JPS6210681B2 - - Google Patents

Info

Publication number
JPS6210681B2
JPS6210681B2 JP7156082A JP7156082A JPS6210681B2 JP S6210681 B2 JPS6210681 B2 JP S6210681B2 JP 7156082 A JP7156082 A JP 7156082A JP 7156082 A JP7156082 A JP 7156082A JP S6210681 B2 JPS6210681 B2 JP S6210681B2
Authority
JP
Japan
Prior art keywords
water
tank
sludge
sedimentation
storage section
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
JP7156082A
Other languages
Japanese (ja)
Other versions
JPS58189008A (en
Inventor
Tadao Imamura
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.)
Chiyoda Chemical Engineering and Construction Co Ltd
Original Assignee
Chiyoda Chemical Engineering and Construction Co Ltd
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 Chiyoda Chemical Engineering and Construction Co Ltd filed Critical Chiyoda Chemical Engineering and Construction Co Ltd
Priority to JP7156082A priority Critical patent/JPS58189008A/en
Publication of JPS58189008A publication Critical patent/JPS58189008A/en
Publication of JPS6210681B2 publication Critical patent/JPS6210681B2/ja
Granted legal-status Critical Current

Links

Description

【発明の詳細な説明】 本発明は水除濁装置に関し、その目的とする所
は懸濁水の上向流式流動分離槽と、これより隔離
して設けられた沈降濃縮槽とを備えた水除濁装置
において、上向流式流動分離槽内に汚泥溜が長期
間堆積されたままになるのを防止できる水除濁装
置を提供することにある。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a water clarification device, the object of which is to provide a water clarification device that is equipped with an upward flow type flow separation tank for suspended water and a sedimentation concentration tank provided isolated from this. An object of the present invention is to provide a water clarification device that can prevent sludge from remaining accumulated in an upflow type flow separation tank for a long period of time.

従来の水除濁装置は特公昭42―25986号公報に
示されるようなもので、即ち被処理水流入口を下
部に、清澄水流出口を上部にそれぞれ有する懸濁
水の上向流式流動分離槽とこれより隔離して設け
られた沈降濃縮槽と、前記流動分離槽内で被処理
水流入口と清澄水流出口との中間部に上端を開口
させ、その下端を前記沈降濃縮槽に連通させた実
質的に垂直なフロツク沈降管と、該沈降とは別に
下端を前記沈降濃縮槽に連通させた清澄水上昇管
とを設け、該管は前記沈降管の上端より高所で前
記流動分離槽に連通するごとく構成された水除濁
装置であつた。
The conventional water clarifier is as shown in Japanese Patent Publication No. 42-25986, namely, an upward flow type flow separation tank for suspended water, which has an inlet for treated water at the bottom and an outlet for clear water at the top. A sedimentation concentration tank provided separately from this, and a substantially liquid crystal structure having an upper end opened at an intermediate portion between the treated water inlet and the clear water outlet in the fluidic separation tank, and a lower end thereof communicating with the sedimentation concentration tank. A flocculation tube perpendicular to the sedimentation tube is provided, and a clarified water riser tube, which is separate from the sedimentation tube and whose lower end communicates with the sedimentation concentration tank, is provided, and the tube communicates with the fluid separation tank at a higher place than the upper end of the sedimentation tube. It was a water clarification device with a similar structure.

上記水除濁装置においては、流動分離槽内で成
長したフロツクの大部分がフロツク沈降管を経由
して沈降濃縮槽内に汚泥溜として貯溜され、次い
でその汚泥溜は濃縮槽外へ抜き出されるものであ
る。ところが、フロツク中の一部は大型のものに
成長することがあり、これが流動分離槽内の上向
流の流動によつては浮上しえないものとなり、そ
の結果フロツクが流動分離槽と沈降濃縮槽とを隔
離する仕切板上面に汚泥溜として堆積することと
なる。堆積した汚泥溜の一部は流動分離槽内の流
動により細分化されてフロツク沈降管内へ導入さ
れることもあるが、一定量の汚泥溜は長期にわた
つて同じ位置に堆積される結果となる。
In the above-mentioned water clarifier, most of the flocs grown in the fluidized separation tank are stored as a sludge pool in the sedimentation thickening tank via the floc settling pipe, and then the sludge pool is extracted outside the thickening tank. It is something. However, some of the flocs may grow to a large size that cannot be floated to the surface by the upward flow in the fluidized separation tank, and as a result, the flocs are separated from the fluidized separation tank and sedimentation concentration. Sludge accumulates on the top of the partition plate that separates the tank from the sludge pool. A part of the accumulated sludge pool may be fragmented by the flow in the flow separation tank and introduced into the floc settling pipe, but a certain amount of sludge pool will remain in the same position for a long period of time. .

ところで、この汚泥溜が無機物あるいは難醗酵
性の有機物である場合はともかく、汚泥溜が醗酵
性の有機物である場合には、長期間の堆積中に汚
泥溜が醗酵して炭酸ガス、メタンガス、硫化水素
ガス等を発生し、これらガスが気泡となつて流動
分離槽内のフロツクに付着し、これによりフロツ
クの比重が軽くなつて流動分離槽内を上昇し、本
来分離されなければならないフロツクが清澄水に
同伴して清澄水流出口より流出することがあり、
完壁な除濁が行なわれないという不都合があつ
た。
By the way, regardless of whether this sludge pool is made of inorganic substances or organic substances that are difficult to ferment, if the sludge basin is made of fermentable organic substances, the sludge tank ferments during long-term accumulation and produces carbon dioxide gas, methane gas, and sulfide. Hydrogen gas etc. are generated, and these gases become bubbles and adhere to the flocs in the fluidized separation tank, which reduces the specific gravity of the flocs and rises in the fluidic separation tank, clearing the flocs that should originally be separated. It may flow out from the clear water outlet along with the water.
There was an inconvenience that complete turbidity removal was not carried out.

本発明は上記の不都合を解消するため流動分離
槽内に垂直に配設した導入管の被処理水流入口を
フロツク沈降管の上端よりも下方に位置せしめる
と共に、仕切板を漏斗状に形成し、該仕切板に汚
泥貯溜部を組合せ、この汚泥貯溜部に集めた汚泥
を濃縮後、醗酵前に随時系外へ抜き出すことによ
り、完壁な除濁を確保できるようにした水除濁装
置を提供するものである。
In order to solve the above-mentioned problems, the present invention positions the inlet of the water to be treated of the inlet pipe vertically arranged in the fluid separation tank below the upper end of the floc settling pipe, and forms the partition plate in the shape of a funnel. To provide a water turbidity device in which a sludge storage section is combined with the partition plate, and the sludge collected in the sludge storage section is concentrated and then extracted from the system at any time before fermentation, thereby ensuring complete turbidity removal. It is something to do.

次に図面について説明すると、第1図は従来装
置の中央縦断面図であり、符号1は流動分離槽で
あつて、該流動分離槽1の底部近くに被処理水流
入口3が位置するよう導入管2を流動分離槽1内
に配設してあり、4は被処理水流入口3から流入
した被処理水の上向流により流動分離槽内に形成
されるフロツク群体である。
Next, to explain the drawings, FIG. 1 is a central vertical cross-sectional view of a conventional device, in which reference numeral 1 is a fluidic separation tank, and the water to be treated is introduced so that the inlet 3 of the water to be treated is located near the bottom of the fluidic separation tank 1. A pipe 2 is disposed in the fluid separation tank 1, and numeral 4 represents a flock formed in the fluid separation tank by the upward flow of the water to be treated flowing in from the inlet 3 of the water to be treated.

また符号7は流動分離槽1の下部に仕切板8に
て隔離される沈降濃縮槽であり、該沈降濃縮槽7
の底部には排出口15bが設けられている。
Further, reference numeral 7 is a sedimentation concentration tank separated by a partition plate 8 at the lower part of the fluid separation tank 1.
A discharge port 15b is provided at the bottom.

前記流動分離槽1と沈降濃縮槽7間には実質的
に垂直な管または筒よりなるフロツク沈降管5が
配設され、該フロツク沈降管5の上端は流動分離
槽1内に挿入開口しており、下端は沈降濃縮槽7
内に挿入開口されている。
A flocculation tube 5 consisting of a substantially vertical pipe or tube is disposed between the fluidization separation tank 1 and the sedimentation concentration tank 7, and the upper end of the flocculation tube 5 is inserted into the fluidization separation tank 1 and opened. The lower end is the sedimentation concentration tank 7.
There is an opening for insertion inside.

符号6は流動分離槽1内の上部に位置する清澄
水部であり、前記沈降濃縮槽7の頂部と清澄水部
6とが清澄水上昇管9により連通され、清澄水上
昇管9の上端は常にフロツク沈降管5の上端より
さらに高所に開口するよう構成されている。な
お、前記フロツク沈降管5の上端は流動分離槽1
の被処理水流入口3よりも高い位置に開口してい
る。
Reference numeral 6 denotes a clear water section located at the upper part of the fluidic separation tank 1. The top of the sedimentation concentration tank 7 and the clear water section 6 are communicated by a clear water riser pipe 9, and the upper end of the clear water riser pipe 9 is It is constructed so that it always opens higher than the upper end of the floc sedimentation tube 5. Note that the upper end of the flocculation tube 5 is connected to the fluid separation tank 1.
It opens at a higher position than the water inlet 3 to be treated.

第2図乃至第6図は本発明装置の実施例を示す
もので、第2図は仕切板8を漏斗状に形成すると
ともに、その中央付近を凹型に陥設して汚泥貯溜
部11を形成したもので、導入管2を流動分離槽
1の中央付近より垂直に配設し、導入管2の被処
理水流入口3を汚泥貯溜部11に向け、汚泥貯溜
部11の上方には邪魔板12を位置させ、該邪魔
板12を上下動自在に構成して、邪魔板12と汚
泥貯溜部11との間隔を調整自在にしたものであ
る。また、導入管2の被処理水流入口3はフロツ
ク沈降管5の上端よりも下方に伸びている。
2 to 6 show an embodiment of the device of the present invention, and in FIG. 2, the partition plate 8 is formed into a funnel shape, and the sludge storage section 11 is formed by recessing the central part of the partition plate 8 into a concave shape. The introduction pipe 2 is arranged vertically from near the center of the fluid separation tank 1, the water inlet 3 of the introduction pipe 2 is directed toward the sludge storage part 11, and a baffle plate 12 is installed above the sludge storage part 11. The baffle plate 12 is configured to be movable up and down, so that the distance between the baffle plate 12 and the sludge storage section 11 can be adjusted. Further, the water inlet 3 of the introduction pipe 2 extends downward from the upper end of the floc settling pipe 5.

第3図は前図の実施例に掻取翼13a,13b
を加えたもので、その掻取翼13aは汚泥貯溜部
11に隣接する仕切板8付近のフロツクを掻取る
位置に配設され、掻取翼13bは沈降濃縮槽7の
底部付近の汚泥溜を掻取る位置に配設されてい
る。
FIG. 3 shows scraping blades 13a and 13b in the embodiment shown in the previous figure.
The scraping blade 13a is arranged at a position to scrape flocs near the partition plate 8 adjacent to the sludge storage section 11, and the scraping blade 13b scrapes the sludge pool near the bottom of the sedimentation thickening tank 7. It is located at the scraping position.

第4図は漏斗状仕切板8の中央最下端に汚泥流
出用ノズル14を設け、該ノズル下方にバケツト
状汚泥貯溜部11を配設してなるものである。
In FIG. 4, a sludge outflow nozzle 14 is provided at the lowest central end of a funnel-shaped partition plate 8, and a bucket-shaped sludge storage section 11 is provided below the nozzle.

第5図は沈降濃縮槽7を漏斗状に形成し、その
最下端に凹型に陥設してなる汚泥貯溜部11を設
け、仕切板8の最下端に設けた汚泥流出用ノズル
14の下端が前記汚泥貯溜部11の下部まで延び
てなるものである。上記第2図乃至第5図におい
て、汚泥貯溜部11内に堆積した汚泥溜は排出口
15aを経由して系外へ抜き出される。
In FIG. 5, the sedimentation thickening tank 7 is formed into a funnel shape, and a concave sludge storage part 11 is provided at the bottom end of the tank, and the bottom end of the sludge outflow nozzle 14 provided at the bottom end of the partition plate 8 is It extends to the lower part of the sludge storage section 11. In FIGS. 2 to 5, the sludge pool accumulated in the sludge storage section 11 is extracted to the outside of the system via the discharge port 15a.

第6図は漏斗状仕切板8の中央最下端に汚泥流
出用ノズル14を設け、該ノズル下方にバケツト
状汚泥貯溜部11を配設し、一方沈降濃縮槽7に
は底部付近の汚泥溜を掻き取る位置に掻取翼13
bを配設してなるものである。
In FIG. 6, a sludge outflow nozzle 14 is provided at the lowermost end of the center of the funnel-shaped partition plate 8, and a bucket-shaped sludge storage section 11 is provided below the nozzle, while a sludge reservoir near the bottom of the sedimentation thickening tank 7 is provided. Scraping blade 13 at the scraping position
b.

本発明は上記の構成にかかり、被処理水流入口
3より流動分離槽1内に流入した被処理水は、上
向流を生じ槽内に流動するフロツク群体4を形成
する。
The present invention has the above structure, and the water to be treated that flows into the fluid separation tank 1 from the water inlet 3 generates an upward flow and forms a flock 4 that flows into the tank.

また、フロツク群体4を通過して除濁された清
澄水は図中、矢印のごとく上昇し、清澄水部6を
経由して清澄水流出口10より系外へ排出され
る。
Further, the clear water that has passed through the flock group 4 and has been clarified rises as indicated by the arrow in the figure, passes through the clear water section 6, and is discharged from the clear water outlet 10 to the outside of the system.

一方、被処理水より分離されたフロツクはフロ
ツク群体4の空隙率を減少せしめて該フロツク群
体を上昇させ、余剰のフロツクをフロツク沈降管
5の上縁より該管内に落下せしめる。したがつ
て、フロツク群体4をフロツク沈降管5の上端と
一致した位置に保持することができる。フロツク
は沈降管5内を落下して下部の沈降濃縮槽7内に
沈澱堆積し、脱水濃縮せられる。一方、沈降濃縮
槽7内で分離した清浄水は清澄水上昇管9内を上
昇し、流動分離槽1内の清澄水部6に放出され脱
水濃縮された汚泥溜は排出口15bより系外に排
出される。なお、フロツク沈降管5の下端は沈降
濃縮槽7の内部へ余分に突出され、沈降するフロ
ツクの一部が清澄水上昇管9内へ混入することを
防止できる。
On the other hand, the flocs separated from the water to be treated reduce the porosity of the floc mass 4 and cause the floc mass to rise, causing the excess flocs to fall from the upper edge of the floc settling tube 5 into the tube. Therefore, the floc mass 4 can be held at a position that coincides with the upper end of the floc sedimentation tube 5. The flocs fall through the sedimentation tube 5 and are deposited in the sedimentation and concentration tank 7 at the bottom, where they are dehydrated and concentrated. On the other hand, the clean water separated in the sedimentation concentration tank 7 rises in the clear water rising pipe 9, and is discharged into the clear water part 6 in the fluidization separation tank 1, where the dehydrated and concentrated sludge pool is discharged from the system through the discharge port 15b. It is discharged. The lower end of the floc sedimentation tube 5 is extra protruded into the sedimentation concentration tank 7 to prevent part of the flocs from entering the clear water riser tube 9.

また、槽内の被処理水は槽壁とフロツク沈降管
5とにより構成された間隙を上昇するとともにフ
ロツク沈降管5の上端部を境に急激に断面積の拡
大する清澄水部6に達する。一方、運転の継続に
ともないフロツク群体4の空隙率が減少し、上向
流の揚力を受けてフロツク沈降管5の上縁よりさ
らに上方に押し上げられたフロツク群体4の部分
は該上縁を溢流して管内に落下する。
Further, the water to be treated in the tank rises through the gap formed by the tank wall and the floc sedimentation tube 5, and reaches a clear water section 6 whose cross-sectional area rapidly increases from the upper end of the floc sedimentation tube 5 as a boundary. On the other hand, as the operation continues, the porosity of the floc mass 4 decreases, and the portion of the floc mass 4 that is pushed up further above the upper edge of the floc sedimentation tube 5 due to the lifting force of the upward flow overflows the upper edge. It flows and falls into the pipe.

フロツク沈降管5の上方においては、その周辺
を上昇する上向流が存在し、一方フロツク沈降管
5およびこれに連通した沈降濃縮槽7の上部は静
止せる清澄水で充満されているから前記上向流の
影響を蒙ることがない。したがつて、フロツク沈
降管内を落下するフロツクは上向流の影響を受け
ず速やかに沈降しうる。しかして、フロツク沈降
管内をフロツクが充満しつつ沈降すれば、清澄水
とフロツク群体との密度差に基づいてフロツク沈
降管内には下方に向う強い連続した方向流が生ず
る結果、フロツク沈降管の上縁周辺には強い吸引
力を生じ、余剰のフロツクをフロツク沈降管内へ
効果的に吸引しうるものである。また、前記方向
流とフロツクの重力方向とが一致するため、フロ
ツクは高速度をもつてフロツク沈降管内を流下す
るとともに、沈降濃縮槽7の頂部には清澄水上昇
管9が配されているから、沈降濃縮槽内に沈降す
るフロツクが同伴する清澄水と該フロツクが沈澱
堆積する際に排斥する清澄水とを該上昇管9を通
して流動分離槽1の清澄水部6へ放流しうるもの
である。よつて装置内には、フロツク沈降管5を
下方へ向け、沈降濃縮槽7を経て清澄水上昇管9
を上方に向かう実質的な水流が発生している。
Above the floc sedimentation tube 5, there is an upward flow rising around it, while the upper part of the floc sedimentation tube 5 and the sedimentation thickening tank 7 connected thereto is filled with still clear water. It is not affected by countercurrent. Therefore, the flocs falling in the floc settling tube are not affected by the upward flow and can quickly settle. Therefore, if the floc sedimentation tube is filled with flocs, a strong continuous downward flow is generated in the floc sedimentation tube based on the density difference between the clear water and the floc population, and as a result, the floc sedimentation tube is A strong suction force is generated around the edge, and excess floc can be effectively sucked into the floc sedimentation tube. Furthermore, since the directional flow coincides with the direction of gravity of the flocs, the flocs flow down the floc sedimentation tube at a high velocity, and a clear water riser tube 9 is disposed at the top of the sedimentation concentration tank 7. The clear water accompanied by the flocs settling in the sedimentation concentration tank and the clear water rejected when the flocs settle and accumulate can be discharged into the clear water section 6 of the flow separation tank 1 through the riser pipe 9. . Therefore, inside the device, the flocculation tube 5 is directed downward, and the clear water riser tube 9 passes through the sedimentation concentration tank 7.
There is a substantial upward flow of water.

ところで、仕切板8の上面にフロツクが汚泥溜
として堆積するような場合には、その汚泥溜が汚
泥貯溜部11に集められるから、その汚泥溜は排
出口15aを経由して系外へ抜き出すことが可能
である。
By the way, when flocs accumulate as a sludge pool on the upper surface of the partition plate 8, the sludge pool is collected in the sludge storage section 11, so that the sludge pool can be extracted out of the system via the discharge port 15a. is possible.

さらに、汚泥貯溜部11の上方に邪魔板12を
設けてあるので、流動分離槽1内の上向流により
汚泥貯溜部11に貯溜された汚泥溜が再度流動分
離槽に巻き上げられるのを防止することができ、
かつ邪魔板12を上下動自在式にしておけば、上
記汚泥溜の堆積量に応じて邪魔板12と汚泥貯溜
部11間の間隔を調整することができ、汚泥溜の
濃縮をより効率的に行えることとなる。
Furthermore, since the baffle plate 12 is provided above the sludge storage section 11, the sludge pool stored in the sludge storage section 11 is prevented from being rolled up into the fluidization separation tank again due to the upward flow within the fluidization separation tank 1. It is possible,
In addition, if the baffle plate 12 is made vertically movable, the distance between the baffle plate 12 and the sludge storage section 11 can be adjusted according to the amount of accumulation in the sludge pool, and the concentration of the sludge pool can be made more efficient. It can be done.

また、仕切板8を漏斗状に形成してあるので、
フロツクの集泥効率が向上し、さらに掻取翼13
a,13bを用いれば一層集泥効率を高めること
も可能である。
In addition, since the partition plate 8 is formed into a funnel shape,
The mud collection efficiency of the floc is improved, and the scraping blade 13
By using a and 13b, it is possible to further improve the mud collection efficiency.

次いで、第4図の例では仕切板の最下端に汚泥
流出用ノズル14を設け、バケツト状の汚泥貯溜
部11を該ノズル14の下方に配設しノズル14
の下端を汚泥貯溜部11の中央下部に位置せしめ
たので、該汚泥貯溜部11に蓄積した汚泥により
流動分離槽1をシールし、沈降濃縮槽7と隔離し
ているため、流動分離槽1内の上向流により汚泥
溜が巻き上げられるのを防ぐ効果がある。また、
第5図の例では汚泥貯溜部11のみから汚泥を排
出するので、全体の構造が簡単で、操作も容易と
なり、設備費が減少する。よつて本発明によれ
ば、汚泥溜を長期間にわたり同じ位置に堆積させ
ないので、醗酵性有機物を含む被処理水を扱う場
合であつても、フロツクを清澄水と一緒に流出さ
せるようなことがなく、完壁な除濁が達成できる
というすぐれた効果がある。
Next, in the example shown in FIG. 4, a sludge outflow nozzle 14 is provided at the lowest end of the partition plate, and a bucket-shaped sludge storage section 11 is provided below the nozzle 14.
Since the lower end is located at the lower center of the sludge storage section 11, the fluid separation tank 1 is sealed by the sludge accumulated in the sludge storage section 11 and is isolated from the sedimentation thickening tank 7. This has the effect of preventing the sludge pool from being rolled up by the upward flow of water. Also,
In the example shown in FIG. 5, sludge is discharged only from the sludge storage section 11, so the overall structure is simple, operation is easy, and equipment costs are reduced. Therefore, according to the present invention, the sludge pool is not allowed to accumulate in the same position for a long period of time, so even when treating water containing fermentable organic matter, there is no possibility that the sludge will flow out together with clear water. It has the excellent effect of achieving complete turbidity removal.

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

第1図は従来装置の中央縦断面図、第2図乃至
第6図は本発明の実施例を示した中央縦断面図で
ある。 1……流動分離槽、2……導入管、3……被処
理水流入口、4……フロツク群体、5……フロツ
ク沈降管、6……清澄水部、7……沈降濃縮槽、
8……仕切板、9……清澄水上昇管、10……清
澄水流出口、11……汚泥貯溜部、12……邪魔
板、13a,13b……掻取翼、14……ノズ
ル、15a,15b……排出口。
FIG. 1 is a central vertical cross-sectional view of a conventional device, and FIGS. 2 to 6 are central vertical cross-sectional views showing embodiments of the present invention. DESCRIPTION OF SYMBOLS 1... Fluid separation tank, 2... Inlet pipe, 3... Water to be treated inlet, 4... Floe mass, 5... Floe settling tube, 6... Clear water section, 7... Sedimentation concentration tank,
8... Partition plate, 9... Clear water riser pipe, 10... Clear water outlet, 11... Sludge storage section, 12... Baffle plate, 13a, 13b... Scraping blade, 14... Nozzle, 15a, 15b...Exhaust port.

Claims (1)

【特許請求の範囲】 1 被処理水流入口を下部に、清澄水流出口を上
部にそれぞれ有する懸濁水の上向流式流動分離槽
と、これより隔離して設けられた沈降濃縮槽と、
前記流動分離槽内で被処理水流入口と清澄水流出
口との中間部に上端を開口させ、その下端を前記
沈降濃縮槽に連通させた実質的に垂直なブロツク
沈降管と、該沈降管とは別に下端を前記沈降濃縮
槽に連通させた清澄水上昇管とを設け、該管は前
記沈降管の上端より高所で前記流動分離槽に連通
するごとく構成された水除濁装置において、流動
分離槽内に垂直に配設した導入管の被処理水流入
口をフロツク沈降管の上端よりも下方に位置せし
め、かつ前記流動分離槽と前記沈降濃縮槽とを隔
離する仕切板を漏斗状に形成するとともに該仕切
板に汚泥貯溜部を組合せ、該汚泥貯溜部に排出口
を設け、さらに該汚泥貯溜部の上方に邪魔板を設
置したことを特徴とする水除濁装置。 2 仕切板の中央付近を凹型に陥設して汚泥貯溜
部を形成してなる特許請求の範囲第1項記載の水
除濁装置。 3 仕切板の最下端に汚泥流出用ノズルを設け、
該ノズル下方にバケツト状汚泥貯溜部を配設し該
ノズルの下端を該貯溜部の下部に位置せしめてな
る特許請求の範囲第1項記載の水除濁装置。 4 沈降濃縮槽を漏斗状に形成し、その最下端に
凹型に陥設してなる汚泥貯溜部を設け、仕切板の
最下端に設けた汚泥流出用ノズルの下端が前記汚
泥貯溜部の一部まで延びてなる特許請求の範囲第
1項記載の水除濁装置。
[Scope of Claims] 1. An upward flow type flow separation tank for suspended water having a treated water inlet at the bottom and a clear water outlet at the top, and a sedimentation concentration tank provided isolated from this,
A substantially vertical block sedimentation tube whose upper end is opened at an intermediate portion between the treated water inlet and the clear water outlet in the fluid separation tank and whose lower end is communicated with the sedimentation concentration tank; In a water clarification device, a clear water riser pipe is separately provided, the lower end of which communicates with the sedimentation concentration tank, and the pipe is configured to communicate with the flow separation tank at a higher place than the upper end of the sedimentation pipe. The inlet of the water to be treated of the inlet pipe vertically arranged in the tank is located below the upper end of the floc sedimentation tube, and a partition plate is formed in the shape of a funnel to isolate the fluid separation tank and the sedimentation concentration tank. A water clarification device, characterized in that a sludge storage section is combined with the partition plate, a discharge port is provided in the sludge storage section, and a baffle plate is further installed above the sludge storage section. 2. The water clarifier according to claim 1, wherein the partition plate is recessed near the center to form a sludge reservoir. 3 Install a sludge outflow nozzle at the bottom end of the partition plate,
2. The water clarifier according to claim 1, wherein a bucket-shaped sludge reservoir is disposed below the nozzle, and the lower end of the nozzle is positioned below the reservoir. 4 The sedimentation thickening tank is formed into a funnel shape, and a concave sludge storage section is provided at the bottom end of the tank, and the lower end of the sludge outflow nozzle provided at the bottom end of the partition plate is a part of the sludge storage section. A water clarification device according to claim 1, which extends to.
JP7156082A 1982-04-30 1982-04-30 Apparatus for removing turbidity of water Granted JPS58189008A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7156082A JPS58189008A (en) 1982-04-30 1982-04-30 Apparatus for removing turbidity of water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7156082A JPS58189008A (en) 1982-04-30 1982-04-30 Apparatus for removing turbidity of water

Publications (2)

Publication Number Publication Date
JPS58189008A JPS58189008A (en) 1983-11-04
JPS6210681B2 true JPS6210681B2 (en) 1987-03-07

Family

ID=13464222

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7156082A Granted JPS58189008A (en) 1982-04-30 1982-04-30 Apparatus for removing turbidity of water

Country Status (1)

Country Link
JP (1) JPS58189008A (en)

Families Citing this family (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61129011A (en) * 1984-11-29 1986-06-17 Japan Organo Co Ltd Floc blanket type flocculative sedimentation apparatus
JPH0227844Y2 (en) * 1985-09-13 1990-07-26
JP3856307B2 (en) 2002-06-06 2006-12-13 株式会社荏原製作所 Coagulation sedimentation method and apparatus
JP4747191B2 (en) * 2008-07-24 2011-08-17 住友重機械エンバイロメント株式会社 Coagulation sedimentation apparatus and coagulation sedimentation processing method
JP5916535B2 (en) * 2012-06-27 2016-05-11 株式会社東洋製作所 Muddy water solid-liquid separator
WO2014171421A1 (en) * 2013-04-16 2014-10-23 住友重機械エンバイロメント株式会社 Solid-liquid separation apparatus and solid-liquid separation method
WO2018155524A1 (en) * 2017-02-24 2018-08-30 オルガノ株式会社 Flocculation device
US11406919B2 (en) 2017-02-24 2022-08-09 Organo Corporation Flocculation and sedimentation apparatus
JP7045881B2 (en) * 2017-02-24 2022-04-01 オルガノ株式会社 Coagulation sedimentation device

Also Published As

Publication number Publication date
JPS58189008A (en) 1983-11-04

Similar Documents

Publication Publication Date Title
JPS62262798A (en) Apparatus for anaerobic purification of waste water
US4988441A (en) Clarification apparatus
JPS6210681B2 (en)
KR101170572B1 (en) Precipitation tank
CN210114860U (en) Vertical flow type sedimentation tank
LT5160B (en) Method of separating suspension, in particular for waste water treatment, and an apparatus for performing the same
JP3681003B2 (en) Suspension separation method, suspension separator, sedimentation channel module, suspension separator unit
JP3374766B2 (en) Anaerobic treatment equipment for organic wastewater
HUT69510A (en) Settling tank with oil separator
CN115608009A (en) Assembled secondary sedimentation tank and sewage treatment equipment
CN206288999U (en) One kind cone bottom skewed culvert filter residue air floatation machine
US4515698A (en) Liquid clarifying apparatus and methods
CN109331506A (en) Vertical sedimentation tank
TW313560B (en)
CN209679570U (en) A kind of vertical sedimentation tank
CN207567085U (en) The device that a kind of scum silica frost sediment sub-prime concentration is arranged clearly
KR100545746B1 (en) Improved structure sedimentation tank with excellent sludge settling efficiency and water treatment efficiency
JP3882464B2 (en) Sedimentation tank
CN215232310U (en) Sewage treatment is with straining hydrophone
CN211611729U (en) Vertical flow sedimentation tank
CN220867257U (en) Concentrating and separating tank suitable for low-concentration slurry
CN2475727Y (en) Airfloat sewage treatment device
CN212974422U (en) High-efficient vertical integrative equipment of oil-water separation that deposits
CN220976662U (en) Inclined plate oil separation tank
CN211595177U (en) Inverted cone up-flow anaerobic sludge reaction device