JPH01218695A - Anaerobic treatment tank - Google Patents
Anaerobic treatment tankInfo
- Publication number
- JPH01218695A JPH01218695A JP63044427A JP4442788A JPH01218695A JP H01218695 A JPH01218695 A JP H01218695A JP 63044427 A JP63044427 A JP 63044427A JP 4442788 A JP4442788 A JP 4442788A JP H01218695 A JPH01218695 A JP H01218695A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- particles
- inclined plates
- sludge bed
- gas
- 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.)
- Pending
Links
- 239000010802 sludge Substances 0.000 claims abstract description 69
- 239000002245 particle Substances 0.000 claims abstract description 29
- 239000002351 wastewater Substances 0.000 claims abstract description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 18
- 244000005700 microbiome Species 0.000 claims description 6
- 239000013049 sediment Substances 0.000 abstract 2
- 230000001079 digestive effect Effects 0.000 abstract 1
- 238000000034 method Methods 0.000 abstract 1
- 239000002699 waste material Substances 0.000 description 17
- 238000000926 separation method Methods 0.000 description 9
- 239000007788 liquid Substances 0.000 description 6
- 238000005192 partition Methods 0.000 description 5
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- 230000029087 digestion Effects 0.000 description 4
- 238000003756 stirring Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 3
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 230000000630 rising effect Effects 0.000 description 2
- 230000004071 biological effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000000994 depressogenic effect Effects 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000010907 mechanical stirring Methods 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 238000005191 phase separation Methods 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Abstract
Description
【発明の詳細な説明】
[産業上の利用分野]
本発明は嫌気性処理装置に係り、特に嫌気性微生物の生
物学的性質を利用して有機性廃水を分解処理する装置に
関する。DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention relates to an anaerobic treatment device, and particularly to a device for decomposing organic wastewater by utilizing the biological properties of anaerobic microorganisms.
[従来の技術]
有機性廃水を嫌気性微生物により処理するための装置と
して、例えはスラッジブラングツl−型の装置がある。[Prior Art] As an apparatus for treating organic wastewater with anaerobic microorganisms, there is, for example, a sludge brangutsu l-type apparatus.
第9図に示ずように、従来この種の装置は、嫌気性微生
物を主体とする汚泥床(スラッジブランゲット)1を容
器2内に形成すると共に、有機性廃水Qを底部3から上
向流にて汚泥床1に接触させ、嫌気性消化を行わせてメ
タンガス(CH4)、二酸化炭素(CO2)などのバイ
オガスGに分解するようになっている。分解処理された
水Wは、汚泥床1の上方から容器2外に流出されるよう
になっている。また発生ずるカスGは漏斗状の蓋部材4
で成るカス収集部5から抜き出さぜるようになっている
。As shown in FIG. 9, conventional equipment of this type forms a sludge bed (sludge blanket) 1 containing mainly anaerobic microorganisms in a container 2, and also directs organic wastewater Q upward from the bottom 3. The sludge is brought into contact with the sludge bed 1 in the flow, and subjected to anaerobic digestion to be decomposed into biogas G such as methane gas (CH4) and carbon dioxide (CO2). The decomposed water W is drained out of the container 2 from above the sludge bed 1. In addition, the generated scum G is a funnel-shaped lid member 4.
It is adapted to be extracted from a waste collecting section 5 consisting of.
この装置は、廃水Q中に含まれる有機性物質の濃度を高
めることで、分解処理効率をあけることができるという
利点がある。This device has the advantage of increasing the decomposition efficiency by increasing the concentration of organic substances contained in the wastewater Q.
たたしこの装置においては、消化により発生ずるカスG
か汚泥中で上昇して汚泥床1を乱し、処理水Wと汚泥S
との分離が難かしくなるので、消化反応部6と固液分離
部7とを区画することが行われる。In this device, the scum G generated during digestion is
water rises in the sludge and disturbs the sludge bed 1, causing treated water W and sludge S
Since it becomes difficult to separate the solid-liquid separation section 6 from the digestion reaction section 6, the solid-liquid separation section 7 is divided into sections.
また、汚泥粒子Sが発生ずるガスGをとり囲むように結
合して成る浮上汚泥が発生するため、固液分離部7へ流
入する前にカスGを充分分離する必要があることから、
カスG(気)−汚泥S(固)−水W(液)の三相分離の
機能を有する装置が種々提案されている。In addition, floating sludge is generated in which sludge particles S are combined to surround the generated gas G, so it is necessary to sufficiently separate the sludge G before it flows into the solid-liquid separation section 7.
Various devices have been proposed that have the function of three-phase separation of sludge G (air) - sludge S (solid) - water W (liquid).
例えば第10図に示すように、汚泥床1の上方に、断面
逆三角形の樋状に組んな仕切板8を設け、その下端頂部
9に迂回流路10を形成したものがある。For example, as shown in FIG. 10, there is a system in which a trough-like partition plate 8 with an inverted triangular cross section is provided above the sludge bed 1, and a detour passage 10 is formed at the lower end apex 9 of the partition plate 8.
この提案によれば、水WとカスGとを上方に(矢印Aに
て示す)、汚泥粒子Sを固液分離部7に導く(矢印B)
ことて、流出する汚泥粒子Sを分離さぜ、さらに水Wと
カスGとを、容器11上方にて別個に形成された区画路
12により分離させることになる。According to this proposal, water W and waste G are directed upward (indicated by arrow A), and sludge particles S are guided to solid-liquid separation section 7 (arrow B).
In other words, the sludge particles S flowing out are separated, and furthermore, the water W and the waste G are separated by the partition passage 12 formed separately above the container 11.
[発明が解決しようとする課題]
しかしながら、上記従来技術のうち、第9図に示した構
成においては、カス収集部5への浮上汚泥の蓄積が避け
られず、場合によってはカスGの抜出しに支障が生じな
り、浮上汚泥が多い場合には処理能力の低下を招くこと
になる。[Problems to be Solved by the Invention] However, among the above-mentioned conventional techniques, in the configuration shown in FIG. If there is a large amount of floating sludge, the processing capacity will be reduced.
この対策として、カス収集部5に機械式撹拌装置等を設
けることも出来るが、特に処理規模の大なる装置におい
ては、設備費、運転費、維持管理等が問題になる。As a countermeasure against this, it is possible to provide a mechanical stirring device or the like in the waste collection section 5, but equipment costs, operating costs, maintenance and management, etc. become problems, especially in devices with a large processing scale.
また仕切板8を設ける構成(第10図)においては、固
液分離にはある程度機能するものの、浮上する汚泥粒子
Sの回収(固気分離)については、迂回する途中で分離
がなされるとは限らず、又、カス収集部への汚泥の浮上
も避けられない。さらに迂回の入口が限られた位置にあ
るので、流路面積が汚泥床1の上面面積に比較して小さ
くならさ′るを得す、下方からの流入を均一に行っても
、上方から流出するときに偏流することとなり、デッド
スペースか生じやすい。特に低濃度廃水である場合は、
発生カスGによる撹拌混合効果も期待できなくなるなめ
問題となる。In addition, in the configuration in which the partition plate 8 is provided (FIG. 10), although it functions to some extent for solid-liquid separation, it is difficult to recover the floating sludge particles S (solid-gas separation) during the detour. However, floating of sludge to the waste collection section is also unavoidable. Furthermore, since the inlet of the detour is located in a limited position, the flow path area is smaller than the area of the upper surface of the sludge bed 1. When doing so, the current tends to drift and a dead space is likely to occur. Especially when it is low concentration wastewater,
This becomes a problem because the stirring and mixing effect due to the generated scum G cannot be expected.
そこで本発明は、上記事情に鑑み、処理水と汚泥粒子と
の分離の他、浮上汚泥を分離・回収することのできる嫌
気性処理装置を提供すべく創案されたものである。In view of the above circumstances, the present invention was devised to provide an anaerobic treatment device that can separate and recover floating sludge in addition to separating treated water and sludge particles.
1課題を解決するための手段]
本発明は、嫌気性微生物を主体とする汚泥床を有した容
器内に、有機性廃水を上記汚泥床の下方から供給して分
解処理する装置において、」−記汚泥床の上方に、処理
後の水と共に流出する汚泥粒子を沈降させてその」二面
に受ける傾斜板を並設し、この傾斜板の下面に、発生ず
る分解ガスをとり込んで浮上する汚泥粒子を、傾斜板に
沿って垂直方向での所定の隔りが生ずる側方まで導く凹
凸部を形成したものである。Means for Solving 1 Problem] The present invention provides an apparatus for decomposing organic wastewater by supplying it from below the sludge bed into a container having a sludge bed mainly composed of anaerobic microorganisms. Above the sludge bed, sloping plates are installed in parallel to allow the sludge particles that flow out with the water after treatment to settle and receive them on two sides, and the lower surfaces of these slanted plates take in the generated decomposed gas and float it to the surface. A concavo-convex portion is formed to guide sludge particles along the inclined plate to the side where a predetermined gap occurs in the vertical direction.
「作 用」
上記構成によって、傾斜板は、処理水と共に汚泥床から
その」一方ノ\流出してくる汚泥粒子を沈降させて汚泥
床へ回収する。また卸斜板の下面に形成された凹凸部は
、浮上汚泥を一旦側方へ導いた後、その浮力により真上
に上昇させることで傾斜板に衝突させ、発生カスと分離
させる。"Function" With the above configuration, the inclined plate settles the sludge particles flowing out from the sludge bed together with the treated water and collects them into the sludge bed. The uneven portion formed on the lower surface of the sloping plate once guides the floating sludge to the side, and then raises it directly upwards due to its buoyancy, causing it to collide with the sloping plate and separating it from the generated sludge.
[実施例] 以下本発明の実施例を添付図面に従って説明する。[Example] Embodiments of the present invention will be described below with reference to the accompanying drawings.
第1図および第2図は、本発明に係る嫌気性処理装置の
第一の実施例を示したものであり、従来と同様に、嫌気
性微生物を主体とする汚泥床1を内部に有した密閉容器
21に、有機性廃水Qを上向流にて供給するための流入
部22と、処理後の水Wを容器21外に流出させるため
の流出部23と、発生ずるバイオガスGを抜き出すため
のカス収集室24およびカス出口25とを設けて成る。1 and 2 show a first embodiment of the anaerobic treatment apparatus according to the present invention, which, like the conventional one, has a sludge bed 1 containing anaerobic microorganisms inside. An inflow part 22 for supplying organic wastewater Q in an upward flow into the closed container 21, an outflow part 23 for flowing the treated water W out of the container 21, and extracting the generated biogas G. A waste collection chamber 24 and a waste outlet 25 are provided for this purpose.
本実施例にあっては、容器21は略直方体状を呈してお
り、流入部22は汚泥床1に対して面金域に均一な流入
となるように設けられた多孔管26を配置されて成る。In this embodiment, the container 21 has a substantially rectangular parallelepiped shape, and the inflow section 22 has a perforated pipe 26 arranged so that the sludge flows uniformly into the metal area with respect to the sludge bed 1. Become.
また流出部23は、上方からみて長方形の並設された開
口部27を有する集水トラフ28で成り、開口部27よ
り越流した処理水Wを一隅29に集めて排出するように
なっている。Further, the outflow section 23 is composed of a water collection trough 28 having rectangular openings 27 arranged in parallel when viewed from above, and the treated water W overflowing from the openings 27 is collected in one corner 29 and discharged. .
そして本発明の特長となる傾斜板30力釈汚泥床1の上
方且つ集水トラフ28の下方に設けられている。この傾
斜板30は等間隔をちって汚泥床1の全面を覆うように
並設され、その傾斜角(約60度)に沿って土自流を導
くことで、上水道施設等で公知の汚泥粒子S沈降をさぜ
るようになっている。An inclined plate 30, which is a feature of the present invention, is provided above the sludge bed 1 and below the water collection trough 28. These inclined plates 30 are arranged at equal intervals so as to cover the entire surface of the sludge bed 1, and by guiding the soil flow along the inclined angle (approximately 60 degrees), the sludge particles S It is designed to stir up sedimentation.
第3図に示すように、傾斜板30の上面31は、汚泥粒
子Sを受りて下方の汚泥床1へ回収てきるような滑らか
な面に成形されているが、その反対側の下面32には、
断面波状を呈した凹凸部33が形成されている。As shown in FIG. 3, the upper surface 31 of the inclined plate 30 is formed into a smooth surface that receives the sludge particles S and collects them into the sludge bed 1 below, while the lower surface 32 on the opposite side for,
An uneven portion 33 having a wavy cross section is formed.
その凸状区間34は、傾斜板30の下面32に沿って浮
上してくる汚泥粒子Sを、立ち上がりの曲線に沿って導
くことで、傾斜軸線35から側方に、図中で言えは右側
に移動させて、所定の垂直方向での隔りが生じるように
なっている。また凹状区間36は汚泥粒子Sが凸状区画
34の頂点付近から略真上に上昇したときに、これと接
触しないように適宜窪まされている。The convex section 34 guides the sludge particles S floating along the lower surface 32 of the inclined plate 30 along the rising curve, thereby moving laterally from the inclined axis 35, to the right in the figure. They are moved to create a predetermined vertical separation. Further, the concave section 36 is suitably depressed so as not to come into contact with the sludge particles S when they rise from near the apex of the convex section 34 almost directly above.
次に本実施例の作用を説明する。Next, the operation of this embodiment will be explained.
流入部22から供給された有機性廃水Qは、汚泥床1に
より公知の消化処理かなされた後、その上方に流出され
る。この際、発生するバイオカスGに影響されて共に流
出する汚泥粒子Sは、傾斜板30の間を流れる途中で沈
降し、上面31に沿って下方の汚泥床1に回収される。The organic wastewater Q supplied from the inflow section 22 is subjected to a known digestion treatment in the sludge bed 1, and then is discharged above the sludge bed 1. At this time, the sludge particles S, which are influenced by the generated biocass G and flow out together, settle while flowing between the inclined plates 30 and are collected in the sludge bed 1 below along the upper surface 31.
一方、ガスGをとり込んでその浮力により上昇しつつ傾
斜板30の下側を進行する汚泥粒子Sは、凹状区間36
から凸状区間34へ移動する際に、その表面から離れて
自由上昇し、次の凹状区間36乃至凸状区間34におい
て衝突する。この衝撃によって弱い結合でなるカスGと
汚泥粒子Sとは分離される。衝突は、凹凸部33に沿っ
て次々に行われ、粒子Sの離脱に従って更に上昇速度か
増し、分離が促進される。分離した粒子Sは、図中、破
線矢印で示したように、沈降した粒子Sと同様に上面3
1に沿って落下する。これでカスGは水W中に浮遊する
ものたけとなり、集水トラフ28の開口部27から越流
する際に容易に分離され、カス収集室24を経て出口2
5から4JP出される。On the other hand, the sludge particles S that take in the gas G and move up under the inclined plate 30 due to its buoyancy move along the concave section 36.
When moving from the convex section 34 to the convex section 34, it leaves the surface and rises freely, colliding in the next concave section 36 to the convex section 34. This impact separates the sludge particles S from the sludge particles G, which are weakly bonded. Collisions occur one after another along the uneven portions 33, and as the particles S separate, the rising speed further increases, promoting separation. The separated particles S, as shown by the broken line arrow in the figure, are similar to the sedimented particles S on the upper surface 3.
Fall along 1. In this way, the waste G becomes a float floating in the water W, and is easily separated when overflowing from the opening 27 of the water collection trough 28, passing through the waste collection chamber 24 to the outlet 2.
4JP is issued from 5.
このように、カスGにより浮」ニする汚泥粒子Sを、階
段状に導いて、浮力により生ずる衝突を繰り返させて分
離さぜるようにしたので、汚泥粒子Sを効率よく、しか
も確実に回収することができる。これにより、カスGの
出口25が塞がれることかなく、円滑にカスGの取出し
を行うことができる。また、浮上粒子自身の浮力を利用
することになるので、撹拌装置等を必要としない。In this way, the sludge particles S floating by the sludge G are guided in a stepwise manner and are separated by repeated collisions caused by buoyancy, so that the sludge particles S can be collected efficiently and reliably. can do. Thereby, the waste G can be smoothly taken out without the waste G outlet 25 being blocked. Furthermore, since the buoyancy of the floating particles themselves is utilized, a stirring device or the like is not required.
さらに、この傾斜板30は、汚泥床1の全面を覆って設
けることができるので、デッドスペース等のない均一な
分離か行い得る。Furthermore, since this inclined plate 30 can be provided to cover the entire surface of the sludge bed 1, uniform separation without dead spaces etc. can be performed.
次に第二の実施例を第4図及び第5図によって説明する
。Next, a second embodiment will be explained with reference to FIGS. 4 and 5.
この実施例の第一・の実施例と異なるところは、傾斜板
30の上端に笠状のカス捕集部材41を設け、発生ずる
カスGを取り出すようにしであることである。このカス
捕集部材41は、片上かり構造で成り、その末端部42
が互いに連結されて、捕集されたカスGが一方の出口4
3からJIF出されるようになっている。This embodiment differs from the first embodiment in that a shade-shaped waste collection member 41 is provided at the upper end of the inclined plate 30 to take out the generated waste G. This waste collection member 41 has a single-sided structure, and its end portion 42
are connected to each other, and the collected waste G is sent to one outlet 4.
JIF has been issued since 3.
このように構成することで、容器44を開放型にするこ
とができると共に、流出部23およびガス収集のための
構造を簡単にできる。また部材41の両端は、カス気泡
が逸散しないように、当て板45等で塞ぐのが望ましい
。With this configuration, the container 44 can be made into an open type, and the structure for the outflow portion 23 and gas collection can be simplified. Further, it is desirable that both ends of the member 41 be closed with a backing plate 45 or the like to prevent waste bubbles from escaping.
なお、以上の実施例においては、同一方向に傾斜する傾
斜板30のみを設けたが、第6図に示すように、方向が
互いに異なる傾斜板51を多段に設けてもよい。この場
合、ガスGと水Wとの流路(それぞれ破線と一点鎖線と
で示ず)が交錯しないように、折り返される区間52に
おいて、傾斜板51に並行な区画板43を余d1に設り
るようにしてもよい(第7図参照)。In the above embodiment, only the inclined plates 30 inclined in the same direction were provided, but as shown in FIG. 6, inclined plates 51 having different directions may be provided in multiple stages. In this case, in order to prevent the flow paths of gas G and water W (not shown by broken lines and dashed-dotted lines, respectively) from intersecting, a partition plate 43 parallel to the inclined plate 51 is provided at the remainder d1 in the folded section 52. (See Figure 7).
また、凹凸部33の形状は、波状に限るものではなく、
例えば第8図に示すような直線状の断面となるようにし
てもよい。この場合、有効な衝突10−一
力が発生するように、凸状区間34から凹状区間36ノ
\と結ぶ面61が水平と90度以上の角度をなすように
形成することか望ましい。Further, the shape of the uneven portion 33 is not limited to a wavy shape,
For example, it may have a linear cross section as shown in FIG. In this case, it is desirable that the surface 61 connecting the convex section 34 to the concave section 36 forms an angle of 90 degrees or more with the horizontal so that an effective collision force is generated.
さらに、凹凸のピッチ、総数、あるいは傾斜板同士の間
隔等は図示例に限るものではなく、処理規模などによっ
て選択されるものである。Further, the pitch of the unevenness, the total number, the interval between the inclined plates, etc. are not limited to the illustrated example, and may be selected depending on the scale of processing and the like.
[発明の効果]
以上要するに本発明によれば、次のような優れた効果を
発揮する。[Effects of the Invention] In summary, according to the present invention, the following excellent effects are achieved.
(1〕 汚泥床の上方に、凹凸部を下面に有した傾斜
板を並設したので、浮上汚泥の分離・回収を確実に行い
、処理能力の向上および円滑なカス抜き出しが達成され
る。(1) Since inclined plates having uneven portions on the lower surface are arranged above the sludge bed, floating sludge is reliably separated and recovered, improving processing capacity and smooth removal of waste.
(2)均一な集水が可能であるので、デッドスペースか
生じることによる反応効率の低下か防止できる。(2) Since it is possible to collect water uniformly, it is possible to prevent a decrease in reaction efficiency due to the formation of dead spaces.
(3)撹拌装置等を必要としないので、運転費等が増加
することがない。(3) Since a stirring device etc. is not required, operating costs etc. do not increase.
第1図は本発明に係る嫌気性処理装置の第一の実施例を
示した側面図、第2図は第1図中の■−■線欠視図、第
3図は第1図中の要部を示した側面図、第4図は第二の
実施例を示した側面図、第5図はその要部を示した側面
図、第6図は第1図中の傾斜板の他の実施例を示した側
面図、第7図はその傾斜板の別の実施例を示した側面図
、第8図は凹凸部の他の実施例を示した側面図、第9図
は従来の嫌気性処理装置を示した側面図、第10図は他
の従来の嫌気性処理装置を示した斜視図である。
図中、1は汚泥床、30は傾斜板、33は凹凸部である
。
特許出願人 石川島播磨重工業株式会社代理人弁理士
絹 谷 信 雄−56・FIG. 1 is a side view showing a first embodiment of the anaerobic treatment apparatus according to the present invention, FIG. 2 is a cutaway view along the line ■-■ in FIG. 1, and FIG. FIG. 4 is a side view showing the main parts, FIG. 4 is a side view showing the second embodiment, FIG. 5 is a side view showing the main parts, and FIG. 6 is another view of the inclined plate in FIG. FIG. 7 is a side view showing another example of the inclined plate, FIG. 8 is a side view showing another example of the uneven portion, and FIG. 9 is a side view showing the conventional anaerobic plate. FIG. 10 is a side view of the anaerobic treatment apparatus, and FIG. 10 is a perspective view of another conventional anaerobic treatment apparatus. In the figure, 1 is a sludge bed, 30 is an inclined plate, and 33 is an uneven portion. Patent applicant: Ishikawajima-Harima Heavy Industries Co., Ltd. Representative patent attorney: Nobuo Kinutani-56
Claims (1)
、有機性廃水を上記汚泥床の下方から供給して分解処理
する装置において、上記汚泥床の上方に、処理後の水と
共に流出する汚泥粒子を沈降させてその上面に受ける傾
斜板を並設し、該傾斜板の下面に、発生する分解ガスを
とり込んで浮上する汚泥粒子を、傾斜板に沿って垂直方
向での所定の隔りが生ずる側方まで導く凹凸部を形成し
たことを特徴とする嫌気性処理装置。1. In a device that decomposes organic wastewater by supplying it from below the sludge bed into a container with a sludge bed mainly composed of anaerobic microorganisms, it flows out together with the treated water above the sludge bed. Inclined plates are installed in parallel to allow the sludge particles to settle down and receive them on the upper surface, and the sludge particles that float up by taking in the decomposed gas generated are placed on the lower surface of the inclined plate in a predetermined direction in the vertical direction along the inclined plates. An anaerobic treatment device characterized by forming an uneven portion leading to the side where a gap occurs.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63044427A JPH01218695A (en) | 1988-02-29 | 1988-02-29 | Anaerobic treatment tank |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63044427A JPH01218695A (en) | 1988-02-29 | 1988-02-29 | Anaerobic treatment tank |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH01218695A true JPH01218695A (en) | 1989-08-31 |
Family
ID=12691191
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP63044427A Pending JPH01218695A (en) | 1988-02-29 | 1988-02-29 | Anaerobic treatment tank |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH01218695A (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20020084396A (en) * | 2001-04-30 | 2002-11-07 | 이상일 | A sedimentation Tank Using Suspended meatial Removing Device |
JP2009522096A (en) * | 2006-01-05 | 2009-06-11 | バイオタン システムズ インターナショナル ビー.ブイ. | Method and reactor for anaerobic wastewater purification |
JP2012050910A (en) * | 2010-08-31 | 2012-03-15 | Kobelco Eco-Solutions Co Ltd | Upflow type reaction tank, water treatment method using the reaction tank, and water treatment apparatus equipped with the reaction tank |
JP2017060931A (en) * | 2015-09-25 | 2017-03-30 | 日本下水道事業団 | Solid-liquid separation system and inclined plate |
CN111943463A (en) * | 2020-10-19 | 2020-11-17 | 湖南湘新水务环保投资建设有限公司 | Reduce membrane pollution's sewage treatment system |
-
1988
- 1988-02-29 JP JP63044427A patent/JPH01218695A/en active Pending
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20020084396A (en) * | 2001-04-30 | 2002-11-07 | 이상일 | A sedimentation Tank Using Suspended meatial Removing Device |
JP2009522096A (en) * | 2006-01-05 | 2009-06-11 | バイオタン システムズ インターナショナル ビー.ブイ. | Method and reactor for anaerobic wastewater purification |
US8043506B2 (en) | 2006-01-05 | 2011-10-25 | Biothane Systems International B.V. | Process and reactor for anaerobic waste water purification |
JP2012050910A (en) * | 2010-08-31 | 2012-03-15 | Kobelco Eco-Solutions Co Ltd | Upflow type reaction tank, water treatment method using the reaction tank, and water treatment apparatus equipped with the reaction tank |
JP2017060931A (en) * | 2015-09-25 | 2017-03-30 | 日本下水道事業団 | Solid-liquid separation system and inclined plate |
CN111943463A (en) * | 2020-10-19 | 2020-11-17 | 湖南湘新水务环保投资建设有限公司 | Reduce membrane pollution's sewage treatment system |
CN111943463B (en) * | 2020-10-19 | 2020-12-15 | 湖南湘新水务环保投资建设有限公司 | Reduce membrane pollution's sewage treatment system |
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