JP4307903B2 - Wastewater septic tank - Google Patents

Wastewater septic tank Download PDF

Info

Publication number
JP4307903B2
JP4307903B2 JP2003141816A JP2003141816A JP4307903B2 JP 4307903 B2 JP4307903 B2 JP 4307903B2 JP 2003141816 A JP2003141816 A JP 2003141816A JP 2003141816 A JP2003141816 A JP 2003141816A JP 4307903 B2 JP4307903 B2 JP 4307903B2
Authority
JP
Japan
Prior art keywords
tank
biological carrier
pressing member
biological
sewage
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 - Fee Related
Application number
JP2003141816A
Other languages
Japanese (ja)
Other versions
JP2004344706A (en
Inventor
裕二 小泉
力 石垣
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.)
Housetec Inc
Original Assignee
Housetec Inc
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 Housetec Inc filed Critical Housetec Inc
Priority to JP2003141816A priority Critical patent/JP4307903B2/en
Publication of JP2004344706A publication Critical patent/JP2004344706A/en
Application granted granted Critical
Publication of JP4307903B2 publication Critical patent/JP4307903B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Landscapes

  • Treatment Of Biological Wastes In General (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は、家庭等から排出される屎尿やその他の生活排水(単に、汚水ともいう)を処理する汚水浄化槽に好適に使用される生物担体押え部材に関するものである。
【0002】
【従来の技術】
図5は、従来の生物担体押え部材を用いた汚水浄化槽(部分縦断面図)の一例である。図示されるように、汚水浄化槽の好気処理槽10内では、充填した生物担体(生物付着材、充填材、接触材あるいは濾材、などともいう。)を押えたり支持するために、上部、下部及び中間部に各々、通水板24、25、26を配して、その通水板どうしで挟まれる空間部に生物担体を充填し、その生物担体に生物細胞を付着・増殖させ、汚水中の有機物を好気的に分解・処理するものである(例えば、特許文献1参照)。
【0003】
図6は、従来の生物担体押え部材を用いた別例の汚水浄化槽(部分縦断面図)で、この場合は、液面WLよりも上方に(上)通水板24を設置している(例えば、特許文献2参照)。
【0004】
【特許文献1】
特開平11−90113号公報
【0005】
【特許文献2】
特開2000−210690号公報
【0006】
【発明が解決しようとする課題】
しかし、図5のように、生物担体を押える(上)通水板24が液中に浸るように配した場合、汚水が流入する(上)通水板24付近は汚水濃度が高く、生物担体だけではなく、(上)通水板24にも生物細胞(生物膜)が付着して、場合によっては上通水板24の穴(又は網目)が閉塞したり、その閉塞によって汚水が次槽へ越流する等の支障が生じる。
また、図6の別例の場合、上通水板24の穴(又は網目)の閉塞は防げるが、保守点検時のサンプリングや、液中の溶存酸素量(BOD)、水素イオン濃度(pH)等の測定が困難であったりの問題が生じる。
【0007】
本発明は、これらの問題を解決しようとするものであり、上通水板に生物細胞(生物膜)が多量に付着しても完全には閉塞せず、したがって、次槽への越流を防ぐことができ、あるいは、保守点検時のサンプリングや、液中のBOD、pH等の測定も容易に行なえる上通水板(すなわち、生物担体押え部材)を提供するものである。
【0008】
【課題を解決するための手段】
上記課題を達成するため、本発明者らは種々検討し、上通水板(生物担体押え部材)の一部が常に液面よりも上方にあるように工夫することによって、その上通水板(生物担体押え部材)の穴(網目)の閉塞は防止できることに着想し、本発明を完成した。
【0009】
すなわち、本発明は、好気処理槽と、この好気処理槽内に配置される生物担体押え部材とを備え、上記生物担体押え部材が、平面板状部と、この平面板状部から上方に隆起した凸部とを有し、上記平面板状部が好気処理槽の槽内液面よりも下となり、上記凸部の一部が好気処理槽の運転中に槽内液面よりも上となるように設置される汚水浄化槽である。
【0011】
【作用】
本発明の生物担体押え部材1では、平面板状部2から上方へ隆起するように凸部3が形成されており、生物担体押え部材1の一部においては液に浸らずに常に液面よりも上方にある。そのため、液中にある生物担体押え部材に生物細胞(生物膜)付着し、生物担体押え部材の穴(網目)が閉塞しても、液面よりも上方の凸部3では穴(網目)の閉塞が起こらない。
【0012】
【発明の実施の形態】
以下、図面を参照して、本発明を更に具体的に説明する。
図1は、本発明の一例の生物担体押え部材1の斜視図である。生物担体押え部材1は、上方に隆起した凸部3(図1では3箇所)を有し、その凸部3の一部は槽内液面WLよりも常に上方にあるように設計されている。また、その生物担体押え部材1には、槽内に充填した生物担体よりも小さな穴(孔状、スリット状、格子状若しくは網目状)が多数形成されていて、汚水を自由に通すが生物担体を通さない(生物担体は流失させない)構造である。
【0013】
ここで、生物担体押え部材1の(全体の)平面視大きさは、汚水浄化槽における好気処理槽10の平面視大きさに適合する大きさとする。また、凸部(隆起部)3は、平面視で、生物担体押え部材1の面積の概ね10%以上60%以下の面積を占めていることが好ましい。凸部3の高さ(L1)は、汚水浄化槽の大きさによっても異なるが、一般家庭用浄化槽に用いる場合は、液面(WL)から概ね10〜100mmが露出する程度とする。
【0014】
生物担体押え部材1の材質は、通常は、ポリプロピレン、ポリエチレン、ポリ塩化ビニル等が用いられ、ステンレス、亜鉛めっき、銅などの金属製とすることもできる。なお、生物担体押え部材1の板厚は規模、材質によっても異なるが、概ね0.5〜10mm程度である。
【0015】
図2は、本発明の生物担体押え部材1を用いた汚水浄化槽の好気処理槽10の部分で、槽内液がWLにあるとき(運転中)である。好気処理槽10は、仕切板4と仕切板5と外槽7とで囲まれており、生物担体を保持するための生物担体支え(通水板)6bを下部に配し、上部には生物担体押え部材1を配しており、また、上半分とした下半分とを分ける中間の位置には別の生物担体支え(通水板)6aを配している。生物担体面押え部材1の平面板状部2は、通常、WL下に没している一方で、凸部3の一部はWL上に露出している。
【0016】
そして、汚水の流れは、通常、図2に示すような流れAである。濃度の高い液が流入する生物担体押え部材1付近では、押え部材1の穴(網目)部に生物細胞(生物膜)が付着しやすく、時間の経過とともにこれが肥大化し、穴(網目)を閉塞させる。ところで、生物担体押え部材1の平面板状部2の穴(網目)が閉塞して液面がやや上昇しても、WLよりも高い位置まで隆起した凸部3を形成させているので、図2に示すような流れBのように、凸部3における穴(網目)から槽下部への液の流入(移流)が起こり、極端な水位上昇と次槽への液越流とを防ぐことができる。
【0017】
なお、時間経過と共に凸部3にも生物細胞(生物膜)が付着し、凸部3の穴(網目)も閉塞してくるが、この場合は、完全に水没している生物担体押え部材1を用いた場合に比べて、生物細胞(生物膜)の成長速度は緩やかである。また、一般家庭用では4ヶ月に1回又はそれ以上の頻度の保守点検が義務付けられているので、その際に、生物担体押え部材1の清掃を行うことによって汚水の流れを正常に保つことができる。
【0018】
図3は上記生物担体押え部材1を用いた汚水浄化槽の概略構成図である。次に、この図を参照して本発明の汚水浄化槽について説明する。
【0019】
汚水浄化槽は、上流側から、汚水中の沈降性固形物を重力下に沈降させる(嫌気的)沈殿分離槽第一室14、続いて沈殿分離第二室15があり、その後流に好気的に生物処理する好気処理槽10(上部に好気条件下で生物処理する生物反応室11が形成され、下部にSSを濾過して濾液を次槽へ移流させる濾過室12が形成されている)、処理水槽17、及び消毒槽18がある。これら各槽は、仕切壁9、4、5、37等によってそれぞれ仕切られている。但し、SSは浮遊性懸濁物質あるいは汚泥の意味である。
【0020】
なお、沈殿分離槽第一室14及び沈殿分離槽第二室15では、嫌気的生物分解機能を高めるために、槽内に充填材(生物担体、濾床)を充填することもできる。
【0021】
生物反応室11では、好気的微生物によって液中の有機物を分解除去する。槽内には、微生物の保持・増殖に好適な生物担体を充填し、好気濾床(微生物反応用)を形成させている。なお、この濾床は、生物担体が固定された固定床であっても、液とともに流動する流動床であってもよい。この際、好気的条件を維持させるためにブロワ20から散気部材(散気管)39を通して空気を吐出する。
【0022】
生物反応室11へ流れ込んだ液は、室内の好気濾床を下向流で流れる。そこで有機物が生物分解されると、その一部は汚泥に転換され、汚泥は増える。
【0023】
濾過室12では、生物反応室11から流れ込んだSSを濾過し、その濾液を次槽へ移流させる。汚泥を濾過・捕捉するため、濾過室12内には濾材を充填した濾過用濾床が形成されている。濾過用濾床を流れる流の方向は、下向流である。
【0024】
濾過用濾床に捕捉されたSSは蓄積すると閉塞等が起こるため、定期的に逆洗が必要となる。所定の時刻になると、タイマー41が働いてブロワ20が稼動し、逆洗管21及びエアリフトポンプ管(逆洗排液返送用)19の両方に空気を送り、逆洗する。逆洗排液はエアリフトポンプ管19を用いて沈殿分離槽第一室4へ返送する。
【0025】
消毒槽18では、消毒薬によって大腸菌や細菌等を殺菌消毒する。消毒後の処理液は、放流口42から汚水浄化槽外へ排出する。
【0026】
汚水浄化槽には、槽内の保守点検及び清掃を容易に行うことができるように、上部にマンホールが設けてあり、そのマンホールにはマンホールカバー13が取り付けられている。
【0027】
なお、図3の汚水浄化槽を用いて水位上昇実験した結果を図4のグラフを示した。
【0028】
【発明の効果】
本発明の生物担体押え部材は、構造が簡単であり、閉塞による越流が起こりにくい。
本発明の汚水浄化槽によれば、安定した汚水処理を行うことができ、また、保守点検時のサンプリングや、液中溶存酸素量、水素イオン濃度等の測定、水質の確認等も容易に行なえる。
【図面の簡単な説明】
【図1】本発明の生物担体押え部材の斜視図(A)及び縦断面図(B)。
【図2】本発明の生物担体押え部材を用いた好気処理槽の縦断面図。
【図3】図2の好気処理槽を組み込んだ汚水浄化槽。
【図4】図3の汚水浄化槽を用いた水位上昇実験結果のグラフ。
【図5】従来の生物担体押え部材を用いた汚水浄化槽の部分縦断面図。
【図6】従来の別例の生物担体押え部材を用いた汚水浄化槽の部分縦断面図。
【符号の説明】
1:生物担体押え部材 2:平面板状部
3:凸部 4、5:仕切板
6a、6b:生物担体支え(通水板)
7:外槽 8:生物担体 9:仕切板
10:好気処理槽(11+12)
11:(好気的)生物反応室 12:濾過室
13:マンホールカバー 14:沈殿分離槽第一室
15:沈殿分離槽第二室 17:処理水槽
18:消毒槽 19:エアリフトポンプ
20:ブロワ 21:逆洗管
24:(上)通水板 25:(中)通水板
26:(下)通水板 39:散気管
41:タイマー 42:放流口
WL:液面
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a biological carrier pressing member suitably used for a sewage septic tank that treats manure discharged from households and the like and other domestic wastewater (also simply referred to as sewage).
[0002]
[Prior art]
FIG. 5 is an example of a sewage septic tank (partial longitudinal sectional view) using a conventional biological carrier pressing member. As shown in the drawing, in the aerobic treatment tank 10 of the sewage purification tank, an upper part, a lower part, and a lower part are provided in order to hold and support a filled biological carrier (also referred to as a biofouling material, a filler, a contact material, or a filter medium). In addition, water passage plates 24, 25, and 26 are arranged in the middle portion, and a biological carrier is filled in a space portion sandwiched between the water passage plates, and a biological cell is attached to and propagated on the biological carrier, and wastewater These organic substances are decomposed and treated aerobically (for example, see Patent Document 1).
[0003]
FIG. 6 shows another example of a sewage septic tank (partial longitudinal sectional view) using a conventional biological carrier pressing member. In this case, a water flow plate 24 is installed above (above) the liquid level WL ( For example, see Patent Document 2).
[0004]
[Patent Document 1]
Japanese Patent Application Laid-Open No. 11-90113
[Patent Document 2]
Japanese Patent Laid-Open No. 2000-210690
[Problems to be solved by the invention]
However, as shown in FIG. 5, in the case where the biological carrier is pressed (upper) and the water flow plate 24 is arranged so as to be immersed in the liquid, the sewage concentration is high in the vicinity of the water flow plate 24 where the sewage flows (upper). Not only the (upper) water flow plate 24 but also biological cells (biofilm) adhere to it, and the holes (or meshes) of the upper water flow plate 24 may be blocked in some cases, and the sewage may be blocked by the blockage. Troubles such as overtopping will occur.
Further, in the case of the other example of FIG. 6, the hole (or mesh) of the water flow plate 24 can be blocked, but sampling at the time of maintenance and inspection, dissolved oxygen amount (BOD), hydrogen ion concentration (pH) in the liquid It is difficult to measure such as.
[0007]
The present invention is intended to solve these problems, and even if a large amount of biological cells (biofilm) adheres to the water flow plate, it is not completely blocked, and therefore the overflow to the next tank is prevented. It is possible to provide an upper water flow plate (that is, a biological carrier pressing member) that can be prevented or that can be easily sampled at the time of maintenance and inspection, and can easily measure BOD, pH, and the like in the liquid.
[0008]
[Means for Solving the Problems]
In order to achieve the above-mentioned problem, the present inventors have made various studies and devised that a part of the upper water flow plate (biological carrier pressing member) is always above the liquid level, thereby providing the upper water flow plate. The present invention has been completed with the idea that blockage of the holes (mesh) of the (biological carrier pressing member) can be prevented.
[0009]
That is, the present invention includes an aerobic treatment tank and a biological carrier pressing member disposed in the aerobic processing tank, and the biological carrier pressing member includes a flat plate-like portion and an upper portion from the flat plate-like portion. And the flat plate-like part is below the liquid level in the tank of the aerobic treatment tank, and a part of the convex part is below the liquid level in the tank during the operation of the aerobic treatment tank. It is a sewage septic tank installed so that it may be on the top.
[0011]
[Action]
In the biological carrier pressing member 1 according to the present invention, the convex portion 3 is formed so as to protrude upward from the flat plate-like portion 2, and a part of the biological carrier pressing member 1 is always immersed from the liquid without being immersed in the liquid. Is also above. Therefore, even if a biological cell (biofilm) adheres to the biological carrier holding member in the liquid and the hole (mesh) of the biological carrier holding member closes, the convex portion 3 above the liquid level has a hole (mesh). There is no blockage.
[0012]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, the present invention will be described more specifically with reference to the drawings.
FIG. 1 is a perspective view of a biological carrier pressing member 1 according to an example of the present invention. The biological carrier pressing member 1 has convex portions 3 (three locations in FIG. 1) protruding upward, and a part of the convex portions 3 is designed to be always above the liquid level WL in the tank. . In addition, the biological carrier holding member 1 has a number of holes (holes, slits, lattices, or meshes) smaller than the biological carrier filled in the tank so that sewage can freely pass through. It is a structure that does not pass through (the biological carrier is not washed away).
[0013]
Here, the (overall) plan view size of the biological carrier pressing member 1 is set to a size suitable for the plan view size of the aerobic treatment tank 10 in the sewage septic tank. Moreover, it is preferable that the convex part (protrusion part) 3 occupies the area of about 10% or more and 60% or less of the area of the biological carrier pressing member 1 in plan view. The height (L1) of the convex portion 3 varies depending on the size of the sewage septic tank, but when used for a general household septic tank, the height (L1) is approximately 10 to 100 mm exposed from the liquid level (WL).
[0014]
The material of the biological carrier pressing member 1 is usually made of polypropylene, polyethylene, polyvinyl chloride, or the like, and may be made of a metal such as stainless steel, galvanized, or copper. In addition, although the plate | board thickness of the biological carrier pressing member 1 changes with scales and materials, it is about 0.5-10 mm in general.
[0015]
FIG. 2 shows a portion of the aerobic treatment tank 10 of the sewage purification tank using the biological carrier presser member 1 of the present invention, when the liquid in the tank is in WL (during operation). The aerobic treatment tank 10 is surrounded by the partition plate 4, the partition plate 5, and the outer tank 7, and a biological carrier support (water passage plate) 6b for holding the biological carrier is arranged in the lower part and in the upper part. The biological carrier pressing member 1 is arranged, and another biological carrier support (water passage plate) 6a is arranged at an intermediate position separating the upper half from the lower half. The planar plate-like portion 2 of the biological carrier surface pressing member 1 is usually submerged under the WL, while a part of the convex portion 3 is exposed on the WL.
[0016]
And the flow of sewage is the flow A as shown in FIG. 2 normally. In the vicinity of the biological carrier holding member 1 into which a highly concentrated liquid flows, biological cells (biofilm) tend to adhere to the hole (mesh) part of the holding member 1, and this becomes enlarged over time, closing the hole (mesh). Let By the way, even if the hole (mesh) of the flat plate-like portion 2 of the biological carrier pressing member 1 is closed and the liquid level rises slightly, the convex portion 3 is raised to a position higher than WL. Like the flow B as shown in FIG. 2, the inflow (advection) of the liquid from the hole (mesh) in the convex portion 3 to the lower part of the tank occurs to prevent an extreme rise in water level and liquid overflow to the next tank. it can.
[0017]
In addition, as time passes, biological cells (biofilm) adhere to the convex portion 3 and the holes (mesh) of the convex portion 3 also close. In this case, the biological carrier pressing member 1 that is completely submerged. The growth rate of biological cells (biofilms) is slower than when using. In addition, in general households, maintenance inspections are required once every four months or more. At that time, it is possible to keep the flow of sewage normal by cleaning the biological carrier pressing member 1. it can.
[0018]
FIG. 3 is a schematic configuration diagram of a sewage septic tank using the biological carrier pressing member 1. Next, the sewage septic tank of the present invention will be described with reference to this figure.
[0019]
The sewage septic tank has, from the upstream side, a sedimentation separation tank first chamber 14 that sediments sedimentary solids in the sewage under gravity (anaerobic), followed by a sedimentation separation second chamber 15, and is aerobic in the downstream flow. An aerobic treatment tank 10 for biological treatment (a biological reaction chamber 11 for biological treatment under aerobic conditions is formed in the upper part, and a filtration chamber 12 for filtering SS and transferring the filtrate to the next tank is formed in the lower part. ), A treated water tank 17 and a disinfection tank 18. Each of these tanks is partitioned by partition walls 9, 4, 5, 37, etc. However, SS means suspended suspended matter or sludge.
[0020]
In the precipitation separation tank first chamber 14 and the precipitation separation tank second chamber 15, in order to enhance the anaerobic biodegradation function, the tank can be filled with a filler (biological carrier, filter bed).
[0021]
In the biological reaction chamber 11, organic substances in the liquid are decomposed and removed by aerobic microorganisms. The tank is filled with a biological carrier suitable for holding and growing microorganisms to form an aerobic filter bed (for microbial reaction). The filter bed may be a fixed bed to which a biological carrier is fixed or a fluidized bed that flows together with the liquid. At this time, in order to maintain the aerobic condition, air is discharged from the blower 20 through the air diffusion member (air diffusion pipe) 39.
[0022]
The liquid flowing into the biological reaction chamber 11 flows downward through the aerobic filter bed in the chamber. Then, when organic matter is biodegraded, a part of it is converted into sludge, and sludge increases.
[0023]
In the filtration chamber 12, the SS flowing from the biological reaction chamber 11 is filtered, and the filtrate is transferred to the next tank. In order to filter and capture the sludge, a filtration filter bed filled with a filter medium is formed in the filtration chamber 12. The direction of the flow through the filter bed is a downward flow.
[0024]
Since the SS trapped in the filter bed for filtration is clogged, clogging or the like occurs, so regular backwashing is necessary. When a predetermined time comes, the timer 41 is activated and the blower 20 is operated. Air is sent to both the backwash pipe 21 and the air lift pump pipe (for backwash drainage return) 19 to perform backwashing. The backwash drainage liquid is returned to the precipitation separation tank first chamber 4 using an air lift pump pipe 19.
[0025]
In the disinfecting tank 18, Escherichia coli, bacteria, and the like are sterilized and disinfected with a disinfectant. The treated liquid after disinfection is discharged out of the sewage septic tank from the outlet 42.
[0026]
The sewage septic tank is provided with a manhole at the top so that maintenance and cleaning inside the tank can be easily performed, and a manhole cover 13 is attached to the manhole.
[0027]
In addition, the graph of FIG. 4 showed the result of the water level rise experiment using the sewage septic tank of FIG.
[0028]
【The invention's effect】
The biological carrier pressing member of the present invention has a simple structure and is unlikely to overflow due to blockage.
According to the sewage septic tank of the present invention, stable sewage treatment can be performed, and sampling at the time of maintenance and inspection, measurement of dissolved oxygen amount in liquid, hydrogen ion concentration, etc., confirmation of water quality, etc. can be easily performed. .
[Brief description of the drawings]
FIG. 1 is a perspective view (A) and a longitudinal sectional view (B) of a biological carrier pressing member of the present invention.
FIG. 2 is a longitudinal sectional view of an aerobic treatment tank using the biological carrier pressing member of the present invention.
3 is a sewage purification tank incorporating the aerobic treatment tank of FIG.
FIG. 4 is a graph showing the results of a water level rise experiment using the sewage septic tank of FIG.
FIG. 5 is a partial longitudinal sectional view of a sewage septic tank using a conventional biological carrier pressing member.
FIG. 6 is a partial vertical cross-sectional view of a sewage septic tank using another conventional biological carrier pressing member.
[Explanation of symbols]
1: Biological carrier holding member 2: Planar plate-like portion 3: Projection 4, 5: Partition plates 6a, 6b: Biological carrier support (water flow plate)
7: Outer tank 8: Biological carrier 9: Partition plate 10: Aerobic treatment tank (11 + 12)
11: (aerobic) biological reaction chamber 12: filtration chamber 13: manhole cover 14: precipitation separation tank first chamber 15: precipitation separation tank second chamber 17: treated water tank 18: disinfection tank 19: air lift pump 20: blower 21 : Backwash pipe 24: (Upper) water flow plate 25: (Middle) water flow plate 26: (Lower) water flow plate 39: Air diffusion pipe 41: Timer 42: Outlet WL: Liquid level

Claims (1)

好気処理槽と、この好気処理槽内に配置される生物担体押え部材とを備え、上記生物担体押え部材が、平面板状部と、この平面板状部から上方に隆起した凸部とを有し、上記平面板状部が好気処理槽の槽内液面よりも下となり、上記凸部の一部が好気処理槽の運転中に槽内液面よりも上となるように設置される汚水浄化槽。An aerobic treatment tank and a biological carrier pressing member disposed in the aerobic processing tank, wherein the biological carrier pressing member includes a flat plate-like portion and a convex portion protruding upward from the flat plate-like portion; So that the flat plate-like part is below the liquid level in the tank of the aerobic treatment tank, and a part of the convex part is above the liquid level in the tank during the operation of the aerobic treatment tank. Sewage septic tank to be installed.
JP2003141816A 2003-05-20 2003-05-20 Wastewater septic tank Expired - Fee Related JP4307903B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2003141816A JP4307903B2 (en) 2003-05-20 2003-05-20 Wastewater septic tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2003141816A JP4307903B2 (en) 2003-05-20 2003-05-20 Wastewater septic tank

Publications (2)

Publication Number Publication Date
JP2004344706A JP2004344706A (en) 2004-12-09
JP4307903B2 true JP4307903B2 (en) 2009-08-05

Family

ID=33530076

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2003141816A Expired - Fee Related JP4307903B2 (en) 2003-05-20 2003-05-20 Wastewater septic tank

Country Status (1)

Country Link
JP (1) JP4307903B2 (en)

Also Published As

Publication number Publication date
JP2004344706A (en) 2004-12-09

Similar Documents

Publication Publication Date Title
KR101226547B1 (en) Sewage treatment system for marine use
JPS5816956B2 (en) Combined treatment and purification equipment for sewage liquid
JP2000005779A (en) Device of preventing clogging of filter media in biological filter tank and method thereof
KR101037888B1 (en) Hybrid wastewater treatment equipment with sedimentation, biological degradation, filtration, phosphorus removal and uv disinfection system in a reactor
JP3469797B2 (en) Sewage treatment method and apparatus
JP4307903B2 (en) Wastewater septic tank
JP4416984B2 (en) Sewage septic tank with filtration unit in the tank
JP2000354858A (en) Sewage treatment method and device therefor
JP4454825B2 (en) Wastewater purification tank and wastewater purification method
JP2006218435A (en) Activated sludge treatment system
JP3975393B2 (en) Wastewater septic tank
JP4075393B2 (en) Mountain-shaped airlift pump pipe and septic tank
KR970003588Y1 (en) Waste-water purifier
KR100272758B1 (en) Waste water treatment method and apparatus using upflow filtering biological bio-film process
JP4187889B2 (en) Aerobic filter bed tank and septic tank
KR950011768B1 (en) Waste water purifier
JP4128316B2 (en) Septic tank
JP4048559B2 (en) U-shaped air lift pump pipe and septic tank
JP4509460B2 (en) Solid-liquid separation tank having a filter bed and sewage septic tank provided with the same
JP4405130B2 (en) Two floor juxtaposed aerobic treatment tank and sewage septic tank with steps
JPH0639391A (en) Method for treating waste water
JP3356937B2 (en) Filtration membrane plate support structure
JP2002357200A (en) Air lift pump, flow regulating tank and septic tank provided with the same, and method for operating air lift pump
JPS5852000Y2 (en) Septic tank
KR100305361B1 (en) Household sewage treatment device

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20051117

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20071220

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20080117

A521 Written amendment

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20080213

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20080311

A521 Written amendment

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20080326

RD03 Notification of appointment of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7423

Effective date: 20080407

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20090421

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20090430

R150 Certificate of patent or registration of utility model

Free format text: JAPANESE INTERMEDIATE CODE: R150

Ref document number: 4307903

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120515

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130515

Year of fee payment: 4

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20140515

Year of fee payment: 5

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees