JPS5820680B2 - Fluidized bed sewage treatment equipment - Google Patents
Fluidized bed sewage treatment equipmentInfo
- Publication number
- JPS5820680B2 JPS5820680B2 JP52076595A JP7659577A JPS5820680B2 JP S5820680 B2 JPS5820680 B2 JP S5820680B2 JP 52076595 A JP52076595 A JP 52076595A JP 7659577 A JP7659577 A JP 7659577A JP S5820680 B2 JPS5820680 B2 JP S5820680B2
- Authority
- JP
- Japan
- Prior art keywords
- flow path
- upward
- downward
- liquid
- treated water
- 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
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Biological Treatment Of Waste Water (AREA)
Description
【発明の詳細な説明】
この発明は曝気槽内に上向流路と、下向流路と、上向流
路中に酸素を含むガスを吹込み、曝気しなから槽内の液
を上向流路中に上向流させて下向流路に温式させ、下向
流路の下端から上向流路に循環させる給気装置を有し、
液中に存在する担体粒子に付着した微生物により有機性
廃水を好気性条件下で処理する流動床式汚水処理装置に
関する。Detailed Description of the Invention This invention injects oxygen-containing gas into an upward flow path, a downward flow path, and an upward flow path in an aeration tank, and allows the liquid in the tank to rise without aeration. It has an air supply device that causes the air to flow upward into the counterflow path, warms it to the downward flow path, and circulates it from the lower end of the downward flow path to the upward flow path,
The present invention relates to a fluidized bed sewage treatment device that treats organic wastewater under aerobic conditions using microorganisms attached to carrier particles present in the liquid.
上記型式の装置は本特許出願人が特願昭51−1198
83号(特開昭53−46156号公報参照)、同51
−154222号(特開昭53−87567号公報参照
)などによって既に提案した。The above type of device was filed in Japanese Patent Application No. 51-1198 by the applicant of this patent.
No. 83 (see Japanese Unexamined Patent Publication No. 53-46156), No. 51
This has already been proposed in No. 154222 (see Japanese Patent Laid-Open No. 53-87567).
この種の装置において上向流路中ではガスのエアリフト
作用で処理すべき原水と、微生物膜が付着した担体粒子
とが上向流し、その際ガスは担体粒子で細分されて原水
、担体粒子、ガスの三相が急激な接触を繰返し、接触効
率を極めて高く維持すると共に、液の循環量を制御し、
ひいては接触処理時間を最適に保たせることが必要であ
る。In this type of device, the raw water to be treated and the carrier particles to which microbial membranes are attached flow upward in the upward flow path by the airlift effect of the gas, and at this time the gas is subdivided by the carrier particles to form raw water, carrier particles, and The three phases of gas repeatedly make rapid contact, maintaining extremely high contact efficiency, and controlling the amount of liquid circulation.
Consequently, it is necessary to keep the contact treatment time optimal.
一般に装置の設計は処理すべき廃水の廃水量を基準にし
て曝気槽の容量を定め、定められた曝気槽の容量に対し
一定の割合になる様に上向流路の断面積、つまり上向流
路を創設するドラフトの断面積を定める。Generally, when designing equipment, the capacity of the aeration tank is determined based on the amount of wastewater to be treated, and the cross-sectional area of the upward flow path is Determine the cross-sectional area of the draft that will create the flow path.
しかし、そうすると曝気槽容量が太きいとドラフトの断
面積もそれにつれて大きくなる。However, in this case, if the aeration tank capacity is large, the cross-sectional area of the draft will also increase accordingly.
そして、ガス吹込量がその大きな断面積のドラフトに見
合う給気源を用いても上向流路内に均一にガスを吹込む
ことは困難になり、エアリフト作用による原水、担体粒
子、ガスの三相の効果的な接触、循環量の制御が行えな
(なる。Even if an air supply source whose gas injection amount is commensurate with the large cross-sectional area of the draft is used, it becomes difficult to uniformly blow gas into the upward flow path. Effective contact of phases and control of circulation volume cannot be achieved.
そこで本発明は給気装置のガス吹込量に合わせてドラフ
トの断面積を所要に定め、曝気槽の容量が大きくてこの
断面積のドラフト一本ではドラフト断面積が不足すると
きはその総断面積が曝気槽の容量に対して所定の割合に
なる様に所要の複数本のドラフトを用い、これを槽内に
大体均一な配置で設け、曝気槽が大きくてもドラフトの
総断面積を槽の容量に対し所要の割合に保ち、前記三相
の接触効率を高く維持すると共に循環量も適切に制御し
て効果的に処理を行える様にしたのである。Therefore, in the present invention, the cross-sectional area of the draft is determined according to the amount of gas blown into the air supply device, and when the capacity of the aeration tank is large and one draft with this cross-sectional area is insufficient, the total cross-sectional area Use the required number of drafts so that they are at a predetermined ratio to the capacity of the aeration tank, and install them in a roughly uniform arrangement within the tank, so that even if the aeration tank is large, the total cross-sectional area of the drafts is By maintaining the required ratio to the capacity, the three-phase contact efficiency is maintained high, and the circulation amount is appropriately controlled to enable effective treatment.
又、本梶明は各ドラフト上端から下向流路に溢大して下
向流する液の一部を処理水取出口に上向させて取出す様
にし、これにより担体粒子を含まない、良水質の処理水
を得ることをも目的とするのである。In addition, in this Kajimei, a part of the liquid that overflows into the downward flow path from the upper end of each draft and flows downward is taken out upward to the treated water outlet, thereby producing high-quality water that does not contain carrier particles. The purpose is also to obtain treated water.
以下、図示の実施例に付いて本発明を説明すると、1は
大容量の曝気槽、2は槽内にドラフト3で劃設された上
向流路、4は上向流路中2に酸素を含むガスを吹込む給
気装置、5は同様に上向流路2中に原水を供給する給液
装置を示す。The present invention will be described below with reference to the illustrated embodiments. 1 is a large-capacity aeration tank, 2 is an upward flow path installed in the tank with a draft 3, and 4 is oxygen in the upward flow path 2. Similarly, reference numeral 5 indicates a liquid supply device that supplies raw water into the upward flow path 2.
槽内には比重1.1〜2.6、粒径0,3〜LOmrn
程度の砂、活性炭、アンスラサイト、プラスチック粒、
その細微生物が表面に付着できる素材からなる担体粒子
が存在し、これを活性汚泥と混合して微生物の被膜を表
面に付着させる。Specific gravity 1.1~2.6, particle size 0.3~LOmrn in the tank
degree sand, activated carbon, anthracite, plastic grains,
There are carrier particles made of a material on which the microorganisms can adhere, and these are mixed with activated sludge to form a microbial coating on the surface.
装置の運転は上向流路2に給気装置4、給液装置5で酸
素を含むガスと原水を供給して行う。The apparatus is operated by supplying oxygen-containing gas and raw water to the upward flow path 2 using an air supply device 4 and a liquid supply device 5.
担体粒子の量は曝気槽の容量の50%以下、好ましくは
15〜30%程度、担体粒子総表面積当りのBOD面積
負荷は10 ? B OD/ m、day以下とする。The amount of carrier particles is 50% or less of the capacity of the aeration tank, preferably about 15 to 30%, and the BOD area load per total surface area of carrier particles is 10? B OD/m, day or less.
又、ドラフト2の断面積と給気装置4の関係は上向流路
内に吹込まれたガスの吹込速度が担体粒子の終末速度(
落下速度)以上で、上向流路中にて粒子を流動化すると
共に、上向流路中を上向流した液が上向流路を取り囲む
下向流路6を下向流し、下向流路の下端から再び上向流
路中に大体1〜5分間で一回循環する様に定める。In addition, the relationship between the cross-sectional area of the draft 2 and the air supply device 4 is that the blowing speed of the gas blown into the upward flow path is the terminal velocity of the carrier particles (
falling velocity), the particles are fluidized in the upward flow path, and the liquid that has flowed upward in the upward flow path flows downward in the downward flow path 6 surrounding the upward flow path. It is designed to circulate once in approximately 1 to 5 minutes from the lower end of the flow path into the upward flow path.
第12図の装置では、曝気槽は平面形状が矩形をなし、
ドラフト3は槽内中央に長辺方向に一定の間隔で四本配
置してあり、この四本のドラフト3による上向流路2の
総断面積は槽1の容量に対して大体所定の割合いをなす
。In the device shown in Fig. 12, the aeration tank has a rectangular planar shape;
Four drafts 3 are arranged at regular intervals in the long side direction in the center of the tank, and the total cross-sectional area of the upward flow path 2 due to these four drafts 3 is approximately a predetermined ratio to the capacity of the tank 1. do something.
従って、前述した様にして装置を運転すると、各ドラフ
ト3により劃設された上向流路2ではガスのエアリフト
作用により原水と担体粒子が急速に上向流し、原水、粒
子、ガスの三相は接触効率の高い好適な処理工程を営む
。Therefore, when the apparatus is operated as described above, raw water and carrier particles rapidly flow upward in the upward flow path 2 provided by each draft 3 due to the air lift action of the gas, resulting in a three-phase flow of raw water, particles, and gas. conducts a suitable treatment process with high contact efficiency.
そして各上向流路から下向流路6に溢大した原水と担体
粒子は該流路6を下向流する際にも並流状態で接触し、
原水は吸着、酸化作用を受けて浄化され、かくして下向
流路の下端から近くの上向流路に入って循環する。The raw water and carrier particles overflowing from each upward flow path to the downward flow path 6 also come into contact in a parallel flow state when flowing downward through the flow path 6,
The raw water is purified by adsorption and oxidation, and thus enters the nearby upward flow path from the lower end of the downward flow path and circulates.
そして、下向流路を下向する液のうち充分に浄化された
ものは下向流路中に上から突入して下向流路の内部上方
を溢流部7と取出部8に劃する割壁9の下で折返し、取
出部8を上向して処理水取出口10に出る。Then, the sufficiently purified liquid flowing downward in the downward flow path rushes into the downward flow path from above and passes through the upper part of the inside of the downward flow path to the overflow part 7 and the take-out part 8. The water is turned back under the split wall 9, and the take-out portion 8 is directed upward to exit the treated water take-out port 10.
従って容量の大きな曝気槽中に、これに見合う断面積の
大きなドラフトを設けて処理を行う場合に生じる問題点
は全く解消する。Therefore, the problems that arise when processing is carried out by providing a draft with a commensurately large cross-sectional area in a large-capacity aeration tank are completely eliminated.
尚、曝気槽1は第3図に示す様に、夫々一つのドラフト
3にマツチした容量の端壁1′が付属した二つの部分端
部槽1a 1aと、必要ならば端壁が無い1つ或いは
複数の部分中間槽1b・・・・・・を配列して接続する
ことにより組立て、各部分槽1a1bに一つ宛ドラフト
を配置してプレハブ式に構成してもよい。As shown in Fig. 3, the aeration tank 1 consists of two partial end tanks 1a and 1a, each with an end wall 1' having a capacity matched to one draft 3, and one without an end wall if necessary. Alternatively, it may be assembled by arranging and connecting a plurality of partial intermediate tanks 1b, and may be constructed in a prefabricated manner by arranging one draft in each partial tank 1a1b.
第45図の実施例は大容量の円筒形曝気槽1に対して本
発明を適用した場合を示す。The embodiment shown in FIG. 45 shows a case where the present invention is applied to a large capacity cylindrical aeration tank 1.
この場合は槽内に同心状に上から突入する円筒形の割筒
11の内部に複数本(こ〜では四本)の円筒形をしたド
ラフト3を設けて上向流路2を形成する。In this case, a plurality (four in this case) of cylindrical drafts 3 are provided inside a cylindrical split tube 11 that protrudes concentrically into the tank from above to form an upward flow path 2.
勿論ドラフトは前述の実施例と同様な角筒であってもよ
い。Of course, the draft may be a rectangular tube similar to the previous embodiment.
この四本のドラフトの総断面積は円筒形の大きな曝気槽
の容量に対して所要の割合いをなす。The total cross-sectional area of these four drafts is the required proportion to the capacity of the large cylindrical aeration tank.
この実施例においても前述の実施例と同様に各上向流路
では原水、担体粒子、ガスの三相は効果的に接触し、上
向流路から下向流路に溢大した液と担体粒子は下向流路
を下向流する際に並流状態で接触し、矢張り液は処理さ
れて上向流路に循環する一方で、浄化された一部の液は
割筒11の外囲である取出部8に上向し、処理水出口1
0に出るのである。In this example, as in the previous example, the three phases of raw water, carrier particles, and gas are effectively in contact with each other in each upward flow path, and the liquid overflowing from the upper flow path to the downward flow path and the carrier The particles come into contact with each other in parallel flow as they flow downward through the downward flow path, and while the liquid is treated and circulated through the upward flow path, a portion of the purified liquid flows outside the split tube 11. The treated water outlet 1
It comes out as 0.
尚、前述の実施例と同じ構成部分は同じ符号で指示し、
説明を省略する。In addition, the same components as in the above-mentioned embodiment are designated by the same reference numerals.
The explanation will be omitted.
以上で明らかな様に本発明によれば処理効率の極めて高
い、性能が優れた大型の装置でも容易に提供できる。As is clear from the above, according to the present invention, even a large-sized apparatus with extremely high processing efficiency and excellent performance can be easily provided.
□ 又、各ドラフト上端から下向流路に溢大した液と担
体粒子は割壁ないし割筒で遮ぎられて処理水取出口には
行くことができない。□ Also, the liquid and carrier particles overflowing from the upper end of each draft into the downward flow path are blocked by the split wall or split tube and cannot reach the treated water outlet.
従って、下向流路を一旦下向流し、割壁ないし割筒の下
端を潜って土向きに折返す液のみが処理水として取出口
に得られるので、処理水には担体粒子の混入がなく、水
質は極めて良好である。Therefore, only the liquid that flows downward through the downward channel, passes through the split wall or the bottom end of the split tube, and turns toward the ground is obtained at the outlet as treated water, so there is no carrier particles mixed into the treated water. , the water quality is extremely good.
第1図は本発明による装置の一実施例の平面図、第2図
は同上の縦断側面図、第3図は第1,2図の装置の曝気
槽をプレ・・ブ式に構成した他の一実施例を示す平面図
、第4図は本発明の更に他の一実施例を示す平面図、第
5図は同上の縦断側面図、図中、1は曝気槽、2は上向
流路、3は上向流路を槽内に形成するドラフト、4は給
気装置、6は下向流路を示す。Fig. 1 is a plan view of an embodiment of the apparatus according to the present invention, Fig. 2 is a longitudinal side view of the same, and Fig. 3 is a pre-configured aeration tank of the apparatus shown in Figs. 1 and 2. FIG. 4 is a plan view showing still another embodiment of the present invention; FIG. 5 is a longitudinal side view of the same; in the figure, 1 is an aeration tank; 2 is an upward flow 3 is a draft that forms an upward flow path in the tank, 4 is an air supply device, and 6 is a downward flow path.
Claims (1)
した微生物により有機性廃水を好気性条件下で処理する
流動床式汚水処理装置において、曝気槽内に上端がほぼ
水面付近にあり、かつ下端が槽底部と間隔を保つ複数の
ドラフトによって各ドラフト内部に形成された複数の上
向流路と、ドラフトの各外側と曝気槽の内側との間に形
成された下向流路と、前記各上向流路中に酸素を含むガ
スを吹込む給気装置と、曝気槽壁上部に設けられた処理
水取出口と、上端を水面上に出し、下端を前記処理水取
出口よりも下に位置させて下向流路中に突入し、前記処
理水取出口と対向して設けられ、下向流路の内部上方を
各上向流路を上向流した液と担体粒子が下向流路を下向
流するために温式する溢流部と、溢流部を下向した液が
前記処理水取出口に向かって上向する取出部とに劃する
割壁とを有し、給気装置からガスを上向流路に吹込んで
曝気しなから槽内の液を上向流中に上向流させて下向流
路に温式させ、下向流路の下端から上向流路に循環させ
、下向流路の液の一部を処理水取出口から取り出すよう
にしたことを特徴とする流動床式汚水処理装置。1. In a fluidized bed sewage treatment device in which biological carrier particles are present in the aeration tank and organic wastewater is treated under aerobic conditions by microorganisms attached to the particles, the upper end of the aeration tank is almost near the water surface, and a plurality of upward passages formed inside each draft by a plurality of drafts whose lower ends are spaced apart from the tank bottom, and a downward passage formed between each outside of the draft and the inside of the aeration tank; An air supply device that blows gas containing oxygen into each of the upward flow paths, a treated water outlet provided at the upper part of the aeration tank wall, and an upper end above the water surface and a lower end below the treated water outlet. The liquid and carrier particles flowing upward through each upward flow path inside the downward flow path and the carrier particles are located at the bottom and enter the downward flow path, and are provided opposite to the treated water outlet. It has an overflow part that is heated to flow downward through the counterflow path, and a partition wall that partitions the liquid flowing downward through the overflow part into a take-out part where the liquid flows upward toward the treated water take-out port. , gas is blown into the upward flow path from the air supply device for aeration, and then the liquid in the tank is made to flow upward during the upward flow to heat the downward flow path. A fluidized bed type sewage treatment device characterized in that the liquid is circulated in a counter-flow path and a part of the liquid in the downward flow path is taken out from a treated water outlet.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP52076595A JPS5820680B2 (en) | 1977-06-29 | 1977-06-29 | Fluidized bed sewage treatment equipment |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP52076595A JPS5820680B2 (en) | 1977-06-29 | 1977-06-29 | Fluidized bed sewage treatment equipment |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5412150A JPS5412150A (en) | 1979-01-29 |
| JPS5820680B2 true JPS5820680B2 (en) | 1983-04-25 |
Family
ID=13609656
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP52076595A Expired JPS5820680B2 (en) | 1977-06-29 | 1977-06-29 | Fluidized bed sewage treatment equipment |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5820680B2 (en) |
Families Citing this family (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5681190A (en) * | 1979-12-06 | 1981-07-02 | Ebara Infilco Co Ltd | Decomposition of sewage such as night soil |
| JPS56161891A (en) * | 1980-05-15 | 1981-12-12 | Yamaki Kogyo:Kk | Apparatus for cycling and decontaminating pool water using artificial waterfall |
| JPS59196675U (en) * | 1983-06-16 | 1984-12-27 | 段谷産業株式会社 | Variable door frame material |
| JPS601881U (en) * | 1983-06-17 | 1985-01-09 | 段谷産業株式会社 | door frame material |
| JPS608380U (en) * | 1983-06-29 | 1985-01-21 | 段谷産業株式会社 | Architectural components used for doorstops, etc. |
| JPS6096000U (en) * | 1983-12-09 | 1985-06-29 | 株式会社西原環境衛生研究所 | Sewage treatment equipment |
| JPH0131354Y2 (en) * | 1984-11-20 | 1989-09-26 | ||
| JPH0131353Y2 (en) * | 1984-11-20 | 1989-09-26 |
-
1977
- 1977-06-29 JP JP52076595A patent/JPS5820680B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5412150A (en) | 1979-01-29 |
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