JP2000170227A - Undraining type flush toilet system - Google Patents

Undraining type flush toilet system

Info

Publication number
JP2000170227A
JP2000170227A JP10349688A JP34968898A JP2000170227A JP 2000170227 A JP2000170227 A JP 2000170227A JP 10349688 A JP10349688 A JP 10349688A JP 34968898 A JP34968898 A JP 34968898A JP 2000170227 A JP2000170227 A JP 2000170227A
Authority
JP
Japan
Prior art keywords
water
tank
treated
aeration
flush toilet
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
JP10349688A
Other languages
Japanese (ja)
Inventor
Shigeo Kawasaki
重雄 川崎
Takashi Tateno
孝 立野
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.)
ASAHI KOMUTEN KK
KAWAKURIIN KK
Original Assignee
ASAHI KOMUTEN KK
KAWAKURIIN KK
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 ASAHI KOMUTEN KK, KAWAKURIIN KK filed Critical ASAHI KOMUTEN KK
Priority to JP10349688A priority Critical patent/JP2000170227A/en
Publication of JP2000170227A publication Critical patent/JP2000170227A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To improve a function by treating a treating object from a flush toilet bowl by an aeration tank, a salinity treating tank and an ozone sterilization treating tank, and resupplying treated water to the flush toilet bowl. SOLUTION: An anaerobic precipitation tank 2 has a return piping 21 for supplying aeration-treated water B, C to anaerobically treat toilet distribution water (a) and the aeration-treated water (b) (B, C). Next, the treated water A is sent to a first aeration tank 3 and a second aeration tank 4 by an overflow to be aerobically treated by receiving aeration supply from a blow 31. Next, a salinity treating tank part 5 reduces salinity of the aeration-treated water C from the tank 4 by a halophilic microorganism. A sterilization treating part 6 is provided with an ozone generator 61 to supply ozone G from a lower opening part of spiral piping 63 arranged in a treating tank 62 to be sterilized. Treated circulating water E treated by the treating part 6 is supplied as toilet water by a pump 71 and piping 72 of a water supply part 7. Thus, since, an increase in the salinity concentration can be prevented, an undraining type flush toilet system can be put to practical use.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、水洗トイレの廃水を処
理し、処理済み水を再度水洗トイレに使用するという循
環処理を行う無排水式水洗トイレシステムに関するもの
である。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a non-drainable flush toilet system for treating waste water from flush toilets and performing a circulation treatment of reusing the treated water for flush toilets again.

【0002】[0002]

【従来の技術】トイレ廃水の処理済み水を再度利用する
無排水循環方式の水洗トイレシステム自体は、公知であ
る。その基本的構成は、特開平5−230858号に示
す通り接触曝気槽での微生物よる汚物の分解と、分解処
理後の滅菌処理を行い、処理済み水を水洗トイレ用とし
て再度使用することを繰り返すものである。
2. Description of the Related Art A flush toilet system of a non-drainage circulation type which reuses treated water of toilet wastewater is known. Its basic structure is as described in Japanese Patent Application Laid-Open No. 5-230858, in which the decomposition of dirt by microorganisms in a contact aeration tank, the sterilization treatment after the decomposition treatment, and the reuse of the treated water for flush toilets are repeated. Things.

【0003】[0003]

【発明が解決しようとする課題】前記の処理システムに
於いて、汚物の分解効率を高めるために、接触濾材の改
良や、処理期間の長期化等が提案されているが、循環処
理を繰り返していると、循環処理水内の塩分濃度が自然
に高まってしまい、配管等の金属部材は、直ぐに腐食し
てしまい、単に汚物分解処理並びに滅菌処理のみでは、
長期の循環処理は困難である。
In the above-mentioned treatment system, improvement of the contact filter medium and prolongation of the treatment period have been proposed in order to increase the efficiency of decomposing wastes. In such a case, the salt concentration in the circulating treatment water naturally increases, and the metal members such as pipes are immediately corroded.
Long-term circulation treatment is difficult.

【0004】また滅菌処理についても、オゾン気体を単
に処理対象水に混入させたとしても、充分な殺菌がなさ
れるためには、多量のオゾン気体供給が必要となり、而
も滅菌反応(酸化反応)に使用されない余剰オゾンは、
そのまま大気に放出すると不都合であるので、大気放出
箇所にフィルターなどの設備が必要となる。
In sterilization, even if ozone gas is simply mixed into the water to be treated, a large amount of ozone gas must be supplied in order to perform sufficient sterilization, and a sterilization reaction (oxidation reaction) is also required. Surplus ozone not used for
Since it is inconvenient to release the gas to the atmosphere as it is, equipment such as a filter is required at the location where the air is released.

【0005】そこで本発明は、塩分処理問題解決手段
と、オゾンによる効率的な滅菌処理手段を提案したもの
である。
Therefore, the present invention proposes a means for solving the problem of salt treatment and an efficient sterilization treatment using ozone.

【0006】[0006]

【課題を解決する手段】本発明に係る無排水式水洗トイ
レシステムは、水洗便器と、水洗便器からの処理対象物
を受け入れて好気処理を行う曝気槽部と、曝気処理済み
水を好塩性微生物によって循環する処理水の塩分濃度を
低下させる塩分処理槽部と、塩分処理済みの循環水のオ
ゾン殺菌を行う滅菌処理槽部と、滅菌処理済み水の供給
ポンプを有する用水供給部とを備えたことを特徴とする
ものである。
A non-drainable flush toilet system according to the present invention comprises a flush toilet, an aeration tank section for receiving an object to be treated from the flush toilet and performing aerobic treatment, and using aeration-treated water for salt-washing. A salt treatment tank for reducing the salt concentration of the treated water circulated by the bacterium, a sterilization treatment tank for performing ozone sterilization of the salt-treated circulating water, and a service water supply unit having a supply pump for the sterilized water. It is characterized by having.

【0007】また特に前記水洗トイレシステムにおい
て、滅菌処理槽部を、処理槽内に、螺旋状配管を内置
し、螺旋状配管の下方開口部からオゾン含有空気または
オゾン気体を小泡状に供給して処理対象水をエアーリフ
ト作用で配管を通過させて処理対象水とオゾンとの接触
を行うようにしたことを特徴とするものである。
In the flush toilet system, in particular, a sterilizing tank is provided with a spiral pipe in the processing tank, and ozone-containing air or ozone gas is supplied in small bubbles from the lower opening of the spiral pipe. Thus, the water to be treated is passed through a pipe by an air lift action to contact the water to be treated with ozone.

【0008】従って曝気槽部の好気処理により有機物の
分解並びに脱窒処理を行い、塩分処理槽部において、好
塩性微生物の作用によって、循環処理水の塩分濃度を低
下させ、オゾン殺菌で滅菌処理を行い再使用可能な清浄
水とし、再度トイレ用水として使用するものである。
Accordingly, organic matter is decomposed and denitrified by aerobic treatment in the aeration tank. In the salt treatment tank, the salt concentration of the circulating treated water is reduced by the action of halophilic microorganisms and sterilized by ozone sterilization. The treated water is used as clean water that can be reused and reused as toilet water.

【0009】またオゾンによる滅菌処理に際しては、処
理槽内に配置した螺旋配管内にオゾン気体を小泡状に供
給すると、泡体は配管内を上昇するが、同時にエアーリ
フト作用によって周囲の処理対象水も配管内を上昇させ
る。従ってオゾン気体の供給は、処理対象水を配管内に
順次送り込むことになり、配管内通過時間処理対象水と
オゾン気体は、接触することになり、効率的なオゾン殺
菌が実現するものである。
In the sterilization treatment with ozone, when ozone gas is supplied in the form of small bubbles into a spiral pipe arranged in a processing tank, the foam rises in the pipe, but at the same time, the surrounding objects to be treated are lifted by an air lift action. Water also rises in the piping. Therefore, the supply of the ozone gas sequentially feeds the water to be treated into the pipe, and the water to be treated and the ozone gas come into contact with each other in the passage time in the pipe, thereby achieving efficient ozone sterilization.

【0010】[0010]

【実施の形態】次に本発明の実施形態について説明す
る。実施形態に示したシステムは、水洗便器1と、嫌気
沈殿槽部2と、第一曝気槽部3と、第二曝気槽部4と、
塩分処理槽部5と、滅菌処理部6と、用水供給部7とで
構成される。
Next, an embodiment of the present invention will be described. The system shown in the embodiment includes a flush toilet 1, an anaerobic sedimentation tank unit 2, a first aeration tank unit 3, a second aeration tank unit 4,
It comprises a salt treatment tank section 5, a sterilization section 6, and a water supply section 7.

【0011】水洗便器1は、通常のものと同一であり、
貯水槽11を備えているものである。嫌気沈殿槽部2
は、一次的な処理対象水の嫌気処理を行うもので、処理
対象水は、トイレ排水(汚物と排水用水)aと、曝気処
理済み水b(B+C)であり、曝気処理済み水B、Cの
供給を受ける戻し配管21を備えているものである。尚
戻し配管21は、曝気を利用したエアーリフト配管とし
ても良い。そして嫌気処理後の処理水Aは、オーバーフ
ローで次の第一曝気槽部3に送られるものである。
The flush toilet 1 is the same as a normal one.
The water tank 11 is provided. Anaerobic sedimentation tank 2
Performs the primary anaerobic treatment of the water to be treated. The water to be treated is toilet wastewater (filtration and wastewater) a and aerated water b (B + C), and aerated water B and C Is provided with a return pipe 21 for receiving the supply of water. The return pipe 21 may be an air lift pipe using aeration. The treated water A after the anaerobic treatment is sent to the next first aeration tank unit 3 by overflow.

【0012】第一曝気槽部3及び第二曝気槽部4は、ブ
ロー31からの曝気供給を受け、好気処理を行うもの
で、適宜な濾材32、41を内置したもので、濾材32
は、牡蠣殻と、ゼオライトであり、第二曝気槽部4の濾
材41は、牡蠣殻と木炭である。第一曝気処理槽部3で
の処理済み水Bは、次の第二曝気槽部4に送られ(オー
バーフロー)、再度曝気処理がなされるものである。
The first aeration tank unit 3 and the second aeration tank unit 4 receive aeration from the blow 31 and perform aerobic treatment. The first aeration tank unit 3 and the second aeration tank unit 4 are provided with appropriate filter media 32 and 41 therein.
Is oyster shell and zeolite, and the filter medium 41 of the second aeration tank unit 4 is oyster shell and charcoal. The treated water B in the first aeration tank section 3 is sent to the next second aeration tank section 4 (overflow), where the aeration processing is performed again.

【0013】塩分処理槽部5は、第二曝気槽部3からの
曝気処理済み水Cを受け入れる槽内に、好塩性微生物
(バイオマイトと称して市販されている)を付着させた
濾材(石炭)51を沈下配置したものである。
The salt-treatment tank unit 5 has a filter medium (having a halophilic microorganism (commercially called biomite)) attached to a tank for receiving the aerated water C from the second aeration tank unit 3. (Coal) 51 is settled down.

【0014】滅菌処理部6は、別置オゾン発生器61を
設け、処理槽62内に、螺旋状配管63を内置し、螺旋
状配管63の下方開口部からオゾン含有空気またはオゾ
ン気体Gを小泡状に供給するようにしたものである。
The sterilization section 6 is provided with a separate ozone generator 61, a spiral pipe 63 is provided in a processing tank 62, and ozone-containing air or ozone gas G is reduced from the lower opening of the spiral pipe 63. It is supplied in the form of foam.

【0015】用水供給部7は、滅菌処理部6で処理した
処理循環水Eをトイレ用水として使用するための供給ポ
ンプ71と、配管72とを備えたものである。
The water supply section 7 is provided with a supply pump 71 for using the treated circulating water E treated by the sterilization section 6 as toilet water, and a pipe 72.

【0016】次に前記各部での処理について説明する。
最初に第一曝気処理槽部3では、ブロー31からの空気
が供給されて、濾材32に付着している好気性バクテリ
アによって処理水Aの汚れを分解するものであるが、曝
気処理においては、通常有機物処理のバクテリアが優勢
であり、第一曝気槽部3では、有機物分解がなされる。
更にアンモニアの形で存在している窒素は、接触曝気槽
に移ると亜硝酸性窒素から硝酸性窒素に変わり、槽内処
理対象水が酸性となるので、牡蠣殻のような石灰質の濾
材をいれておくことで中性化する。
Next, the processing in each section will be described.
First, in the first aeration tank 3, air from the blow 31 is supplied to decompose the stain of the treated water A by aerobic bacteria attached to the filter medium 32. In the aeration, Usually, bacteria treated with organic substances are dominant, and organic substances are decomposed in the first aeration tank unit 3.
Furthermore, nitrogen present in the form of ammonia is converted from nitrite nitrogen to nitrate nitrogen when transferred to the contact aeration tank, and the water to be treated in the tank becomes acidic, so add a calcareous filter medium such as oyster shell. Be neutralized by keeping.

【0017】また第二曝気槽部4では、第一曝気槽部3
での曝気処理済み水Bが大部分の有機質が分解処理され
ているので、第二曝気槽部では、主として硝化バクテリ
アによる脱窒処理(窒素は、窒素ガスとして放出され
る)がなされると共に、残存有機物の完全分解処理を行
う。
In the second aeration tank section 4, the first aeration tank section 3
In the second aeration tank, denitrification treatment (nitrogen is released as nitrogen gas) is mainly performed in the second aeration tank because most of the organic matter is decomposed in the water B that has been subjected to the aeration treatment in the above. Completely decompose the remaining organic matter.

【0018】そこで嫌気槽沈殿槽部2での処理である
が、脱窒菌は、通性嫌気性菌で、酸素が存在する場合に
は呼吸し、存在しないと発酵によってエネルギーを確保
して繁殖するもので、好気嫌気に関わらず増殖し、酸素
が存在しないと硝酸性窒素や、亜硝酸性窒素を分解して
酸素を得ることになるので、硝酸性窒素や亜硝酸性窒素
を含む第一及び第二曝気槽部3,4の処理水B、Cを嫌
気沈殿槽部2に戻してやると脱窒処理がなされる。
Therefore, in the treatment in the anaerobic tank settling tank section 2, the denitrifying bacteria are facultative anaerobic bacteria, breathe when oxygen is present, and when they are not present, secure energy by fermentation and reproduce. It grows regardless of aerobic or anaerobic, and if there is no oxygen, it will decompose nitrate nitrogen and nitrite nitrogen to obtain oxygen, so the first containing nitrate nitrogen and nitrite nitrogen When the treated waters B and C in the second aeration tank sections 3 and 4 are returned to the anaerobic precipitation tank section 2, denitrification processing is performed.

【0019】有機物の分解並びに脱窒処理がなされた処
理済み水Cは、次の塩分処理槽部5に送られ、好塩性微
生物の作用によって処理済みの循環水D内の塩分を減少
させる。塩分減少の正確な作用原因は不明であるが、好
塩性微生物がその増殖によって塩分を取り込み、塩分処
理槽内の残留塩分は増加するが、循環水の塩分濃度の上
昇は無いようにしていると推察される。そして塩分処理
済みの循環水Dは、次の滅菌処理部6に送られる。
The treated water C which has undergone the decomposition and denitrification treatment of organic matter is sent to the next salt treatment tank section 5 to reduce the salt content in the treated circulating water D by the action of halophilic microorganisms. Although the exact cause of the salinity reduction is unknown, the halophilic microorganisms take in the salt due to their growth and the residual salinity in the salinity treatment tank increases, but there is no increase in the salinity of the circulating water. It is inferred. Then, the circulating water D that has been subjected to the salt content is sent to the next sterilizing section 6.

【0020】滅菌処理部6では、螺旋配管63内にオゾ
ン気体Gを小泡状に供給すると、泡体は配管63内を上
昇するが、同時にエアーリフト作用によって周囲の処理
対象水(塩分処理済み循環水)Dも配管内を上昇させ
る。従ってオゾン気体Gの連続供給によって、処理対象
水Dとオゾン気体Gは、配管63通過途中の間互いに接
触することになり、効率的なオゾン殺菌が実現すること
になる。
In the sterilization section 6, when the ozone gas G is supplied into the spiral pipe 63 in the form of small bubbles, the foam rises in the pipe 63, but at the same time, the surrounding water to be treated (salt-treated) The circulating water D also rises in the pipe. Therefore, by the continuous supply of the ozone gas G, the water D to be treated and the ozone gas G come into contact with each other during the passage through the pipe 63, and efficient ozone sterilization is realized.

【0021】そして滅菌処理水Eは清浄水であるので、
再度トイレ用水として使用できるものであり、完全無排
水の水洗トイレシステムが実現するものである。
Since the sterilized water E is clean water,
It can be used again as toilet water, and a completely non-drained flush toilet system is realized.

【0022】尚本発明は前記実施例に限定されるもので
は無く、嫌気沈殿槽が無く、脱窒が不充分であっても、
トイレ用水として使用できる範囲であれば、石灰質によ
る中和で十分である。また必要に応じて各曝気槽に逆洗
機構を配置しても良い。更に適宜長期間使用した後に
は、必要に応じて各槽の沈殿汚泥のくみ取り処理を行
う。
It should be noted that the present invention is not limited to the above-described embodiment, and even if there is no anaerobic sedimentation tank and denitrification is insufficient,
Neutralization with calcareous is sufficient as long as it can be used as toilet water. Further, a backwashing mechanism may be arranged in each aeration tank as needed. Furthermore, after using it for a long period of time, the sludge is removed from each tank as needed.

【0023】[0023]

【発明の効果】以上のように本発明は、無排水式水洗ト
イレシステムに、 曝気処理済み水の好塩性微生物によ
る循環水の塩分処理を行う塩分処理槽部を介在させたも
ので、無排水とするために排水を処理して再使用すると
いう循環方式の採用に伴う塩分濃度上昇という課題を解
決し、無排水式水洗トイレシステムの実用化を確実にし
たものである。
As described above, the present invention relates to a non-drainable flush toilet system in which a salt treatment tank section for performing salt treatment of circulating water by a halophilic microorganism of aerated water is provided. This solves the problem of increased salt concentration associated with the adoption of a circulation system that treats and reuses wastewater to make it into wastewater, and has ensured the practical use of a non-drainable flush toilet system.

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

【図1】本発明の実施形態の簡便な全体システム図。FIG. 1 is a simple overall system diagram of an embodiment of the present invention.

【図2】同滅菌処理部の説明図。FIG. 2 is an explanatory diagram of the sterilization processing unit.

【符号の説明】[Explanation of symbols]

1 水洗便器 11 貯水槽 2 嫌気沈殿槽部 21 戻し配管 3 第一曝気槽部 31 ブロー 32 濾材 4 第二曝気槽部 41 濾材 5 塩分処理槽部 51 濾材 6 滅菌処理部 61 オゾン発生器 62 処理槽 63 螺旋状配管 7 用水供給部 71 供給ポンプ 72 配管 Reference Signs List 1 flush toilet 11 water storage tank 2 anaerobic sedimentation tank part 21 return pipe 3 first aeration tank part 31 blow 32 filter medium 4 second aeration tank part 41 filter medium 5 salt treatment tank part 51 filter medium 6 sterilization treatment part 61 ozone generator 62 treatment tank 63 Spiral pipe 7 Water supply unit 71 Supply pump 72 Pipe

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 1/50 550 C02F 1/50 550C 560 560H 3/34 3/34 Z 101 101D ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C02F 1/50 550 C02F 1/50 550C 560 560H 3/34 3/34 Z 101 101D

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 水洗便器と、水洗便器からの処理対象物
を受け入れて好気処理を行う曝気槽部と、曝気処理済み
水を受け入れて好塩性微生物による循環処理水の塩分濃
度を低下させる塩分処理槽部と、塩分処理済みの循環水
の殺菌を行う滅菌処理槽部と、滅菌処理済み循環水を水
洗便器に供給する供給ポンプを有する用水供給部とを備
えたことを特徴とする無排水式水洗トイレシステム。
1. A flush toilet, an aeration tank for receiving an object to be treated from the flush toilet and performing aerobic treatment, and accepting aerated water to reduce a salt concentration of circulating treatment water by halophilic microorganisms. A salinity treatment tank unit, a sterilization treatment tank unit for sterilizing circulating water subjected to salt treatment, and a service water supply unit having a supply pump for supplying sterilized circulating water to a flush toilet. Drain type flush toilet system.
【請求項2】 処理槽内に、螺旋状配管を内置し、螺旋
状配管の下方開口部からオゾン含有空気またはオゾン気
体を小泡状に供給して処理対象水をエアーリフト作用で
配管を通過させて処理対象水とオゾンとの接触を行って
なる滅菌処理槽部を備えた請求項1記載の無排水式水洗
トイレシステム。
2. A spiral pipe is provided in the treatment tank, and ozone-containing air or ozone gas is supplied in small bubbles from the lower opening of the spiral pipe, and the water to be treated passes through the pipe by an air lift action. The non-drainable flush toilet system according to claim 1, further comprising a sterilization treatment tank section configured to contact the water to be treated with ozone.
JP10349688A 1998-12-09 1998-12-09 Undraining type flush toilet system Pending JP2000170227A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10349688A JP2000170227A (en) 1998-12-09 1998-12-09 Undraining type flush toilet system

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Cited By (4)

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KR20190066222A (en) * 2017-12-05 2019-06-13 주식회사 퓨어엔비텍 Non-discharge water treatment equipment and non-discharge water treatment method using the same
JP2020049393A (en) * 2018-09-21 2020-04-02 松本工業株式会社 Sewage disposal method
JP2020048429A (en) * 2018-09-21 2020-04-02 松本工業株式会社 Method for producing nitrated nutrient solution from human excrement
CN111592141A (en) * 2020-05-19 2020-08-28 同济大学 Non-discharge self-cleaning type circulating water flushing toilet

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20190066222A (en) * 2017-12-05 2019-06-13 주식회사 퓨어엔비텍 Non-discharge water treatment equipment and non-discharge water treatment method using the same
KR102008362B1 (en) * 2017-12-05 2019-08-07 주식회사 퓨어엔비텍 Non-discharge water treatment equipment and non-discharge water treatment method using the same
JP2020049393A (en) * 2018-09-21 2020-04-02 松本工業株式会社 Sewage disposal method
JP2020048429A (en) * 2018-09-21 2020-04-02 松本工業株式会社 Method for producing nitrated nutrient solution from human excrement
CN111592141A (en) * 2020-05-19 2020-08-28 同济大学 Non-discharge self-cleaning type circulating water flushing toilet

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