に送給され、透過されながら活性
エアー発生装置10で発生した活性エアーが送気管13
dを経て吹き込まれ不快臭の原因物質であるメタンガス
やアンモニヤガスなどが分解される。なお、12aは活
性エアーの分配器である。
In the sedimentation tank 7, flocs in the sewage subjected to contact aeration are precipitated, and the sewage from which the flocs have been removed flows into the intermediate purified water tank 8 via the floating material removing weir G, the overflow channel 4c, and the overflow 4c. The intermediate purified water accumulated in the intermediate purified water tank 8 is pumped up by the pump 16a and sent to the pretreatment filter 14 through the water pipe 17a, and the active air generated by the active air generator 10 while passing therethrough is supplied to the air pipe 13
M is blown in through d, and methane gas, ammonia gas, and the like, which are substances causing the unpleasant odor, are decomposed. In addition, 12a is a distributor of active air.

【0018】前処理フィルター14を通過した中間浄化
水は送水管17bを経て除菌フィルター15に送給され
る。活性エアー発生装置10で発生した活性エアーは送
気管13eを経て吹き込まれ、除菌と脱臭が行われ送水
管17cを経て除菌浄化水槽9に流入する。除菌浄化水
槽9に溜積された除菌浄化水はポンプ16bでポンプア
ップされて給水管18を経て水洗便所に供給される。な
お、上記前処理フィルター14と除菌フィルター15に
吹き込まれた後の回収活性エアーは、回収管13fを経
て接触曝気槽5で再利用される。
The intermediate purified water that has passed through the pretreatment filter 14 is sent to the sterilization filter 15 via a water pipe 17b. The active air generated by the active air generator 10 is blown through an air supply pipe 13e to remove bacteria and deodorize, and flows into a sterilization / purification water tank 9 via a water supply pipe 17c. The sterilized purified water accumulated in the sterilized purified water tank 9 is pumped up by the pump 16b and supplied to the flush toilet via the water supply pipe 18. The collected active air blown into the pretreatment filter 14 and the sterilization filter 15 is reused in the contact aeration tank 5 through the collection pipe 13f.

【0019】活性エアー発生装置10で発生した活性エ
アーは、分配器12aで分配され送気管13bを経て接
触曝気槽5の底部に設置した散気管19から吹き込ま
れ、不快臭の原因物質であるメタンガスやアンモニヤガ
スが分解される。また、接触曝気槽5内には腐植堆積土
を主成分とする多孔質濾材20が充填してあり、この多
孔質濾材20は凝集力に富み、汚水がこれを通過する間
に汚水中のフロックが取り除かれる。なお、上記活性エ
アーを沈澱分離槽3に吹き込めば一層の脱臭効果を得る
ことができる。
The active air generated by the active air generator 10 is distributed by a distributor 12a and blown from a diffuser pipe 19 provided at the bottom of the contact aeration tank 5 through an air supply pipe 13b, so that methane gas which is a substance causing unpleasant odor is produced. And ammonia gas are decomposed. The contact aeration tank 5 is filled with a porous filter medium 20 mainly composed of humus sediment. The porous filter medium 20 is rich in cohesive force, and the floc in the sewage flows while the sewage passes therethrough. Is removed. If the active air is blown into the precipitation / separation tank 3, a further deodorizing effect can be obtained.

【0020】21は、微生物分解処理槽で、この微生物
分解処理槽に沈澱分離槽3、接触曝気槽5、沈澱槽7等
で発生するスカムやフロックの沈澱汚泥を適宜の手段で
移送投入し、ここで完全に微生物分解処理するものであ
る。
Reference numeral 21 denotes a microbial decomposition treatment tank. The scum and floc settled sludge generated in the sedimentation separation tank 3, the contact aeration tank 5, the sedimentation tank 7 and the like are transferred to the microbial decomposition treatment tank by appropriate means. Here, the microorganism is completely degraded.

【0021】活性エアー発生装置10は図2に示すよう
に、大気中の塵埃を除去するための除塵フィルター10
1、永久磁石103に囲まれた空気通路102、チャン
バー104、帯電域105、海藻炭を有効成分とする繊
維からなる遠赤外線発生域106、空気溜め108が順
次配置されてなるもので、遠赤外線発生域106には遠
赤外線の発生を促進すためのヒーター107が設けられ
ている。
As shown in FIG. 2, the active air generator 10 has a dust filter 10 for removing dust from the atmosphere.
1. An air passage 102 surrounded by a permanent magnet 103, a chamber 104, a charging area 105, a far-infrared ray generating area 106 made of fibers containing seaweed charcoal as an active ingredient, and an air reservoir 108 are sequentially arranged. The generation area 106 is provided with a heater 107 for promoting generation of far infrared rays.

【0022】ブロワー11(図1)で吸引された大気
は、空気通路102を磁力(磁束)線を直交するかたち
で通過する間にマイナスイオン化され、さらに遠赤外線
発生域106を通過する間に不快臭の原因物質を分解す
る活性の強い空気となる。
The air sucked by the blower 11 (FIG. 1) is negatively ionized while passing through the air passage 102 in a direction perpendicular to the magnetic force (magnetic flux) line, and unpleasant while passing through the far infrared ray generation area 106. It becomes air with strong activity to decompose odor-causing substances.

【0023】前処理フィルター14は図3に示すよう
に、フィルター室141内に1乃至3μの透過孔を有す
るフィルター膜142がジグザグ状に配置されポンプ1
6a(図1)から延びる送水管17aが上流側フィルタ
ー室143に接続され、下流側フィルター室144には
除菌フィルター15に延びる送水管17bが接続されて
いる。上記上流側フィルター室143には膜面に堆積す
るフロックを落とすための超音波振動素子145が設置
されている。なお、146はフィルター膜142を支持
する支柱である。
As shown in FIG. 3, the pre-treatment filter 14 has a filter chamber 142 having a zigzag filter membrane 142 having a transmission hole of 1 to 3 μm in a filter chamber 141.
A water supply pipe 17a extending from 6a (FIG. 1) is connected to the upstream filter chamber 143, and a water supply pipe 17b extending to the sterilization filter 15 is connected to the downstream filter chamber 144. The upstream filter chamber 143 is provided with an ultrasonic vibration element 145 for dropping flocs deposited on the film surface. Reference numeral 146 denotes a support for supporting the filter film 142.

【0024】除菌フィルター15は図4に示すように、
外套管151の中心に0.1乃至0.0003μ、好ま
しくは0.001乃至0.0003μの透孔を有する多
孔質円筒形フィルター153が納められ外套管151は
両端にフランジ155で封緘され、上記円筒形フィルタ
ー153も同時に固定される。外側空間152には前処
理フィルター14から延びる送水管17bが接続され、
上部フランジ155aの中心には活性エアー発生装置1
0から延びる送気管13dが接続され、下部フランジ1
55bの中心には円筒形フィルターを通過し除菌された
浄化水を送る送水管17cが延び除菌浄化水槽9に至
る。
As shown in FIG.
A porous cylindrical filter 153 having a through hole of 0.1 to 0.0003 μ, preferably 0.001 to 0.0003 μ is placed in the center of the mantle tube 151, and the mantle tube 151 is sealed at both ends with flanges 155. The cylindrical filter 153 is also fixed at the same time. A water pipe 17b extending from the pretreatment filter 14 is connected to the outer space 152,
The active air generator 1 is located at the center of the upper flange 155a.
0 is connected to the air supply pipe 13d extending from the lower flange 1
At the center of 55b, a water supply pipe 17c for passing purified water that has been sterilized through a cylindrical filter extends and reaches the sterilized purified water tank 9.

【0025】微生物分解処理槽21は図5に示すよう
に、架台21aの内寄りに支持枠21bが設けられ、こ
の支持枠21bに円筒状の外側槽21cが支持され、そ
の左右の中央から偏心した位置に水平方向に貫通孔21
dが開けられて、この貫通孔21dの外側には軸受け2
1eが設けられている。
As shown in FIG. 5, the microbial decomposition treatment tank 21 is provided with a support frame 21b provided on the inner side of a gantry 21a, and a cylindrical outer tank 21c is supported on the support frame 21b. Through hole 21 in the horizontal direction
d is opened, and the bearing 2 is provided outside the through hole 21d.
1e is provided.

【0026】軸受け21eには中空軸21fが貫通して
いて、その中央部分に隔壁21gが設けられ、その両側
に汚泥の流入口21hと分解ガス排出口21i設けられ
ている。この中空軸21fにはパンチングネット21j
を筒状に形成し、内面に攪拌翼21kを付設した内側槽
21nが回転可能に支持されている。なお、21oは内
側槽21n内を微生物分解に適した状態に保湿するため
の散水パイプ、21pは水溜め枡、21qは保温するた
めのヒーターである。
A hollow shaft 21f penetrates the bearing 21e, and a partition 21g is provided at a central portion thereof. An inflow port 21h for sludge and a decomposition gas discharge port 21i are provided on both sides thereof. The hollow shaft 21f has a punching net 21j.
Is formed in a cylindrical shape, and an inner tank 21n provided with a stirring blade 21k on the inner surface is rotatably supported. Reference numeral 21o denotes a watering pipe for moisturizing the inside of the inner tank 21n in a state suitable for microbial decomposition, 21p a water reservoir, and 21q a heater for keeping the temperature.

【0027】微生物分解槽21に投入された汚泥は、内
側槽21nの微生物の増殖・培養床と混ぜられ微生物分
解により分解ガスと水と分解残渣とになる。
The sludge fed into the microbial decomposition tank 21 is mixed with the microorganism growth / culture bed in the inner tank 21n to be decomposed into decomposed gas, water and decomposition residues by microbial decomposition.

【0028】次に、下記仕様のテストプラントを製作
し、この発明の効果を確認した。 仮設水洗便所からの汚水流入量:0.0125m3 /hr 第1沈澱分離槽の内容積 :0.6m3 第2沈澱分離槽の内容積 :0.2m3 第1接触曝気槽の内容積 :0.6m3 同 多孔質濾材の投入量 :0.4m3 同 活性エアー吹き込み量 :1440m3 /hr 第2接触曝気槽の内容積 :0.3m3 同 多孔質濾材の投入量 :0.24m3 同 活性エアー吹き込み量 : 960m3 /hr 沈澱槽の内容積 :0.2m3 汚水のシステム内滞留時間 :120hr 多孔質濾材=腐植堆積土(黒ボク土)+珪石+バインダー (商品名:タッチストーン) 前処理フィルター膜の透過孔 :2μ 除菌フィルターの透過孔 :0.0002μ 活性エアー発生装置 磁石(外径・内径・長さ)=80φ×40φ×250mm 遠赤外線発生物・・・海草炭含有繊維、遠赤外線の波長=4〜14μ ブロワーの空気排出量 ・・・0.04m3 /min ブロワーの排出空気圧力 ・・・0.12kgf/cm2 ヒーター温度 40℃。
Next, a test plant having the following specifications was manufactured, and the effects of the present invention were confirmed. Sewage inflow from temporary flush toilet: 0.0125 m 3 / hr Inner volume of first sedimentation / separation tank: 0.6 m 3 Inner volume of second sedimentation / separation tank: 0.2 m 3 Inner volume of first contact aeration tank: 0.6 m 3 same porous filter material input amount: 0.4 m 3 same active air blowing amount: 1440 m 3 / hr inner volume of second contact aeration tank: 0.3 m 3 same porous filter material input amount: 0.24 m 3 Same active air blowing amount: 960 m 3 / hr Inner volume of sedimentation tank: 0.2 m 3 Retention time of sewage in the system: 120 hr Porous filter media = humus sedimentary soil (kuroboku soil) + silica stone + binder (Product name: Touch) Stone) Permeation hole of pretreatment filter membrane: 2μ Permeation hole of sterilization filter: 0.0002μ Active air generator Magnet (outer diameter / inner diameter / length) = 80φ × 40φ × 250mm Far-infrared ray generator ・ ・ ・ Contains seaweed charcoal Fiber, far-infrared wavelength = 4 to 14μ Blower air discharge: 0.04 m 3 / min Blower discharge air pressure: 0.12 kgf / cm 2 Heater temperature: 40 ° C.

【0029】上記仕様のテストプラントでランニングテ
ストを行ったところ、下記の結果を得た。 不快臭 ・・・なし 水の色度 ・・・10以下 大腸菌群 ・・・検出されず 一般細菌 ・・・検出されず BOD ・・・5ppm 以下 SS ・・・5ppm 以下 PH ・・・5.8〜8.6
When a running test was performed in a test plant having the above specifications, the following results were obtained. Unpleasant odor… None Water chromaticity… 10 or less Escherichia coli group… Not detected General bacteria… Not detected BOD… 5ppm or less SS… 5ppm or less PH… 5.8 ~ 8.6

【0030】[0030]

【発明の効果】以上の説明から明らかなように、この発
明によれば汚水浄化システムを構成する各槽から不快臭
の発生がなく、また、浄化効率が向上することによつ
て、全体の小型化を可能にした。
As is clear from the above description, according to the present invention, no unpleasant odor is generated from each tank constituting the sewage purification system, and the purification efficiency is improved. Made possible.

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

【図1】この発明の実施形態に係るシステムの構成図FIG. 1 is a configuration diagram of a system according to an embodiment of the present invention.

【図2】同活性エアー発生装置の構成図FIG. 2 is a configuration diagram of the active air generator.

【図3】前処理フィルターの構成図FIG. 3 is a configuration diagram of a pre-processing filter.

【図4】除菌フィルターの構成図FIG. 4 is a configuration diagram of a sterilization filter.

【図5】微生物分解槽の構成図FIG. 5 is a configuration diagram of a microorganism decomposition tank.

【符号の説明】[Explanation of symbols]

1 配管 2 汚水 3 沈澱分離槽 4a,4b 移流管 5 接触曝気槽 6a,6b 連通管 7 沈澱槽 8 浄化水槽 9 除菌済水槽 10 活性エアー発生装置 11 ブロワー 12a,12b 分配器 13a,13b,13c,13d,13e,13f,送
気管 14 前処理フィルター 15 除菌フィルター 16a,16b ポンプ 17a,17b,17c 送水管 18 給水管 19 散気管 20 多孔質濾材 21 微生物分解処理槽 22 堆積汚泥搬送路 23 フロック沈降促進筒
Reference Signs List 1 pipe 2 sewage 3 sedimentation separation tank 4a, 4b advection pipe 5 contact aeration tank 6a, 6b communication pipe 7 sedimentation tank 8 purified water tank 9 sanitized water tank 10 active air generator 11 blower 12a, 12b distributor 13a, 13b, 13c , 13d, 13e, 13f, air supply pipe 14 pretreatment filter 15 sterilization filter 16a, 16b pump 17a, 17b, 17c water supply pipe 18 water supply pipe 19 diffuser pipe 20 porous filter medium 21 microbial decomposition treatment tank 22 sedimentary sludge transport path 23 floc Settling promotion cylinder

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 沈澱分離槽と接触曝気槽と沈澱槽とを順
次配設し、上記各槽を汚水が移行する間に該汚水を浄化
し、浄化された水を循環利用する汚水浄化システムにお
いて、上記汚水浄化システムに活性エアー発生装置を付
設し、この装置から発生する活性エアーを上記接触曝気
槽内に吹き込むとともに、上記活性エアーの吹き込み口
の上部に腐植質堆積土を主材とする多孔質濾材を配置
し、沈澱槽をパスした中間浄化水を、前処理フィルター
と除菌フィルターを透過させながら上記活性エアーを吹
き込む手段を設けてなることを特徴とする汚水浄化シス
テム。
1. A sewage purification system in which a sedimentation separation tank, a contact aeration tank, and a sedimentation tank are sequentially arranged, the sewage is purified while the sewage is transferred to each of the tanks, and the purified water is circulated and used. An active air generator is attached to the sewage purification system, and active air generated from the system is blown into the contact aeration tank, and a porous material mainly composed of humic sediment is provided above the active air blowing port. A wastewater purification system, comprising means for blowing the active air while passing through a pretreatment filter and a sterilization filter, through which the intermediate purification water having passed through the sedimentation tank is disposed with a quality filter medium.
【請求項2】 上記活性エアー発生装置が、空気通路に
対し磁石を、その磁力(磁束)線が直交するように配置
し、上記空気通路の後段に帯電域と遠赤外線発生繊維を
充填した遠赤外線発生域を連通状に設けてなる請求項1
に記載の汚水浄化システム。
2. The active air generating device according to claim 1, wherein a magnet is arranged in the air passage so that a magnetic force (magnetic flux) line is orthogonal to the air passage, and a charging region and a far infrared ray generating fiber are filled in a latter stage of the air passage. 2. The infrared ray generating area is provided in a communicating manner.
A sewage purification system according to item 1.
【請求項3】 上記汚水浄化システムにおいて、前処理
フィルターの透過孔が1乃至3μであり、除菌フィルタ
ーの透過孔が0.1乃至0.0003μである請求項1
または2のいずれかに記載の汚水浄化システム。
3. The sewage purification system according to claim 1, wherein the permeation hole of the pretreatment filter is 1 to 3 μm, and the permeation hole of the sterilization filter is 0.1 to 0.0003 μm.
Or the sewage purification system according to any one of 2.
【請求項4】 上記除菌フィルターの透過孔が0.00
1乃至0.0003μである請求項1乃至3のいずれか
に記載の汚水浄化システム。
4. The bactericidal filter according to claim 1, wherein a permeation hole of said filter is 0.00.
The sewage purification system according to any one of claims 1 to 3, wherein the sewage purification system has a particle size of 1 to 0.0003 µm.
【請求項5】 上記汚水浄化システムにおいて、沈澱分
離槽と接触曝気槽および沈澱槽で発生する汚泥を微生物
分解処理槽に投入し微生物分解することを特徴とする請
求項1乃至4のいずれかに記載の汚水浄化システム。
5. The sewage purification system according to claim 1, wherein sludge generated in the sedimentation separation tank, the contact aeration tank and the sedimentation tank is charged into a microbial decomposition treatment tank for microbial decomposition. A sewage purification system as described.
【請求項6】 上記汚水浄化システムにおいて、該シス
テムに使用される水洗便器に排泄物を圧送するポンプを
付設してなることを特徴とする請求項1乃至5のいずれ
かに記載の汚水浄化システム。
6. The sewage purification system according to claim 1, wherein the sewage purification system further comprises a pump for pumping excrement into a flush toilet used in the system. .
JP9731097A 1997-04-15 1997-04-15 Wastewater purifying system Pending JPH10286566A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9731097A JPH10286566A (en) 1997-04-15 1997-04-15 Wastewater purifying system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9731097A JPH10286566A (en) 1997-04-15 1997-04-15 Wastewater purifying system

Publications (1)

Publication Number Publication Date
JPH10286566A true JPH10286566A (en) 1998-10-27

Family

ID=14188926

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9731097A Pending JPH10286566A (en) 1997-04-15 1997-04-15 Wastewater purifying system

Country Status (1)

Country Link
JP (1) JPH10286566A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1078903A2 (en) 1999-08-23 2001-02-28 Suiko Kinzoku Kabushiki Kaisha Human waste treatment system
JP2001321798A (en) * 2000-05-18 2001-11-20 Enzyme Kk Method and apparatus for treating organic thick wastewater
JP2008006388A (en) * 2006-06-30 2008-01-17 Kankyo Protect:Kk Sewage cleansing system
WO2009017917A1 (en) * 2007-07-27 2009-02-05 Sanchez Robert M Waste water filtering system
WO2010119737A1 (en) * 2009-04-16 2010-10-21 株式会社 地球環境秀明 Recirculation toilet based on complex fermentation method
JP5116888B1 (en) * 2012-04-17 2013-01-09 誠二 高松 Non-water-supplying circulating flush toilet system and container toilet containing this system
US20140299058A1 (en) * 2010-12-27 2014-10-09 Sharp Kabushiki Kaisha Deposition device, and collection device

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1078903A2 (en) 1999-08-23 2001-02-28 Suiko Kinzoku Kabushiki Kaisha Human waste treatment system
US6258594B1 (en) 1999-08-23 2001-07-10 Suiko Kinzoku Kabushiki Kaisha Human waste treatment system
EP1078903A3 (en) * 1999-08-23 2002-07-03 Suiko Kinzoku Kabushiki Kaisha Human waste treatment system
JP2001321798A (en) * 2000-05-18 2001-11-20 Enzyme Kk Method and apparatus for treating organic thick wastewater
JP4540180B2 (en) * 2000-05-18 2010-09-08 エンザイム株式会社 Method and apparatus for treating organic concentrated wastewater
JP2008006388A (en) * 2006-06-30 2008-01-17 Kankyo Protect:Kk Sewage cleansing system
WO2009017917A1 (en) * 2007-07-27 2009-02-05 Sanchez Robert M Waste water filtering system
WO2010119737A1 (en) * 2009-04-16 2010-10-21 株式会社 地球環境秀明 Recirculation toilet based on complex fermentation method
US20140299058A1 (en) * 2010-12-27 2014-10-09 Sharp Kabushiki Kaisha Deposition device, and collection device
US9365927B2 (en) * 2010-12-27 2016-06-14 Sharp Kabushiki Kaisha Deposition method and collection method
JP5116888B1 (en) * 2012-04-17 2013-01-09 誠二 高松 Non-water-supplying circulating flush toilet system and container toilet containing this system

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