JPS6135201Y2 - - Google Patents

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Publication number
JPS6135201Y2
JPS6135201Y2 JP16610880U JP16610880U JPS6135201Y2 JP S6135201 Y2 JPS6135201 Y2 JP S6135201Y2 JP 16610880 U JP16610880 U JP 16610880U JP 16610880 U JP16610880 U JP 16610880U JP S6135201 Y2 JPS6135201 Y2 JP S6135201Y2
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JP
Japan
Prior art keywords
chamber
sludge
tank
wastewater
basket
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.)
Expired
Application number
JP16610880U
Other languages
Japanese (ja)
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JPS5790711U (en
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
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Priority to JP16610880U priority Critical patent/JPS6135201Y2/ja
Publication of JPS5790711U publication Critical patent/JPS5790711U/ja
Application granted granted Critical
Publication of JPS6135201Y2 publication Critical patent/JPS6135201Y2/ja
Expired legal-status Critical Current

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Description

【考案の詳細な説明】 本考案は排水、とくに生活雑用水に含まれる活
泥を沈降およびろ過処理することを目的とした沈
澱槽に関するものである。
[Detailed Description of the Invention] The present invention relates to a sedimentation tank for the purpose of settling and filtering live mud contained in wastewater, especially household water.

一般家庭から排出される生活雑排水の処理方法
としては、公共下水道施設が利用され、いまだ下
水道施設が整備されていない地域では、河川、側
溝などへ直接排出するかあるいは土壌中へ吸込ま
せるなどして処理している。
Public sewage facilities are used to treat gray water discharged from general households, and in areas where sewage facilities are not yet in place, it may be discharged directly into rivers, gutters, etc., or it may be sucked into the soil. are being processed.

ところが、家庭の厨房、風呂、洗濯などから排
出される生活雑排水には、流しや洗い場のの過用
目皿を潜り抜けた野菜くず、手髪などの固形分や
油類などが多量に含まれているため、前記のよう
に河川などへ直接放流した場合、自然浄化作用を
上回る規模でこれらの汚泥物質が流入すると、汚
泥の堆積により美観を損ねたり、水質を著るしく
汚染する。また水田の場合は富栄養化による作物
の成育障害が発生したりする。更に土壌へ直接吸
い込ませる場合には、汚泥の付着や堆積により土
壌の処理能力が低下し、やがて近辺の地下水、河
川水を汚染することにもなる。
However, gray water discharged from household kitchens, baths, laundry, etc. contains large amounts of solid matter such as vegetable scraps, hand hair, and oils that have slipped through overused sinks and washrooms. Therefore, when these sludge substances are directly discharged into a river or the like as described above, if these sludge substances flow in at a scale that exceeds the natural purification effect, the sludge accumulates and spoils the aesthetic appearance and seriously pollutes the water quality. Furthermore, in the case of rice fields, eutrophication can cause crop growth problems. Furthermore, if the sludge is sucked directly into the soil, the treatment capacity of the soil will be reduced due to adhesion and accumulation of sludge, which will eventually contaminate nearby groundwater and river water.

ところで、生活雑排水が含む汚染物質には有機
質物と無機質物とがあり、有機質物の分解には水
中の酸素を必要とし、汚染物質を含む排水が一定
期間に消費する酸素量をBOD(生物化学的酸素
消費量)と呼び、排水中に懸濁している固形分の
量をSS(懸濁物質)と呼んでおり、いずれも数
値が大きいほど汚染度は高くなる。
By the way, the pollutants contained in gray wastewater include organic substances and inorganic substances. Oxygen in water is required to decompose organic substances, and the amount of oxygen consumed by wastewater containing pollutants in a certain period of time is calculated by BOD (biological The amount of solids suspended in wastewater is called SS (suspended solids), and the higher the value, the higher the degree of pollution.

したがつて排水処理用沈澱槽の役割は、排水中
の有機質や無機質の固形分を沈澱ろ過することに
よりBODとSS値を下げ、排出先の処理負担を軽
減させることにある。ここで、生活雑排水処理用
沈澱槽の機能を考えてみると、 (1) 耐久性があること (2) 一般家庭の敷地内で容易に設置できる寸法で
あること。
Therefore, the role of a sedimentation tank for wastewater treatment is to reduce the BOD and SS values by settling and filtering the organic and inorganic solids in the wastewater, thereby reducing the processing burden on the wastewater discharge destination. If we consider the functions of a settling tank for treating gray water, (1) it must be durable, and (2) it must be of a size that can be easily installed on the premises of a general household.

(3) 家庭の排水量に見合つた沈澱、ろ過能力をも
つこと。
(3) It must have sedimentation and filtration capabilities commensurate with household wastewater volume.

(4) 汚泥掃除等の保持が簡便であること。(4) It is easy to maintain and clean sludge.

等の点を満足させる必要がある。 It is necessary to satisfy the following points.

特に一般家庭用の沈澱槽の設置個所は厨房近辺
の狭少な場所が多く、しかも沈澱汚泥の処理作業
は婦女子が行う場合が多い。したがつて地中に埋
設しても土圧、腐食などの作用に対して耐久性が
あり、コンパクトでありながら処理量が大きく、
しかも清掃が簡単に行える構造が望まれる。
In particular, settling tanks for general households are often installed in small spaces near kitchens, and the work of treating the settled sludge is often carried out by women and girls. Therefore, even when buried underground, it is durable against earth pressure and corrosion, and although it is compact, it has a large processing capacity.
Moreover, a structure that can be easily cleaned is desired.

また、排水の内容は各家庭によつて質や量が異
なつているため、これにも対応できる沈澱槽が要
求されている。
Furthermore, since the quality and quantity of wastewater differs from household to household, a sedimentation tank that can handle this is required.

そこで処理能力を向上させるためには、沈澱槽
の容量を大きくするか、多室構造にして滞流によ
る沈澱効果を高めるか、または目の細かいフイル
ターを使用して除去効果を上げる方法が考えられ
るが、家庭用としては沈澱槽の大型化にはおのず
と限界があり、また多室構造にすると、各室に沈
澱かごが必要となつて清掃が繁雑化し、さらに、
目の細かいフイルターを使用すると細かくなる程
単位時間当りの排水処理量が小さくなるという問
題が生ずる。
Therefore, in order to improve processing capacity, it is possible to increase the capacity of the sedimentation tank, increase the sedimentation effect by creating a multi-chambered structure, or use a fine-mesh filter to increase the removal effect. However, for household use, there is a natural limit to the size of the sedimentation tank, and if a multi-chamber structure is used, each chamber will require a sedimentation basket, making cleaning more complicated.
If a fine filter is used, a problem arises in that the finer the filter, the smaller the amount of wastewater treated per unit time.

従来公知の家庭用沈澱槽を考えると、いずれも
寸法上の制約を受け小型化しているため、排水の
処理能力が不足したり、あるいは処理能力を維持
するため槽内を多室としたため汚泥の除去、清掃
が面倒となるなどの問題があつた。
Considering conventional household sedimentation tanks, they are all limited in size and have been made smaller, resulting in insufficient wastewater treatment capacity, or because the tank has multiple chambers to maintain treatment capacity, sludge There were problems such as troublesome removal and cleaning.

以上の問題を改善すべく、本考案者は鋭意研究
の結果、処理能力の向上に資する新しい構造を開
発したので、こゝに提案しようとするものであ
る。
In order to improve the above-mentioned problems, the inventor of the present invention has developed a new structure that contributes to improved processing performance as a result of intensive research, and would like to propose it here.

すなわち、本考案は下端が底部に達するのれん
状の一次フイルターと、下部流路11aを形成し
た浮遊物除去板を設けて沈澱槽を三つの室に仕切
り、その第1室の後室と第2室の底に取手を備え
た出し入れ可能な汚泥かごを置き、前記第1室の
前室と第3室の底部を汚泥が汚泥かごに流れ落ち
るように傾斜させ、且つ前記第1室の前室に〓状
の臭気逆流防止用の流入パイプを挿入し、その排
水口に邪魔板を針金で吊下すると共に、前記第3
室にのれん状の二次フイルターを収め、且つ排出
パイプを接続した排水処理用沈澱槽である。
That is, the present invention divides the sedimentation tank into three chambers by providing a curtain-shaped primary filter whose lower end reaches the bottom and a floating matter removal plate forming a lower flow path 11a. A removable sludge basket equipped with a handle is placed at the bottom of the chamber, and the bottoms of the front chamber of the first chamber and the third chamber are inclined so that the sludge flows into the sludge basket, and the front chamber of the first chamber is A square-shaped inflow pipe for preventing odor backflow is inserted, and a baffle plate is suspended from the drain port with a wire.
This is a sedimentation tank for wastewater treatment that houses a curtain-shaped secondary filter in the chamber and connects a discharge pipe.

このように構成すると、邪魔板の設置位置及び
角度によつて水流を調整することができ、しかも
水流が分散させられるので、減速して水流による
槽内汚れの撹拌作用が弱められるので、従来のも
のより沈澱時間が短縮する効果があり、しかも一
次及び二次フイルターによるフイルター効果によ
つて小型の沈澱槽でも処理能力のあるものが得ら
れることになる。
With this configuration, the water flow can be adjusted by adjusting the installation position and angle of the baffle plate, and since the water flow is dispersed, the water flow is slowed down and the stirring effect of the water flow on dirt in the tank is weakened. It has the effect of shortening the precipitation time more than anything else, and the filter effect of the primary and secondary filters allows even a small precipitation tank to have sufficient processing capacity.

以下、本考案の実施例について図面に基づき説
明すれば次の通りである。
Hereinafter, embodiments of the present invention will be described based on the drawings.

第1図は本案実施例の平面図、第2図はその縦
断面図、第3図はA−A線断面図で、Aは沈澱槽
である。
FIG. 1 is a plan view of the embodiment of the present invention, FIG. 2 is a vertical sectional view thereof, and FIG. 3 is a sectional view taken along the line A--A, where A is a settling tank.

沈澱槽本体の材質はプラスチツク、コンクリー
トあるいはそれらの繊維補強材料などで容易に持
ち運びができる寸法および重量に造られる。
The material of the sedimentation tank body is plastic, concrete, or their fiber-reinforced materials, and the size and weight are such that it can be easily carried.

そして槽内は三つの室1,2,3に仕切られ、
流入口4には第1室の前室1aに臨む〓状の臭気
逆流防止用の流入パイプ5が挿入されていて、そ
の排水口に邪魔板6が4本の針金7で出口側を上
に斜めに吊り下げてある。また同時に二あるいは
三方向から接続できるよう他の二方向に予備流入
口形成可能部4a,4bが用意されている。そう
して第1室1の後室1bと第2室2の底に出し入
れ可能な取手8を備えた汚泥かご9を置き、その
中央に上方に引抜き可能な一次フイルター10を
下端が底部に達するまで挿入し、第1室と第2室
に分割する。第2室2と第3室3の間は下部流路
11aを形成した浮遊物除去板11で仕切られて
おり、第3室3には二次フイルター12が収めら
れ、さらに排水パイプ13が接続している。
The inside of the tank is divided into three chambers 1, 2, and 3.
A cross-shaped inflow pipe 5 for preventing odor backflow facing the front chamber 1a of the first chamber is inserted into the inflow port 4, and a baffle plate 6 is connected to the drain port with four wires 7 with the exit side facing upward. It is hung diagonally. In addition, preliminary inlet forming portions 4a and 4b are provided in two other directions so that connections can be made from two or three directions at the same time. Then, a sludge basket 9 equipped with a handle 8 that can be taken in and taken out is placed at the bottom of the rear chamber 1b of the first chamber 1 and the second chamber 2, and a primary filter 10 that can be pulled out upward is placed in the center with its lower end reaching the bottom. Insert until the end and divide it into the first and second chambers. The second chamber 2 and the third chamber 3 are separated by a floating matter removal plate 11 that forms a lower flow path 11a, and the third chamber 3 houses a secondary filter 12, and is further connected to a drain pipe 13. are doing.

前記一次フイルター10と二次フイルター12
は合成樹脂製リボンaの上部を芯板に止めてのれ
ん状としたもので、リボンaの断面形状や大きさ
及び密度等は本沈澱槽を使用する条件によつて決
められる。また第1室1の前室1aと第3室3の
底部は汚泥が汚泥かご9に流れ落ちるよう傾斜し
ている。なお各リボンaの下端部は通常そのまゝ
であるが、必要に応じて固定する場合もある。ま
た図示しなかつたが、沈澱槽本体には、雨水や外
部からのごみが混入しないよう防錆処理した鉄板
などで蓋をする。
The primary filter 10 and the secondary filter 12
The upper part of a synthetic resin ribbon a is fixed to a core plate to form a curtain shape, and the cross-sectional shape, size, density, etc. of the ribbon a are determined by the conditions under which the settling tank is used. Further, the bottoms of the front chamber 1a of the first chamber 1 and the third chamber 3 are inclined so that the sludge flows down into the sludge basket 9. Note that the lower end of each ribbon a usually remains as it is, but may be fixed if necessary. Although not shown in the drawings, the sedimentation tank body is covered with a rust-proofed iron plate or the like to prevent rainwater and external debris from getting mixed in.

以上のように構成されるので、今臭気逆流防止
用ベンドパイプ5を通つて槽内へ雑排水が流入す
ると、邪魔板6によつて四散する。四散した汚水
は流速を落し拡散しながら一次フイルター10を
通過することによつて更に流れが弱まる。
With the above structure, when gray water flows into the tank through the odor backflow prevention bend pipe 5, it is dispersed by the baffle plate 6. The scattered wastewater passes through the primary filter 10 while slowing down and diffusing, thereby further weakening the flow.

一方排水中の汚泥は傾斜している邪魔板6上に
は堆積することなく第1室の前室1aの底面を滑
り落ち、あるいは一次フイルター10によつて、
第1室の後室1aに設置してある汚泥かご9に沈
降堆積する。
On the other hand, the sludge in the drainage does not accumulate on the inclined baffle plate 6, but slides down the bottom of the front chamber 1a of the first chamber, or is filtered through the primary filter 10.
The sludge settles and accumulates in the sludge basket 9 installed in the rear chamber 1a of the first chamber.

そうして一次フイルター10でろ過された汚水
は二次フイルター12でさらにろ過され浄化水と
なつて排水パイプ13から槽外へ排出される。
The wastewater filtered by the primary filter 10 is further filtered by the secondary filter 12 to become purified water, and is discharged from the drain pipe 13 to the outside of the tank.

浮遊物や油脂類は一次フイルター10でも一部
除去されるが、微細な浮遊物などは第2室2を通
過する際浮上し、浮遊物除去板11によつて進行
を妨げられ第2室2の水面上に滞溜する。
Floating substances and fats and oils are partially removed by the primary filter 10, but fine floating substances float up when passing through the second chamber 2 and are prevented from advancing by the floating substance removal plate 11. stagnates on the water surface.

雑排水の流入が止むと、槽内の水位より高い流
入パイプ中には排水汚泥が残溜することなく槽内
へ流入し、一方臭気逆流防止用流入パイプの流出
口は水中にあるため槽内の臭気が流入パイプ中へ
逆流することもない。
When the inflow of gray water stops, wastewater sludge flows into the tank without remaining in the inflow pipe that is higher than the water level in the tank, while the outflow port of the inflow pipe for preventing odor backflow is under water, so the inside of the tank is odors will not flow back into the inlet pipe.

沈澱汚泥の清掃作業は極めて簡単である。ま
ず、一次フイルター10及び二次フイルター12
を抜き上げ、取手8を持つて汚泥かご9を槽外に
出す。各フイルター10,12はのれん状である
ので、水洗又は櫛歯などでしごくことにより詰つ
ている汚泥を容易に除去できる。第1室、第2室
で共用する汚泥かご9は網状になつているので水
切れがよいため軽く持ち上げられる。なお取手を
固定式でなく180度回転できるとしてかごが逆転
するようにしておけば清掃がよりしやすくなる。
Cleaning the settled sludge is extremely easy. First, the primary filter 10 and the secondary filter 12
Pull out the sludge basket 9, hold the handle 8, and take the sludge basket 9 out of the tank. Since each of the filters 10 and 12 has a curtain shape, clogged sludge can be easily removed by washing with water or squeezing with a comb. The sludge basket 9, which is shared by the first and second chambers, has a net shape and drains easily, so it can be easily lifted. Furthermore, if the handle is not fixed and can be rotated 180 degrees so that the basket can be reversed, cleaning will be easier.

清掃終了後は逆の順序で収納する。 After cleaning, store in reverse order.

以上実施例について説明したが、本考案では使
用時、流入パイプの出口は沈澱槽内の汚水中に突
入しているので、槽内の臭気が流入パイプ中に逆
流することがないので、臭気が厨房や風呂場にた
だようということがなく、また、前述のように邪
魔板の設置位置を実験的に定めることにより、小
型で処理能力のある沈澱槽が得られる効果があ
る。
As described above, the present invention is used because the outlet of the inflow pipe enters the wastewater in the sedimentation tank, so the odor inside the tank does not flow back into the inflow pipe. It does not have to be left in the kitchen or bathroom, and by determining the installation position of the baffle plate experimentally as described above, a compact sedimentation tank with high processing capacity can be obtained.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本案実施例の平面図、第2図はその縦
断面図、第3図はA−A線断面図である。 A……沈澱槽、1……第1室、2……第2室、
3……第3室、4……流入口、5……流入パイ
プ、6……邪魔板、7……針金、8……取手、9
……汚泥かご、10……一次フイルター、11…
…浮遊物除去板、12……二次フイルター、13
……排出パイプ。
FIG. 1 is a plan view of the embodiment of the present invention, FIG. 2 is a longitudinal sectional view thereof, and FIG. 3 is a sectional view taken along the line A--A. A...Sedimentation tank, 1...First chamber, 2...Second chamber,
3...Third chamber, 4...Inflow port, 5...Inflow pipe, 6...Baffle plate, 7...Wire, 8...Handle, 9
...Sludge basket, 10...Primary filter, 11...
...Floating matter removal plate, 12...Secondary filter, 13
...Exhaust pipe.

Claims (1)

【実用新案登録請求の範囲】[Scope of utility model registration request] 下端が底部に達するのれん状の一次フイルター
10と、下部流路11aを形成した浮遊物除去板
11を設けて沈澱槽Aを三つの室1,2,3に仕
切り、その第1室の後室1bと第2室2の底に取
手8を備えた出し入れ可能な汚泥かご9を置き、
前記第1室1の前室1aと第3室3の底部を沈泥
が汚泥かご9に流れ落ちるように傾斜させ、且つ
前記第1室の前室1aに〓状の臭気逆流防止用の
流入パイプ5を挿入し、その排水口に邪魔板6を
針金7で吊下すると共に前記第3室3にのれん状
の二次フイルター12を収め且つ排出パイプ13
を接続したことを特徴とする排水処理沈澱槽。
The settling tank A is partitioned into three chambers 1, 2, and 3 by providing a curtain-shaped primary filter 10 whose lower end reaches the bottom and a floating matter removal plate 11 forming a lower flow path 11a, and a rear chamber of the first chamber. A removable sludge basket 9 equipped with a handle 8 is placed at the bottom of 1b and the second chamber 2,
The bottoms of the front chamber 1a of the first chamber 1 and the third chamber 3 are sloped so that the silt flows down into the sludge basket 9, and the front chamber 1a of the first chamber is provided with an inflow pipe shaped like a log to prevent backflow of odor. 5, a baffle plate 6 is suspended from the drain port with a wire 7, a curtain-shaped secondary filter 12 is housed in the third chamber 3, and a discharge pipe 13 is inserted.
A wastewater treatment sedimentation tank characterized by being connected to.
JP16610880U 1980-11-21 1980-11-21 Expired JPS6135201Y2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16610880U JPS6135201Y2 (en) 1980-11-21 1980-11-21

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16610880U JPS6135201Y2 (en) 1980-11-21 1980-11-21

Publications (2)

Publication Number Publication Date
JPS5790711U JPS5790711U (en) 1982-06-04
JPS6135201Y2 true JPS6135201Y2 (en) 1986-10-14

Family

ID=29524765

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16610880U Expired JPS6135201Y2 (en) 1980-11-21 1980-11-21

Country Status (1)

Country Link
JP (1) JPS6135201Y2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP6176955B2 (en) * 2013-03-13 2017-08-09 浩義 井上 Solid-liquid separator
CN107308722A (en) * 2017-07-31 2017-11-03 安徽诺鑫自动化设备有限公司 A kind of Novel filter device for Hydraulic and Hydro-Power Engineering

Also Published As

Publication number Publication date
JPS5790711U (en) 1982-06-04

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