JPS58189008A - Apparatus for removing turbidity of water - Google Patents

Apparatus for removing turbidity of water

Info

Publication number
JPS58189008A
JPS58189008A JP7156082A JP7156082A JPS58189008A JP S58189008 A JPS58189008 A JP S58189008A JP 7156082 A JP7156082 A JP 7156082A JP 7156082 A JP7156082 A JP 7156082A JP S58189008 A JPS58189008 A JP S58189008A
Authority
JP
Japan
Prior art keywords
water
tank
sludge
sedimentation
partition plate
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
JP7156082A
Other languages
Japanese (ja)
Other versions
JPS6210681B2 (en
Inventor
Tadao Imamura
今村 忠夫
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 Corp
Chiyoda Chemical Engineering and Construction Co Ltd
Original Assignee
Chiyoda Corp
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 Corp, Chiyoda Chemical Engineering and Construction Co Ltd filed Critical Chiyoda Corp
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

Abstract

PURPOSE:To make it possible to withdraw accumulated flocs out of a system at any time, in an apparatus for removing the turbidity of water consisting of an upwardly flowing type fluidized separation tank and a precipitative concentration tank partitioned by a partition wall, by providing a sludge storing part equipped with a discharge port to the partition plate. CONSTITUTION:Water to be treated is flowed into the bottom part of a fluidized separation tank 1 from an inflow port 3 through an introducing pipe 2 and a fluidized bed 3 comprising flocs is formed in the tank 1 by the upwardly directed stream of water to be treated. Flocs are precipitated to a precipitative concn. tank 7 through a precipitation pipe 5 while clarified water is rised through a riser pipe 9. The partition plate 8 of the separation tank 1 and the concn. tank 7 is formed into a funnel shape and a sludge storing part 11 is formed in the vicinity of the center thereof. By this structure, because flocs incapable of being floated by the upwardly directed stream in the separation tank 1 are not accumulated on the partition plate and precipitated to the storing part 11, there is no generation of a carbon dioxide gas, a methane gas or a hydrogen sulfide gas due to fermentation of sludge resulting from long-term accumulation and the perfect removal of turbidity can be carried out.

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、これ鼾より隔離して設けられ
九沈降濃縮槽とを備えた水除鵠装置において、上向流式
流動分離槽内に汚泥溜か長期間堆積されたままになるの
を防止できる水除濁装叡を提供することにある。
[Detailed Description of the Invention] The present invention relates to a water turbidity device, the object of which is to include an upward flow type flow separation tank for suspended water and a sedimentation concentration tank provided isolated from this from the snoring area. To provide a water turbidity device capable of preventing sludge from remaining accumulated in an upflow flow separation tank for a long period of time in a water filtration device.

従来の水除燗装置は特公昭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
流虻分[僧とこむより隔離して設けられた沈降濃虹槽と
、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ック沈降管と、該沈降
とは別に下端を前記沈降−縮Mに]!!!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t&蛎分離槽に連通するごとく構成された水除陶装
置であった。
The conventional water smelting device is as shown in Japanese Patent Publication No. 42/-25986, that is, the inlet of the water to be treated is located at the bottom.
Upward flow type flow separation of suspended water, each having a clear water outlet at the top [a sedimentation tank installed separately from the monk and the water separation tank, and an inlet for treated water and an outlet for clear water in the flow separation tank] A substantially vertical floc sedimentation tube having an upper end opened in the middle part thereof and a lower end thereof communicating with the sedimentation concentration tank; ! ! The water removal device was equipped with a riser pipe for clear water, and the pipe was configured to communicate with the T & oyster separation tank at a higher place than the upper end of the settling pipe.

上紀水除滴装置1においては、流動分離槽内で成長した
フロックの大部分がフロック沈降管を経由[、て沈降I
M細槽内に汚泥溜として貯溜され、次いでその汚泥溜は
嬢砺簿外へ抜き出されるものである。ところか、フロッ
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っては浮上しえないも
のとなり、その結果フロッ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ッ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って同じ位置に堆積
される結果となる。
In the Joki water removal device 1, most of the flocs grown in the fluid separation tank pass through the floc sedimentation tube [, and sedimentation I
The sludge is stored as a sludge in the M tank, and then the sludge is taken out of the storage room. However, some of the flocs may grow to a large size that cannot be floated up by the upward flow in the fluidized separation tank, and as a result, the flocs are separated from the fluidized separation tank and the sedimentation thickener. The sludge accumulates on the top surface of the partition plate that separates the sludge. A part of the accumulated sludge pool may be fragmented by the flow in the flow separation tank and introduced into the floc settling tube, but a certain amount of the sludge pool ends up being deposited in the same position for a long time.

ところで、この汚泥溜が無機物あるいは錬醗酵性の有機
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jらガ
スが気泡となって流動分離槽内の70ツクに付着し、こ
れによりフロックの比重が軽くなって流動外1i41内
を上昇し、本来分離されなければならないフロックが清
澄水に同伴して清澄流出口より流出することがあ沙、完
壁な除濁が行なわれないという不都合があった。
By the way, regardless of whether this sludge basin is made of inorganic substances or fermentable organic substances, if the sludge basin is made of fermentable organic substances, the sludge basin 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 70 pieces in the fluid separation tank, which reduces the specific gravity of the flocs and rises inside the fluid outside 1i41, which should originally be separated. There is an inconvenience that the flocs may flow out from the clearing outlet along with the clear water, and complete turbidity removal cannot be performed.

本発明は上記の不都合を解消するため仕切板に汚泥貯溜
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だ水除〜装at提供するものである
In order to solve the above-mentioned problems, the present invention combines a sludge storage section with a partition plate, and after concentrating the sludge collected in this sludge storage section, it is extracted from the system at any time before fermentation, thereby achieving complete turbidity removal. We will provide water removal and equipment to ensure this.

次に図rkJについて説明すると、第1図は従来装置の
中央W断面図であり、符号1は流動分離槽であって、該
流動外111槽1の底部近くに被処理水流入口S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
Fi被処理水流入口6から流入し九被処理水の上向流に
より流動力M借内に形成されるフロック群体である。
Next, referring to Fig. rkJ, Fig. 1 is a cross-sectional view of the center W of the conventional apparatus, and reference numeral 1 is a fluidic separation tank, and the inlet S of the water to be treated is located near the bottom of the external fluidic 111 tank 1. A similar introduction pipe 2 is arranged in the fluid separation tank 1, and 4
Fi is a flock of flocs that flows in from the inlet 6 of the water to be treated and is formed by the flow force M due to the upward flow of the water to be treated.

また符号7は流動分離4111の下部に仕切板8(てg
4離される沈降濃縮槽であり、該沈降濃縮槽7の庶W6
には排出口15bが設けられている。
Also, reference numeral 7 indicates a partition plate 8 (te g
4 is a sedimentation concentration tank separated from the sedimentation concentration tank 7, and the bottom W6 of the sedimentation concentration tank 7 is
is provided with a discharge port 15b.

前記流動外11と沈降濃縮槽7間には実質的に垂直な管
またVi筒よりなるフロック沈降管5が配設され、該フ
ロック沈降管5の上−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 floc sedimentation tube 5 made of a substantially vertical pipe or a Vi cylinder is disposed between the flow outside 11 and the sedimentation concentration tank 7, and the upper part of the floc sedimentation tube 5 is inserted into the fluid separation tank 1 and opened. The lower end is inserted into the sedimentation concentration tank 7 and opened.

符号6Fi流動分離槽1内の上部に位置する清澄木部で
あり、前記沈降S縮僧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
70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、前記フロック沈降管5の上端は
流動分離槽1の被処理水流入口5よりも高い位置に開口
している。
The code 6Fi is the clear wood located at the upper part of the fluidic separation tank 1, and the top of the sedimentation S-condenser 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 70-tub sedimentation tube 5. Note that the upper end of the floc settling tube 5 opens at a higher position than the inlet 5 of the water to be treated in the fluid separation tank 1.

第2図は本発明装置の一実施例の中央縦断面図であり、
仕切板8の中央付近を凹mに陥設して汚泥貯溜部11を
形成したものである。
FIG. 2 is a central vertical sectional view of an embodiment of the device of the present invention;
A sludge storage section 11 is formed by recessing the center of the partition plate 8 into a concave m.

第5図乃至第7図は本発明装置の他の実施例を示すもの
で、第S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を流動外11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S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f11板12を上下動自在に構成して、邪魔板1
2と汚泥貯溜部11との間隔を調整自在にしたものであ
る。
5 to 7 show other embodiments of the apparatus of the present invention, and in FIG. S, the partition plate 8 is formed into a funnel shape, and the central part thereof is recessed to form a sludge storage section 11. The introduction pipe 2 is arranged vertically from near the center of the flow outside 11, the inlet S of the water to be treated of the introduction pipe 2 is directed towards the sludge storage part 11, and a baffle plate is installed above the sludge storage part 11. 12, and the baffle plate 1 is configured to be movable up and down.
2 and the sludge storage section 11 can be freely adjusted.

第4図は前図の実施例に掻取111113m、13bを
加えたもので、その掻取翼151は汚泥貯溜部11に隣
接する仕切板8付近の70ツクを掻取る位置にi、設さ
れ、掻取翼15bは沈降製動(′J7の底部付近の汚泥
溜を掻取る位置に配設されている。
FIG. 4 shows the embodiment shown in the previous figure with scrapers 111113m and 13b added, and the scraping blade 151 is installed at a position i to scrape 70 pieces near the partition plate 8 adjacent to the sludge storage section 11. The scraping blade 15b is disposed at a position to scrape the sludge pool near the bottom of the sedimentation drive ('J7).

第5同Fi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、該ノズル下方にパケット状汚泥貯溜部
11を配設してなるものである。
A sludge outflow nozzle 14 is provided at the lowest center end of the fifth Fi funnel-shaped partition plate 8, and a packet-shaped sludge storage section 11 is provided below the nozzle.

第6図は沈降濃縮PII7と漏斗状に形成し、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11w部11の下・部まで低びてなるものである。
In FIG. 6, the sedimentation concentration PII 7 is formed into a funnel shape, and a concave sludge storage part 11 is provided at the bottom end of the funnel, and the bottom end of the sludge outflow nozzle 14 provided at the bottom end of the partition plate 8 is The sludge 11w extends down to the bottom of the section 11.

上記第2図乃至第6図において、汚泥貯溜部11内に堆
積した汚泥溜は排出口15&を経由して糸外へ抜き出さ
れる。
In FIGS. 2 to 6, the sludge accumulated in the sludge storage section 11 is extracted to the outside of the thread via the discharge port 15&.

第7図は漏斗状仕切&8の中央最下端に汚泥流田川ノズ
ル14を設け、該ノズル下方にパケット状汚泥貯溜部1
1な配設し、一方沈降濃縮槽7にVi底部付近の汚泥溜
を掻き取る位W!に掻取翼15bを配設し7てなるもの
である。
In Fig. 7, a sludge flow Tagawa nozzle 14 is provided at the lowermost end of the center of the funnel-shaped partition &8, and a packet-shaped sludge storage section 1 is provided below the nozzle.
1 arrangement, and on the other hand, the sludge pool near the bottom of the Vi is scraped off in the sedimentation thickening tank 7! A scraping blade 15b is disposed on the blade 7.

本発明は上記の構成にかかり、被処理水流入口Sより流
動分11内に流入した被処理水は、上向流を生じ槽内に
流動するフロック群体4を形成するO ま九、フロック群体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W66を経由して清澄
水流出口10より糸外へ排出される。
The present invention has the above-mentioned configuration, and the water to be treated that flows into the flow portion 11 from the water inlet S to be treated forms an upward flow and forms a flock of flocs 4 that flows into the tank. The clear water that has passed through and has been turbid rises as shown by the arrow in the figure, and is discharged to the outside of the thread from the clear water outlet 10 via the clear water W66.

一方、被処理水より分離されたフロックは70ツク群体
4の□空隙率を減少せしめて該フロック群体を上昇させ
、余剰のフロックを70ツク沈降管5の上縁よシ該管内
に落下せしめる。したがって、フロック群体4を70ツ
ク沈降管5の上端を一致した位置に保持することができ
る。フロックは沈降管5内を落下して下部の沈降濃&I
稽7内に沈澱堆積し、脱水濃縮せられる。一方、沈降濃
縮M7内で分離した清澄水上昇管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より糸外に排出される。なお、フロック
沈降管5の下端は沈降−縮檜7の内部へ余分に突出され
、沈降するフロッ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 70-piece colony 4 and cause the floc group to rise, causing the excess flocs to fall from the upper edge of the 70-piece settling tube 5 into the tube. Therefore, it is possible to hold the floc group 4 at the same position as the upper end of the sedimentation tube 5 by 70 pieces. The flocs fall through the sedimentation tube 5 and settle into the sediment concentration &I at the bottom.
Precipitates are deposited in the tank and are dehydrated and concentrated. On the other hand, the clear water separated in the sedimentation concentration M7 rises in the riser pipe 9, is discharged into the clear water section 6 in the fluidized separation tank 1, and the dehydrated and concentrated sludge pool is discharged to the outside of the thread from the discharge port 15b. The lower end of the floc sedimentation tube 5 is extra protruded into the sedimentation-cured cypress 7 to prevent a 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70ツク沈降管:□11 5とにより構成された間隙を上昇するとともに70ツク
沈降管5の上端部を境に、11激に断面積の拡大する清
澄水部641:繍する。一方、運転の継&ecともない
フロック群体4の空1lI4Aが減少し、上向流の揚力
を受けてフロック沈降l#5の上縁よりさらに上方に押
し上げられたフロック群体40部分は該上縁を溢流して
管内に落下する。
In addition, the water to be treated in the tank rises through the gap formed by the tank wall and the 70-tsuk sedimentation pipe: □115, and the cross-sectional area expands dramatically at the upper end of the 70-tsukuk settling pipe 5. Clear water section 641: Stitch. On the other hand, as the operation progresses, the empty space 1lI4A of the floc colony 4 decreases, and the part of the floc colony 40 that is pushed up further above the upper edge of the floc sedimentation l#5 due to the lifting force of the upward flow overflows the upper edge. It flows and falls into the pipe.

フロック沈降t5の上方においては、その周辺を上昇す
る上向流が存在し、一方フロック沈降管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1輪な象ることがない。した
がって、フロック沈降管内を落下するフロックは上向流
の1愉を受けず速やかに沈降しつる。しかし、で、フロ
ック沈降管内を70ツクが充満しつつ沈降すれば、1w
澄水とフロック群体との密度差に基づいてフロック沈降
管内には下方に向う強い連続した方向流が生ずる結果、
フロック沈降管の上縁周辺には強い吸引力を生じ、余剰
の70ツクをフロック沈降管内へ効果的&:@引しつる
ものである。また、前記方向流と70ツクの重力方向と
が一致するため、フロックは高速度をもってフロック沈
降管内を流下するとともに1沈降#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
するフロックが同伴する清澄水と該フロック゛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へ放流しつるものである。よって
装置内には、フロック沈降管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 t5, there is an upward flow that rises around the area, while the upper part of the floc sedimentation tube 5 and the sedimentation concentration tank 7 connected thereto is filled with still clear water. I can never imagine a flow of flow. Therefore, the flocs falling through the floc settling tube are not affected by the upward flow and quickly settle. However, if the floc sedimentation tube is filled with 70 flocs and settles, 1w
Based on the density difference between the clear water and the floc colony, a strong continuous downward directional flow is generated in the floc settling tube.
A strong suction force is generated around the upper edge of the floc sedimentation tube, effectively pulling the excess 70 pieces into the floc sedimentation tube. In addition, since the directional flow and the direction of gravity of 70 points coincide, the flocs flow down in the floc settling tube at high speed, and a clear water riser tube 9 is disposed at the top of the 1 settling # condenser tank 7. The clear water accompanied by the flocs settling in the sedimentation concentration tank and the clear water rejected when the flocs are deposited are discharged into the clear water section 6 of the fluidic separation tank 1 through the riser pipe 9. . Therefore, a substantial water flow is generated within the apparatus, which directs the floc sedimentation tube 5 downward, passes through the sedimentation concentration tank 7, and heads upward through the clear water riser tube 9.

ところで、仕切板8の上面に70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Fi排出口15mを経由し
て系外へ抜き出すことが可能である。
By the way, if 70 pieces of sludge accumulate on the upper surface of the partition plate 8 as a sludge pool, the sludge pool will be collected in the sludge storage section 11 and will be extracted from the system via the sludge pool Fi discharge port 15m. Is possible.

さらに、汚泥貯溜部11の上方に邪魔板12ft設けて
おけば、流動分離槽1内の上向流により汚泥貯ffM部
11&:貯舖された汚泥溜が再度流動分離mに巻き上げ
られるのを防止することかでき、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幼木的に行えることとなる。
Furthermore, by providing a 12ft baffle plate above the sludge storage section 11, it is possible to prevent the sludge storage ffM section 11 &: stored sludge pool from being rolled up into the fluidization separation m again due to the upward flow within the fluidization separation tank 1. 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 improved. can be done more like a young tree.

ま九、仕切板8を漏斗状に杉成しておくと、フロックの
集泥効率が向上し掻取板1!+a、15bを用いれば一
階集泥効率を高めることも可能である。
Ninth, if the partition plate 8 is formed into a funnel shape, the efficiency of floc collection will improve and the scraping plate 1! If +a and 15b are used, it is also possible to increase the first-floor mud collection efficiency.

次いで、第5図の例では仕切板の最下端に汚泥流田川ノ
ズル14を設け、パケット状の汚泥貯溜r!/6+1を
該ノズル14の下方に配設置ノズル14の下端を汚泥貯
溜部11の中央下f!i6に位置せしめたので、該汚泥
貯溜部11に蓄槽した汚泥により流動分離層1をシール
し、沈降#I縮層7と隔離しているので流動分11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6図の例では汚泥貯MI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。よって本発明によれば、汚泥
層を長期間にわAり同じ位置[jl:積させない・シ 
 1 で、醗酵性有機物を含む被処理水を扱う場合であっても
、フロッ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4成できるというすぐれた効果がある
Next, in the example shown in FIG. 5, a sludge flow nozzle 14 is provided at the bottom end of the partition plate, and a packet-shaped sludge storage r! /6+1 is placed below the nozzle 14. The lower end of the nozzle 14 is placed below the center of the sludge storage section 11 f! i6, the sludge stored in the sludge storage section 11 seals the fluidized separation layer 1 and separates it from the sedimentation #I condensation layer 7, so the upward flow in the fluidized portion 11 prevents the sludge pool from forming. It has the effect of preventing it from being rolled up. Further, in the example shown in FIG. 6, sludge is discharged only from the sludge storage MI section 11, so the overall structure is simple, operation is easy, and equipment costs are reduced. Therefore, according to the present invention, the sludge layer is kept at the same position for a long period of time [jl: not allowed to accumulate;
1. Even when treating water containing fermentable organic matter, flocs do not flow out together with clear water, and there is an excellent effect of complete turbidity removal.

【図面の簡単な説明】 第1図は従来装置の中央縦断面図、第2図乃至第7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 管5・・・被処
理水流入口  4−=7’/り群体5・−70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  1o・・・清澄水
流出口11・・汚泥貯溜l9612−・邪魔板1!5N
、15b・・・掻取II  14− ノズル15a、1
5b−・排出口
BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a central vertical cross-sectional view of a conventional device, and FIGS. 2 to 7 are central vertical cross-sectional views showing embodiments of the present invention. 1... Fluid separation tank 2- Conduit 5... Treated water inlet 4-=7'/group 5-70 sedimentation tube 6... Clear water section 7... Sedimentation concentration tank 8.
... Partition plate 9 ... Clear water riser pipe 1o ... Clear water outlet 11 ... Sludge storage l9612 - Baffle plate 1!5N
, 15b...Scraping II 14- Nozzle 15a, 1
5b-・Discharge 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&i檜に連通させた
実實的に垂直な70ツク沈降管と、該沈降管とは別に下
端を萌紀沈降lli細槽に連通させた清澄水上昇管とを
設け、該管ii前記沈降管の上端より高所で前記流動分
離fII(連通するごとく構成された水除燗装置におい
て、前記流動分離槽と前記沈降濃&if#IとをvJl
Ilmlする仕切板に汚泥貯溜部を組合せ、該汚泥貯溜
部に排出口を設けたことな特徴とする水除濁装置、 (21仕切板を漏斗状にV/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填紀駅の水除濁装置。 (4)  仕切板の最下端に汚泥流出用ノズルを設は該
ノズル下方にパケット状汚泥貯溜部を配e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。 (5)  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L’ 14
部の一部まで低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 that has a treated water inlet at the bottom and a clear water outlet at the top, and a sedimentation concentration tank that is isolated from this tank; A practically vertical 70-tube sedimentation tube having an upper end opened at an intermediate portion between the treated water inlet and the clear water outlet in the fluid separation tank and communicating the lower end with the sedimentation cypress, and the sedimentation tube. Separately from the pipe, there is provided a clear water riser pipe whose lower end communicates with the Moeki sedimentation tank, and at a higher place than the upper end of the sedimentation pipe, the flow separation fII (a water removal pipe configured so as to communicate) is provided. In the apparatus, the fluid separation tank and the sedimentation concentration &if#I are set at vJl.
A water clarifier, characterized in that a sludge storage section is combined with a partition plate that separates the sludge, and a discharge port is provided in the sludge storage section. The water clarification device according to claim 1. (3) The water clarification device for the first Saiki station as claimed in claim 1, wherein the partition plate is recessed near the center to form a sludge storage section. (4) A sludge outflow nozzle is provided at the lowermost end of the partition plate, and a packet-shaped sludge reservoir is disposed below the nozzle, and the lower end of the nozzle is positioned below the reservoir. Water clarifier. (5) 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 bottom end of the sludge outflow nozzle provided at the bottom end of the partition plate is The sludge L' 14
2. The water clarifier according to claim 1, wherein the water clarifier is lowered to a part of the water.
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 true JPS58189008A (en) 1983-11-04
JPS6210681B2 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)

Cited By (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
JPS6250711U (en) * 1985-09-13 1987-03-30
WO2003104151A1 (en) * 2002-06-06 2003-12-18 株式会社荏原製作所 Method and device for flocculating setting
JP2010023008A (en) * 2008-07-24 2010-02-04 Sumitomo Heavy Industries Environment Co Ltd Flocculation and sedimentation apparatus and flocculation and sedimentation method
JP2014004569A (en) * 2012-06-27 2014-01-16 Toyo Eng Works Ltd Solid-liquid separation apparatus for muddy water
JPWO2014171421A1 (en) * 2013-04-16 2017-02-23 住友重機械エンバイロメント株式会社 Solid-liquid separation device and solid-liquid separation method
WO2018155524A1 (en) * 2017-02-24 2018-08-30 オルガノ株式会社 Flocculation device
JP2018140389A (en) * 2017-02-24 2018-09-13 オルガノ株式会社 Coagulator
US11406919B2 (en) 2017-02-24 2022-08-09 Organo Corporation Flocculation and sedimentation apparatus

Cited By (12)

* 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
JPH0462762B2 (en) * 1984-11-29 1992-10-07 Organo Kk
JPS6250711U (en) * 1985-09-13 1987-03-30
JPH0227844Y2 (en) * 1985-09-13 1990-07-26
WO2003104151A1 (en) * 2002-06-06 2003-12-18 株式会社荏原製作所 Method and device for flocculating setting
US7090777B2 (en) 2002-06-06 2006-08-15 Ebara Corporation Aggregation precipitation method
JP2010023008A (en) * 2008-07-24 2010-02-04 Sumitomo Heavy Industries Environment Co Ltd Flocculation and sedimentation apparatus and flocculation and sedimentation method
JP2014004569A (en) * 2012-06-27 2014-01-16 Toyo Eng Works Ltd Solid-liquid separation apparatus for muddy water
JPWO2014171421A1 (en) * 2013-04-16 2017-02-23 住友重機械エンバイロメント株式会社 Solid-liquid separation device and solid-liquid separation method
WO2018155524A1 (en) * 2017-02-24 2018-08-30 オルガノ株式会社 Flocculation device
JP2018140389A (en) * 2017-02-24 2018-09-13 オルガノ株式会社 Coagulator
US11406919B2 (en) 2017-02-24 2022-08-09 Organo Corporation Flocculation and sedimentation apparatus

Also Published As

Publication number Publication date
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