JPS605288A - Method and apparatus for promoting simple treatment of various household waste water - Google Patents

Method and apparatus for promoting simple treatment of various household waste water

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Publication number
JPS605288A
JPS605288A JP10949183A JP10949183A JPS605288A JP S605288 A JPS605288 A JP S605288A JP 10949183 A JP10949183 A JP 10949183A JP 10949183 A JP10949183 A JP 10949183A JP S605288 A JPS605288 A JP S605288A
Authority
JP
Japan
Prior art keywords
wastewater
basin
sewage
heat
household
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.)
Granted
Application number
JP10949183A
Other languages
Japanese (ja)
Other versions
JPS646835B2 (en
Inventor
Masatoshi Shindo
正俊 進藤
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.)
KANKYO KANRI CENTER KK
Original Assignee
KANKYO KANRI CENTER 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 KANKYO KANRI CENTER KK filed Critical KANKYO KANRI CENTER KK
Priority to JP10949183A priority Critical patent/JPS605288A/en
Publication of JPS605288A publication Critical patent/JPS605288A/en
Publication of JPS646835B2 publication Critical patent/JPS646835B2/ja
Granted legal-status Critical Current

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  • Treatment Of Biological Wastes In General (AREA)

Abstract

PURPOSE:To promote the biochemical oxidizing action of various waste waters, by such a simple method that hot waste water and the other various waste waters in household waste water are induced to a heat insulating measure to be stored therein and the heat energy of hot waste water is transmitted to various waste waters. CONSTITUTION:Drain pipes 4 for household various waste waters from a kitchen K, a washing lavatory S or the like are provided so as to reach a public water area such as a road culvert D by piping work in such a state that sewage measures b1, b2... are arranged to required places. In place of one sewage measure in this arranged pipe system, a heat insulating measure 1 provided with a heat insulating material 2 is provided. The draw-in port 41 of the drain pipe 4 from the hot waste water source such as a bathroom F and the draw-in ports 51 of the other various waste waters are separately confronted to the heat insulating measure 1 to induce the hot waste water and the various waste waters in separate systems. The heat energy possessed by the hot waste water is directly transmitted to the various waste waters in the heat insulating measure 1. Biochemical oxidizing action is promoted during the stay of the waste waters in the heat insulating measure 1 and various waste waters of which the BOD values are lowered are discharged from the drain pipes 4.

Description

【発明の詳細な説明】 この発明は、道路側溝等の公共用水域に排出される家庭
雑排水の沈澱、分離効果をfffi易に処理、促進する
ための、特に寒冷地に有効な方法と、その実施に必要と
なる処理装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention provides a method particularly effective in cold regions for easily treating and promoting the sedimentation and separation effects of domestic gray water discharged into public water bodies such as road gutters; It relates to the processing equipment necessary for its implementation.

都市計画が進められた大都市周辺の団地をかかえる市町
村等では、膨大な量で排出される汚物等の生活排水を特
定箇所に集中させ、近代的な下水汚物処理技術によって
完全な浄化処理を実施するようにしているが、その他の
地域での生活排水の処理状況を見てみると、良心的な配
慮をしている家庭でも、精々建物の周辺から道路側溝に
至る過程で幾つかの汚水桝を経由させ、それら汚水桝に
おいて沈澱2分離から生物化学的酸化処理を施すように
しているだけで、汚物源となる物質をより効果的に除去
するそれ以上に有効な手段が採用されることはほとんど
見受けられないというのが実情である。その結果、公共
用水域には汚物が実質的に垂流し状に流入、滞留して排
水効果が損われ、溢水の原因となるばかりではなく、生
活環境を不衛生で住みにくい状態に陥れてしまっている
0 このような状況を呈している大きな原因の一つは、生活
排水である家庭雑廃水が公共用水域に達するまでの各家
庭敷地内で、簡便且つ安価に採用し得る有用な処理促進
方法およびそのための装置が開発実用化されていない実
情にあるのではないかと考えられる。
In cities, towns and villages with housing complexes around large cities where urban planning has been advanced, huge amounts of household wastewater such as filth is concentrated in specific areas and complete purification treatment is carried out using modern sewage treatment technology. However, when we look at the treatment status of domestic wastewater in other regions, we find that even households that take conscientious considerations end up using several sewage basins in the process from around buildings to roadside gutters. By simply conducting biochemical oxidation treatment from sediment separation in these sewage basins, it is not possible to adopt more effective means to more effectively remove substances that are the source of filth. The reality is that it is almost never seen. As a result, filth practically flows into public water bodies and accumulates there, impairing the drainage effect, not only causing flooding, but also making the living environment unsanitary and inhospitable. 0 One of the major reasons for this situation is the need to promote effective treatment that can be easily and inexpensively carried out on each household premises before household wastewater reaches public water bodies. It is thought that the actual situation is that the method and equipment for the same have not been developed and put into practical use.

そこで、この発明ではそれらの状況に対処するため、永
年に亘り鋭意開発研究を継続して来た結果、以下に詳述
するとおりの簡便な汚水処理方法とそのための装置全完
成、実′用化するに至ったものである。
Therefore, in order to deal with these situations, this invention has been devoted to continuous development and research for many years, and as a result, we have completed and put into practical use a simple sewage treatment method and a device for it, as detailed below. This is what I came to do.

水域に至る時点で所謂BOD (生物化学的酸素要求量
)の価をなるべく低く至らしめることを指向するもので
、家庭雑廃水に温廃水とそれ以外の廃水が存在している
ことに着目し、家庭雑廃水の中の温廃水、主に風呂場か
らの廃水をその他の雑廃水と別系統で、保温材の併用さ
れた比較的大きな容量を有するコンクリート桝その他の
保温桝内に誘導する如くなし、該保温桝内において温廃
水の有する熱エネルギーを直接かもしくは間接に温廃水
以外の雑廃水に伝達することにより、これら温廃水以外
の家庭雑廃水の生物化学的酸化作用を促進させ、公共用
水域に達する前にBOD値を極力低下させてしまうよう
にすることを特徴とする、家庭雑廃水の簡易処理促進方
法である。家庭雑廃水の中の温廃水としては、既述した
とおり、主として風呂場からの廃水を想定しているが、
これは、まず単一箇所からまとまって大量に排出され、
他の雑廃水から分離し易いことと、比較的沈澱物の少な
い廃水であることに起因しており、勿論、その他空調施
設からの排水等も同様の理由から格好の温廃水である外
、台所等で排出される廃水の中、分離可能な限りその温
廃水を利用するのが望ましい。したがって、温廃水とそ
れ以外の廃水といっても、実質的には雑廃水の中の分離
しがたい温廃水は、この発明では温廃水以外の廃水とし
て扱われることになる。
The aim is to reduce the so-called BOD (Biochemical Oxygen Demand) value as low as possible at the time it reaches the water body, and it focuses on the fact that household wastewater contains warm wastewater and other types of wastewater. Warm domestic wastewater, mainly wastewater from bathrooms, is not routed separately from other miscellaneous wastewater into a concrete basin or other heat-insulating basin that has a relatively large capacity and is also equipped with heat-insulating material. By directly or indirectly transmitting the thermal energy of warm wastewater to miscellaneous wastewater other than hot wastewater in the thermal insulation basin, the biochemical oxidation effect of domestic miscellaneous wastewater other than hot wastewater is promoted, and the heat energy is This is a simple method for promoting the treatment of household wastewater, which is characterized by reducing the BOD value as much as possible before it reaches the water area. As mentioned above, the hot wastewater included in household wastewater is mainly assumed to be wastewater from bathrooms.
First, a large amount of this is emitted from a single location,
This is due to the fact that it is easy to separate from other miscellaneous wastewater and is wastewater with relatively little sediment.Of course, wastewater from other air conditioning facilities is also suitable for the same reasons, as well as kitchen wastewater. It is desirable to use warm wastewater as much as possible from the wastewater discharged from other plants, etc., if it is separable. Therefore, even though warm wastewater and other wastewater are referred to, warm wastewater that is difficult to separate from miscellaneous wastewater is treated as wastewater other than warm wastewater in this invention.

通常、水温が摂氏5度以下に低下してしまうと、微生物
相の生活作用が著しく停滞し、生物化学的な浄化機能に
支障を来してしまい、汚水桝内で沈澱、分離した汚物等
のスラッジは、酸化、腐敗されることなく、終には道路
側溝等の公共用水域に流れ出てしまい、生活環境に悪影
響を及ぼすことになる。特に寒冷地ではその傾向が長期
間に亘るため、公共用水域の汚れがひどくなってしまう
ことが知られている。しかしながら、近代的な下水汚物
処理施設の完備されていないそれら地域では、そのよう
な原因が解ってはいても、各家庭毎に」二記下水汚物処
理施設で採用しているような、消化槽内部に熱交換器を
設置し、細菌の繁殖適正温度の範囲に合わせて一定湿度
に温度調整するようにする高価で高度な施設を採用する
こと等は到底望むことができない。そこで、この発明で
は、家庭雑廃水の中の温廃水を熱エネルギー源に利用す
るようにしたものであるが、従前までの要所要所に小型
(−辺600〜400關程度)の汚水桝を配し、それら
を1本の排水管で接続して公共用水域まで誘導する形式
の排水系統では、例えば、風呂場等から大量に温廃水が
排出されてもその池の雑廃水と一緒になって流出してし
まい、小いないことと、滞留容積が小さいことからすぐ
に冷却してしまい、沈澱、分離した汚物等のスラッジを
酸化、腐敗させる生物化学的酸化作用に何等寄与するこ
とができないばかりか、最も活用可能な温廃水源である
風呂場からの温廃水等は、一度期に大組に流出するため
、比較的小規模の汚水桝内にあっては、折角沈澱、分離
したスラッジを攪拌、浮遊せしめ、酸化、腐敗する間も
なく公共用水域に流れ出してしまう悪作用さえ及ぼすほ
どである。したがって、この発明は、それら従前までの
排水系統とは別系統で温廃水用の排水系統を設けること
、温廃水の滞留時間を延ばすに必要な比較的大きな容量
の保温桝を実現することによって家庭兼廃水の中の温廃
水を有効な熱エネルギー源に活用し得るようにしたもの
である。
Normally, when the water temperature drops below 5 degrees Celsius, the life activities of microorganisms significantly stagnate, which impedes the biochemical purification function and causes sedimentation and separation of sewage in the sewage basin. The sludge is not oxidized or putrefied, and eventually flows out into public water bodies such as road gutters, which has a negative impact on the living environment. It is known that, especially in cold regions, this tendency continues for a long period of time, resulting in public water bodies becoming increasingly polluted. However, in those areas where modern sewage treatment facilities are not fully equipped, even if the cause is known, each household has to install a digestion tank like the one used in the sewage treatment facilities mentioned in Section 2. It is impossible to hope for the use of expensive and sophisticated facilities that install a heat exchanger inside and adjust the temperature to a constant humidity according to the temperature range suitable for bacterial growth. Therefore, in this invention, warm wastewater in domestic miscellaneous wastewater is used as a thermal energy source, but small sewage basins (approximately 600 to 400 square meters) are installed at key points. In a drainage system that connects them with a single drainage pipe and guides them to a public water area, for example, even if a large amount of warm wastewater is discharged from a bathroom, etc., it will be mixed with the miscellaneous wastewater of the pond. Because it is small and has a small retention volume, it cools down quickly and cannot contribute in any way to the biochemical oxidation effect that oxidizes and rots the sludge such as sediment and separated filth. In addition, hot wastewater from bathrooms, which is the most usable hot wastewater source, flows into the large tank at once, so if it is in a relatively small-scale sewage basin, it is necessary to remove the sedimentation and separated sludge. It is so harmful that it becomes agitated, floats, oxidizes, and even spills into public water bodies before it decomposes. Therefore, this invention provides a drainage system for warm wastewater that is separate from the conventional drainage system, and realizes a relatively large-capacity heat retention basin necessary to extend the retention time of hot wastewater, thereby making it possible to improve the efficiency of household use. This system is designed to make it possible to utilize warm wastewater in the combined wastewater as an effective source of thermal energy.

この発明の家庭兼廃水の簡易処理方法を各家庭で採用す
るには、従前までの小型の汚水桝を幾つか連続させて1
系統の排水系統を実現するようにしたところにあっては
、温廃水源(例えば風呂場等)に最も近いそれら排水系
統部分に予めかあるいは追加工事等によって所定規模で
保温材の併用された保湿材の併用された保温桝を設置し
、その保温桝まで従前までの排水系統とは別系統で温廃
水源からの排水管を誘導、敷設するだげの負担で簡便に
採用することが可能である。また、全く汚水桝を設けず
、直接公共用水域に家庭兼廃水を放流している家庭にお
いても、その公共用水域に達するまでの中途に−I―記
と同様の負担で実施することができる。なお、保温材の
併用された保温桝の規模は、大孔−辺600mm程度の
桝が最低規模の目安とされる。
In order to adopt the simple domestic and wastewater treatment method of this invention in each household, it is necessary to connect several conventional small-sized sewage basins into one.
In places where system drainage systems have been implemented, heat insulating materials have been added to the parts of the drainage system closest to the hot wastewater source (for example, bathrooms, etc.) in advance or through additional construction to provide moisture retention. It is possible to install a heat-retaining basin that uses a combination of wood and to install a drainage pipe from the warm wastewater source to the heat-retaining basin in a separate system from the previous drainage system. be. In addition, even in households that do not have a sewage basin at all and discharge domestic wastewater directly into public water bodies, this can be carried out at the same cost as in Section -I- until it reaches the public water area. . Note that the minimum size of a heat-insulating box in which a heat-insulating material is used is a large hole with a side of about 600 mm.

上記のとおりの家庭兼廃水の簡易処理促進方法を最も効
率的に実施する実施態様の一つとして、保温桝内に流入
する温廃水の熱エネルギーを効率良く温廃水以外の雑廃
水に伝達する次のような方法が完成されている。
As one of the most efficient implementations of the above-mentioned method for promoting the simple treatment of household wastewater, the following method is adopted: A similar method has been completed.

即ち、保温材が併用されて所定規模に形成された保温桝
内に、熱交換壁兼用の隔II壁から成る汚水桝を独立さ
せて形成するか、もしくは、既存の汚水桝や汚水処理槽
を独立させて配設し、これら汚水桝や汚水処理槽には温
廃水以外の家庭兼廃水を、また、上記汚水桝や汚水処理
槽で区画された部分以外の保温桝内には温廃水を夫夫別
系統で流入、滞留させると共に、保温桝内に別々に流入
、滞留する温廃水とそれ以外の雑廃水とを夫々別個に保
温桝外に流出する如くなし、保温桝内に滞留する温廃水
とそれ以外の雑廃水との滞留時間に差異を生ぜしめ、温
廃水の有する熱エネルギーを間接的に温廃水以外の雑廃
水に伝達するようにした家庭兼廃水の簡易処理促進方法
である。
In other words, a sewage basin consisting of a partition II wall that also serves as a heat exchange wall is formed independently within a heat insulation basin formed to a predetermined scale using a heat insulating material, or an existing sewage basin or sewage treatment tank is used. These sewage basins and sewage treatment tanks will be used for household wastewater other than heated wastewater, and the heat-retaining basins other than those divided by the sewage basins and sewage treatment tanks will be used for heated wastewater. The hot wastewater flows in and stays in separate systems, and the warm wastewater and other miscellaneous wastewater that flow in and stay in the heat-insulating box separately flow out of the heat-insulating box, and the warm wastewater stays in the heat-insulating box. This is a simple method for promoting the treatment of household wastewater, which creates a difference in the residence time between hot wastewater and other miscellaneous wastewater, and indirectly transfers the thermal energy of hot wastewater to miscellaneous wastewater other than hot wastewater.

この方法では、保温桝内においても温廃水とそれ以外の
雑廃水とが熱交換壁兼用隔離壁によって分離されている
ため、゛所定容量の温廃水が常に保温桝内に残留して所
定の熱エネルギーを保存し、しかも、温廃水の流入によ
ってその他の雑廃水の折角沈澱、分離したスラッジを攪
拌、浮遊さ、せてしまうことを防止できることから、ス
ラッジの生物化学的酸化作用が非常に効率良く進み、公
共用水域に達するBOD値を極力低下させることができ
るものとなる。
In this method, warm wastewater and other miscellaneous wastewater are separated in the heat-retaining tank by a heat exchange wall and isolation wall, so that a predetermined volume of hot wastewater always remains in the heat-retaining tank and the predetermined heat is maintained. The biochemical oxidation effect of sludge is extremely efficient because it conserves energy and prevents the inflow of warm wastewater from causing other miscellaneous wastewater to settle, and the separated sludge to be stirred and suspended. As a result, the BOD value that reaches public water bodies can be reduced as much as possible.

上記のとおりの方法を実施するための代表的な実施例が
、第1〜6図に示されている。
Representative embodiments for carrying out the method as described above are shown in FIGS. 1-6.

まず、第1図に示す配置図からも理解されるとおり、厨
房に、洗濯・洗面所S等からの家庭雑記水用の排水管4
を、従来どおり、要所要所に汚水桝b1.b2・・・・
・・を配した」−1道路側溝り等の公共用水域まで配管
、設置する。通常、この配管系は、新築される建造物は
固より、既に建築されて1しまっている建造物の大部分
に採用されているから、特別に新しい技術的配慮を必要
としない。
First, as can be understood from the layout shown in Figure 1, there is a drain pipe 4 in the kitchen for household miscellaneous water from the laundry/washroom S, etc.
As before, sewage basins b1. b2...
-1 Piping and installation to public water bodies such as road ditches. Normally, this piping system is used not only in newly constructed buildings but also in the majority of already constructed buildings, and therefore does not require any special new technical consideration.

この配管系の中の1つの汚水桝b (特にどれでなけれ
ばならないという限定はないが、熱効率や配管上の問題
から温廃水源・−により近し)箇所の汚水桝b、実施例
では、汚水桝す乙と汚水桝b5との間で、この発明によ
らなければ汚水桝b4−図示せず−が配されるべきとこ
ろ)しこ代えて、保温材2の併用された保湿°桝1を設
置する。
In this example, one sewage basin B in this piping system (although there is no particular limitation on which one it has to be, it is closer to the hot waste water source due to thermal efficiency and piping problems), Between the sewage basin B and the sewage basin B5, where the sewage basin b4 (not shown) would have been placed if it were not according to the present invention), a moisturizing basin 1 in which a heat insulating material 2 is used together is installed. Set up.

この保温材1は、第2ないしろ図に示す平面図および同
縦断面図に図示されている実施例のように、温廃水源(
第1図に示す実施例では浴室下)からの排水管4の引込
み口4′lと、その他の雑廃水の排水管5の引込み口5
1とを夫々別々に保温材1内に望ませ、温廃水とその他
の雑廃水とが別系統で保温材1内に誘導されるようにな
し、保温材1内において初めて温廃水とその他の雑廃水
とが混合されて直接温廃水の熱エネルギーがその他の雑
廃水に伝達されるようにする。そして、この熱エネルギ
ーは、保温材2が併用されて保温性の向上された所定規
模の保温材1内において比較的永く滞留し、生物化学的
酸化作用を助長して排水管4から排水される雑廃水のB
OD値をドげるようにする構造のものが最も簡便ではあ
るが、排出される雑廃水の量と保温材1の容量との関係
によって雑廃水の滞留期間が左右される、即ち、温廃水
に比較してその他の雑廃水量が多い場合に温廃水か希釈
された」二、保湿tsから流れ出してしまうため、温廃
水の熱エネルギーが有効に活用されにくくなることも予
想される。
This heat insulating material 1 is constructed from a warm wastewater source (
In the embodiment shown in FIG. 1, the inlet 4'l of the drain pipe 4 from (under the bathroom) and the inlet 5 of the drain pipe 5 for other miscellaneous waste water.
1 and 1 separately in the heat insulating material 1, so that the warm wastewater and other miscellaneous wastewater are guided into the heat insulating material 1 through separate systems, and the warm wastewater and other miscellaneous wastewater are separated into the heat insulating material 1 for the first time. The wastewater is mixed directly with the hot wastewater so that the thermal energy of the hot wastewater is transferred to other miscellaneous wastewater. Then, this thermal energy remains for a relatively long time in the heat insulating material 1 of a predetermined size whose heat retaining properties are improved by using the heat insulating material 2, promotes biochemical oxidation, and is drained from the drain pipe 4. Miscellaneous wastewater B
Although a structure that lowers the OD value is the simplest, the retention period of miscellaneous wastewater depends on the relationship between the amount of miscellaneous wastewater discharged and the capacity of the heat insulating material 1. When the amount of other miscellaneous wastewater is large compared to the amount of other miscellaneous wastewater, it is expected that the thermal energy of the heated wastewater will be difficult to utilize effectively because the heated wastewater will flow out of the moisturizing ts.

そこで、更に有効にこの発明の家庭外廃水の簡易処理促
進方法を実施するための装置として、第4ないし5図に
示す実施例の採用が必要となる場合がある。即ち、保温
材1の構造と[7て、外側面が発泡スチロールのような
合成樹脂発泡体その他の保温材2で覆われたコンクリー
ト桝で、その大きさは略600罰角立方体程度のものが
必要である(従前までに採用されている汚水桝の多くは
soomm角立方体のものである)。
Therefore, it may be necessary to employ the embodiments shown in FIGS. 4 and 5 as a device for more effectively carrying out the method for promoting the simple treatment of non-domestic wastewater of the present invention. That is, the structure of the heat insulating material 1 and [7] A concrete box whose outer surface is covered with a synthetic resin foam such as Styrofoam or other heat insulating material 2, and the size of which is approximately 600 square cubes, is required. (Many of the sewage basins that have been used so far are of the shape of a zoom square cube).

その内側には、波型ステンレス板やプラスチックス波型
板等を素材とする熱交換壁兼用隔離壁乙により汚水桝を
独立させて形成し、該汚水桝内を温廃水以外の雑廃水を
滞留させるド水滞留槽12、該汚水桝外の保温材1内を
温廃水を滞留させる温廃水滞留槽11とする。そして、
下水滞留槽12には、厨房にや洗濯、洗面所S力)らの
排水管5の引込み口51と掃出し口52を温廃水滞留槽
11に連通しないように独立させて配管すると共に、温
廃水滞留槽114こけ、温廃水源である浴室Fからの排
水管4の引込み口41と掃出し口42をド水滞留槽12
に関係せず独立させて配管する。なお、図示した実施例
では、保温材1のド流側に補助相6を一体に形成した例
とし、各掃出し口52.42側の排水管5.4を該補助
桝乙に望ませた後、補助桝乙に従前までの排水管5を接
続するようにしてしするが、必ずしもこの例に限定され
るものではなく、補助相6を設けず、各掃出し口52.
42側の排水管5.4を夫々独立したまま下流の汚水桝
b5に接続するようにしたり、あるl/)はまた、直接
夫々の排水管5.4を公共用水域Gこ到達するようにし
ても良い。
On the inside, an independent sewage basin is formed by a heat exchange wall and isolation wall B made of corrugated stainless steel plates, plastic corrugated plates, etc., and miscellaneous wastewater other than hot wastewater is stored inside the sewage basin. The inside of the heat insulating material 1 outside the sewage basin is used as a warm wastewater retention tank 11 in which heated wastewater is retained. and,
In the sewage retention tank 12, the intake port 51 and the sweep-out port 52 of the drain pipe 5 for the kitchen, laundry, washroom, etc. are installed independently so that they do not communicate with the heated wastewater retention tank 11, and the heated wastewater is Retention tank 114 The inlet 41 and sweep-out port 42 of the drain pipe 4 from the bathroom F, which is a source of hot wastewater, are connected to the water retention tank 12.
Piping should be done independently, regardless of the In the illustrated embodiment, the auxiliary phase 6 is integrally formed on the downstream side of the heat insulating material 1, and after the drain pipes 5.4 on the side of each sweep-out port 52. , the conventional drain pipe 5 is connected to the auxiliary pipe 5, but the example is not necessarily limited to this example, and the auxiliary phase 6 is not provided, and each sweep port 52.
The drain pipes 5.4 on the 42 side can be connected to the downstream sewage basin B5 while remaining independent, or the drain pipes 5.4 on the 42 side can be connected directly to the public water area G. It's okay.

第6ないし7図には、更に他の実施例が示されている。Still other embodiments are shown in FIGS. 6 and 7.

此の実施例では、犀尿浄化槽7を保温材1内に泣股し、
尿尿浄化槽7の夕1側に残る保温材1内を温廃水滞留槽
11となし、11コ尿浄δ 水管引込み口、十≠は同掃出し口、14は割栗石その他
の基礎盤、15は槽固定具を友々示している。
In this embodiment, the septic tank 7 is placed inside the heat insulating material 1,
The inside of the heat insulating material 1 remaining on the side 1 of the urine-urine septic tank 7 is designated as the heated wastewater retention tank 11, 11 is the urine-purifier δ water pipe inlet, 10 is the same sweep-out port, 14 is the foundation board such as cracked stone, 15 is Showing the tank fixings.

上記の各実施例からも理解されるとおり、この発明の方
法を実施する」二で必要となる装置は、何れも従前まで
の汚水桝の設置状況とそれ程変わることなく簡便に据え
付けを可能とする簡潔な構造のものであることから、安
価に製造、販売することができ、一般家庭において大き
な負担を抱えることなく簡易に家庭随廃水の処理促進方
法の実施を可能にするものである。特に、第4〜5図に
図示した装置に依れば、温廃水の熱エネルギーをより効
果的に活用することができ、公共用水域の浄化にとって
極めて有効なものとなる。
As can be understood from the above-mentioned embodiments, all of the devices required in step 2 of carrying out the method of the present invention can be easily installed without changing much from the installation situation of conventional sewage basins. Since it has a simple structure, it can be manufactured and sold at low cost, and it enables ordinary households to easily carry out the method for promoting the treatment of household wastewater without putting a large burden on them. In particular, the apparatus shown in FIGS. 4 and 5 allows the thermal energy of warm wastewater to be used more effectively, making it extremely effective for purifying public water bodies.

値上のとおり、この発明の家庭雑廃水の簡易処理促進方
法およびその装置は、家庭内から無造作に放出されてし
まう雑廃水の中の温廃水の熱エネルギーに着目し、それ
をその他の雑廃水の生物化学的酸化作用の活性化に有効
利用可能にしたものであることから、従前までのように
電気その他特別の熱エネルギーに依るもののように放熱
構造を特殊なものとしたりして大損りなものとなって一
般家庭での採用を難しくすることもなければ、通常の維
持経費を心配することもなくなり、各家庭の僅かな負担
で一地域の生活環境を極めて衛生的な状態にすることが
できる。特に、寒冷地等一時的に生物化学的酸化作用の
鈍化してしまう地域での採用は有効であり、また、その
他の地域においてもBOD値をより低下させて悪臭や病
害虫等の発生を極力押さえる手段、装置として有効であ
る。
As mentioned above, the method and device for promoting the simple treatment of household miscellaneous wastewater of the present invention focuses on the thermal energy of hot wastewater, which is included in the miscellaneous wastewater that is casually discharged from the home, and uses it to transfer the heat energy to other miscellaneous wastewater. Because it can be used effectively to activate the biochemical oxidation effect of This does not make it difficult for ordinary households to adopt it, and there is no need to worry about regular maintenance costs, making it possible to make the living environment of an area extremely sanitary with only a small burden on each household. . It is particularly effective to use in regions where biochemical oxidation is temporarily slowed down, such as in cold regions, and it can also be used in other regions to further reduce the BOD value and minimize the occurrence of bad odors and pests. It is effective as a means and device.

【図面の簡単な説明】 図面は、この発明の方法を実施する上で必要となる装置
の代表的な実施例を示したもので、第1図は、配置図、
第2図は、第1実施例の゛14面図、第6図は、同A 
−A断面図、第4図は、他の実施例による平面図、第5
図は、1i1113〜I3断面図、第6図は、更に他の
実施例によるものの平面図、第7図は、同C−C断面図
である。 1・・・保温桝、2・・・保温材、ろ・・・熱交換壁兼
用隔離壁、4・・・温廃水誘導用の排水管、5・・・そ
の他の雑廃水用の排水管、6・・・補助桝、7・・・I
q4尿浄化槽、b・・・従来の汚水桝、D・・・道路側
F:”i 。
[BRIEF DESCRIPTION OF THE DRAWINGS] The drawings show typical embodiments of the apparatus necessary to carry out the method of the present invention, and FIG. 1 shows a layout diagram,
FIG. 2 is a 14th view of the first embodiment, and FIG.
-A sectional view, FIG. 4 is a plan view according to another embodiment, and FIG.
The figure is a cross-sectional view from 1i1113 to I3, FIG. 6 is a plan view of another embodiment, and FIG. 7 is a cross-sectional view taken along the line C--C. 1...Heat insulation box, 2...Heat insulation material, Filter...Isolation wall that also serves as a heat exchange wall, 4...Drain pipe for guiding warm wastewater, 5...Drain pipe for other miscellaneous waste water, 6... Auxiliary box, 7... I
q4 Urine septic tank, b... conventional sewage basin, D... road side F: "i.

Claims (1)

【特許請求の範囲】 1 家庭兼廃水の中の温廃水とその他の雑廃水とを夫々
別系統で保温材の併用された比較的大きな容量を有する
コンクリート桝その他の保温桝内に誘導、滞留する如く
なし、該保温桝内において温廃水の有する熱エネルギー
を直播もしくは間接に温廃水以外の雑廃水に伝達するこ
とにより、これら温廃水以外の家庭兼廃水の生物化学的
酸化作用を促進するようにした家庭兼廃水の簡易処理促
進方法。 2 保湿桝内に熱交換壁兼用隔離壁から成る汚水桝を独
立させて形成するか、もしくは、既存の汚水桝や汚水処
理槽を独立させて配設し、これら汚水桝や汚水処理槽に
は温廃水以外の家庭兼廃水を、また、上記汚水桝や汚水
処理槽で区画された部分以外の保温桝内には温廃水を安
々別系統で流入、滞留させると共に、保湿桝内に別々に
流入、滞留する温廃水とそれ以外の郊廃水とを夫々別個
に保温桝外に流出する如< tr シ、保温桝内に滞留
する温廃水とそれ以外の雑廃水の滞留時間に差異を生せ
しめるようにした特許請求の範囲第1項記載の家庭兼廃
水の簡易処理促進方法。 6 所定の大きさで保温材を併用する等して形成したコ
ンクリート桝等の保温桝内に、熱交換壁兼用隔離壁で区
画した汚水桝を形成し、汚水桝内を家庭温廃水以外の雑
廃水を滞留する下水滞留槽、汚水桝外の保温桝内を家庭
濡廃水を滞留する温廃水滞留槽となし、夫々の滞留槽に
夫々独立して通じる流入管と流出管とを形成する如くし
た、特許請求の範囲第1〜2項記載の家庭兼廃水の簡易
処理促進方法を実施する処理装置。
[Scope of Claims] 1. Warm wastewater and other miscellaneous wastewater in household and wastewater are guided and retained in separate systems in a concrete basin or other heat-insulating basin having a relatively large capacity and also using a heat-insulating material. By transmitting the thermal energy of warm wastewater directly or indirectly to miscellaneous wastewater other than warm wastewater in the heat-retaining basin, the biochemical oxidation effect of household wastewater other than warm wastewater is promoted. A simple method for promoting the treatment of household wastewater. 2. Either form an independent sewage basin consisting of a heat exchange wall and isolation wall within the moisture retention basin, or install an existing sewage basin or sewage treatment tank independently, and these sewage basins or sewage treatment tanks Domestic wastewater other than heated wastewater, as well as heated wastewater that is not separated by the above-mentioned sewage basins and sewage treatment tanks, is allowed to flow into and remain in the heat retention basin in a separate system, and flow separately into the moisture retention basin. In this way, the warm wastewater that remains in the heat insulation tank and the other waste water are discharged separately from the heat insulation tank, and the retention time of the warm wastewater that remains in the heat insulation tank and the other waste water are made to differ. A method for promoting the simple treatment of household wastewater according to claim 1. 6. A sewage basin separated by a heat exchange wall and isolation wall is formed inside a heat-retaining basin such as a concrete basin of a predetermined size using heat insulating material, etc., and the inside of the sewage basin is used to store wastewater other than household heated wastewater. A sewage retention tank for retaining wastewater, and a warm wastewater retention tank for retaining household wet wastewater are formed inside the heat-retaining basin outside the sewage basin, and an inflow pipe and an outflow pipe are formed that independently communicate with each retention tank. , A treatment device for carrying out the method for promoting the simple treatment of domestic wastewater as set forth in claims 1 and 2.
JP10949183A 1983-06-18 1983-06-18 Method and apparatus for promoting simple treatment of various household waste water Granted JPS605288A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10949183A JPS605288A (en) 1983-06-18 1983-06-18 Method and apparatus for promoting simple treatment of various household waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10949183A JPS605288A (en) 1983-06-18 1983-06-18 Method and apparatus for promoting simple treatment of various household waste water

Publications (2)

Publication Number Publication Date
JPS605288A true JPS605288A (en) 1985-01-11
JPS646835B2 JPS646835B2 (en) 1989-02-06

Family

ID=14511591

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10949183A Granted JPS605288A (en) 1983-06-18 1983-06-18 Method and apparatus for promoting simple treatment of various household waste water

Country Status (1)

Country Link
JP (1) JPS605288A (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5038355A (en) * 1973-07-12 1975-04-09
JPS5111659U (en) * 1974-07-12 1976-01-28
JPS53103651A (en) * 1977-02-21 1978-09-09 Tomoyuki Okumura System for treating waste water of building

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5038355A (en) * 1973-07-12 1975-04-09
JPS5111659U (en) * 1974-07-12 1976-01-28
JPS53103651A (en) * 1977-02-21 1978-09-09 Tomoyuki Okumura System for treating waste water of building

Also Published As

Publication number Publication date
JPS646835B2 (en) 1989-02-06

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