JP2001198600A - Sludge drying method - Google Patents

Sludge drying method

Info

Publication number
JP2001198600A
JP2001198600A JP2000007637A JP2000007637A JP2001198600A JP 2001198600 A JP2001198600 A JP 2001198600A JP 2000007637 A JP2000007637 A JP 2000007637A JP 2000007637 A JP2000007637 A JP 2000007637A JP 2001198600 A JP2001198600 A JP 2001198600A
Authority
JP
Japan
Prior art keywords
sludge
drying
water
shelf
container
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
JP2000007637A
Other languages
Japanese (ja)
Other versions
JP3616738B2 (en
Inventor
Masaru Miyamoto
勝 宮本
Toshihiro Wada
敏博 和田
Seiji Onishi
聖治 大西
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.)
MK KK
Original Assignee
MK KK
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 MK KK filed Critical MK KK
Priority to JP2000007637A priority Critical patent/JP3616738B2/en
Publication of JP2001198600A publication Critical patent/JP2001198600A/en
Application granted granted Critical
Publication of JP3616738B2 publication Critical patent/JP3616738B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Landscapes

  • Treatment Of Sludge (AREA)

Abstract

PROBLEM TO BE SOLVED: To solve the problem that many days have been taken to dry sludge in the sun in a concrete pool since the water from the sludge is evaporated only from the upper face. SOLUTION: Sludge A is introduced into a filter vessel 10 with a filter cloth 12 impermeable to sand and permeable to water and air laid over the inside, the sludge-containing filter vessel 1 is separated from the ground to drip the water in the sludge A through the filter cloth 12 by gravity, then the water remaining in the sludge A is evaporated from the upper face opened to the atmosphere and the contact face of the filter cloth 12, and the sludge is dried in the sun. Consequently, the evaporation area of the sludge A is increased, and the drying days are decreased.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本願発明は、例えば浄水場や
下水処理場、あるいは工場などで発生する汚泥を乾燥さ
せるための汚泥乾燥方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a sludge drying method for drying sludge generated in, for example, a water purification plant, a sewage treatment plant, or a factory.

【0002】[0002]

【従来の技術及び発明が解決しようとする課題】水中か
ら汲み上げられた汚泥は、含水率が95〜97%もあ
り、その高含水率のままでは次の処理が行えないので、
高含水汚泥は乾燥(あるいは脱水)させる必要がある。
従来から、汚泥乾燥方法として、汚泥を天日で自然乾燥
させる方法と、汚泥を機械的に圧縮濾過する方法とがあ
る。
2. Description of the Related Art Sludge pumped from water has a water content of as high as 95 to 97%, and the next treatment cannot be carried out with the high water content.
High water sludge needs to be dried (or dewatered).
Conventionally, sludge drying methods include a method of naturally drying sludge in the sun and a method of mechanically compressing and filtering sludge.

【0003】従来の天日乾燥による汚泥乾燥方法は、一
般にコンクリートプールの底に砂を敷き詰め、この敷砂
の上に汲み上げた汚泥を載せて天日乾燥させるようにし
ている。尚、汚泥中の水は、敷砂の空間を透過してプー
ル底から外に流れ出すとともに、空気に接触する汚泥上
面から水蒸気となって徐々に蒸発する。
[0003] In the conventional method of drying sludge by sun drying, generally, sand is spread on the bottom of a concrete pool, and the sludge pumped on the sand is dried in the sun. In addition, the water in the sludge permeates through the space of the bed sand and flows out from the pool bottom, and gradually evaporates as steam from the upper surface of the sludge which comes into contact with the air.

【0004】ところで、このような従来の天日による汚
泥乾燥方法では、プール中で乾燥させる汚泥はその上面
しか空気に接触していないので、蒸発による乾燥効率が
非常に悪い。因に、プール内において例えば厚さ50cm
程度の汚泥を天日乾燥させる場合には、季節によって長
短があるが1回当たり年平均で5〜6ケ月もかかり、し
かも汚泥の厚さが厚いと最終含水率が50%程度までし
か乾燥できない。
[0004] In such a conventional method of drying sludge by the sun, the sludge to be dried in the pool only contacts the air on the upper surface thereof, so that the drying efficiency by evaporation is very poor. By the way, in the pool, for example, 50cm in thickness
If the sludge is dried in the sun, it may take a long or short time depending on the season, but it takes 5 to 6 months on average each time, and if the sludge is thick, it can only be dried to a final moisture content of about 50%. .

【0005】又、このように、汚泥をプール内に入れて
天日乾燥させる方法では、単位面積当たりの汚泥量を多
くする(厚さを厚くする)と、汚泥中心部まで乾燥させ
る日数が加速度的に多く必要であり、汚泥乾燥場所の回
転効率が悪くなる(単位面積当たりの汚泥乾燥処理量が
少ない)。従って、従来の天日乾燥方法では、順次発生
する量の汚泥を乾燥処理するためにそれに見合う広面積
の処理場所を確保する必要があった。
[0005] In addition, in the method of drying the sun by putting sludge into a pool as described above, if the amount of sludge per unit area is increased (thickness is increased), the number of days for drying to the center of the sludge is accelerated. And the rotation efficiency of the sludge drying place is deteriorated (the sludge drying treatment amount per unit area is small). Therefore, in the conventional solar drying method, it is necessary to secure a large-area treatment place corresponding to the amount of the sludge that is sequentially generated in order to dry the sludge.

【0006】他方、汚泥を機械的に圧縮濾過する方法で
は、機械設備が大掛かりとなり、且つ濾過材に高圧力が
かかるのでその濾過材の耐久期間が短くなるので、汚泥
一単位当たりの乾燥処理コストが高価であるという問題
がある。
On the other hand, in the method of mechanically compressing and filtering sludge, the mechanical equipment becomes large and high pressure is applied to the filtering material, so that the durable period of the filtering material is shortened. However, there is a problem that it is expensive.

【0007】本願発明は、汚泥を天日乾燥させる際に、
汚泥中の水分の蒸発を促進させて時間当たりの乾燥効率
を向上させ得るようにした汚泥乾燥方法を提供すること
を第1の目的とし、小さい敷地面積で時間当たりの汚泥
乾燥処理量を多くできるようにした汚泥乾燥方法を提供
することを第2の目的としている。
[0007] The invention of the present application, when drying the sludge in the sun,
It is a first object of the present invention to provide a sludge drying method capable of improving the drying efficiency per hour by promoting the evaporation of water in the sludge, and can increase the sludge drying treatment amount per hour in a small site area. A second object is to provide a method for drying sludge as described above.

【0008】[0008]

【課題を解決するための手段】本願発明は、上記課題を
解決するための手段として次の構成を有している。本願請求項1の発明 本願請求項1の発明は、天日乾燥による汚泥乾燥方法を
対象にしている。そして、請求項1の汚泥乾燥方法で
は、砂の通過を阻止し且つ水及び空気の通過を許容する
濾布を敷いた濾過容器内に汚泥を収容し、その汚泥入り
濾過容器を地面から離間させて汚泥中の水を濾布を通し
て自然滴下させた後、汚泥中の残余の水分を大気に開放
された上面側及び濾布の接触面からそれぞれ蒸発させな
がら天日乾燥させるようにする。
The present invention has the following structure as means for solving the above-mentioned problems. The invention of claim 1 of the present application The invention of claim 1 of the present application is directed to a method of drying sludge by solar drying. According to the sludge drying method of the first aspect, sludge is contained in a filter container provided with a filter cloth which prevents passage of sand and allows water and air to pass therethrough, and separates the filter container containing the sludge from the ground. After the water in the sludge is naturally dropped through the filter cloth, the remaining moisture in the sludge is dried in the sun while evaporating from the upper surface open to the atmosphere and the contact surface of the filter cloth.

【0009】この請求項1の汚泥乾燥方法で使用される
濾過容器は、特に限定するものではないが、例えば2m
×3〜4m程度の面積で高さが20〜30cm程度の比較
的薄型のものがよい。そして、この濾過容器内には、汚
泥を例えば10〜20cmの範囲で充填する。
The filtration container used in the sludge drying method of the first aspect is not particularly limited, but is, for example, 2 m.
A relatively thin one having an area of about 3 to 4 m and a height of about 20 to 30 cm is preferable. Then, the filtration container is filled with sludge in a range of, for example, 10 to 20 cm.

【0010】汚泥入り濾過容器は、地面から離間させた
状態で自然乾燥させるが、水中から汲み出した汚泥を濾
過容器内に充填した当初は、汚泥中の水が濾過容器の濾
布を通して下方に滴下する。尚、濾過容器内の汚泥厚さ
が10〜20cm程度であれば、2〜3日程度で水の滴下
が終了する。そして、その後は汚泥の上面からだけでな
く、濾布の側周面及び底面からも汚泥中の水分が蒸発す
るようになる。即ち、本願請求項1の汚泥乾燥方法で
は、水の滴下終了後は汚泥における外気に接触する面積
(水分の蒸発面積)が大幅に広くなり、汚泥中の水分の
蒸発効率(乾燥効率)が良好となる。本願請求項2の発明 本願請求項2の発明は、上記請求項1の汚泥乾燥方法に
おいて、汚泥入り濾過容器を、上下に間隔をもって重合
配置させた複数の棚上をその下段棚側から上段棚側へ順
次移動させながら天日乾燥させるようにしている。
The filter container containing sludge is naturally dried while being separated from the ground, but when the sludge pumped from the water is filled in the filter container, water in the sludge drops downward through the filter cloth of the filter container. I do. In addition, if the sludge thickness in a filtration container is about 10-20 cm, dripping of water will be completed in about 2-3 days. After that, the water in the sludge evaporates not only from the top surface of the sludge but also from the side peripheral surface and the bottom surface of the filter cloth. That is, in the sludge drying method of claim 1 of the present application, after the completion of the dropping of water, the area of the sludge that comes into contact with the outside air (evaporation area of water) is greatly increased, and the evaporation efficiency (drying efficiency) of the water in the sludge is good. Becomes The invention according to claim 2 of the present invention is directed to the method for drying sludge according to claim 1, wherein a plurality of shelves in which filter containers containing sludge are superimposed and arranged at intervals above and below are arranged from the lower shelf side to the upper shelf side. Sun drying while moving sequentially to the side.

【0011】この請求項2の汚泥乾燥方法では、棚を2
段以上重合配置させた乾燥棟を使用する。又、この請求
項2の場合は、汚泥入り濾過容器を下段棚から順次上段
棚側へ移動させるのにリフター装置を使用するとよい。
そして、水中から汲み出したばかりの高含水の汚泥入り
濾過容器は、最下段の棚上に載せてそこで数日間水切り
をし、水の滴下が終わったものを順次上段側の棚上に移
動させていく。尚、各棚が満杯状態では、最上段の乾燥
済みの汚泥入り濾過容器を棚から除去した後、次段の汚
泥入り濾過容器を上段棚に載せ変えていけばよい。
In the sludge drying method according to the second aspect, the shelves are
Use a drying building with more than one stage. In the case of the second aspect, a lifter device may be used to sequentially move the sludge-containing filtration container from the lower shelf to the upper shelf.
Then, the high-hydrated sludge filtration container that has just been pumped out of the water is placed on the bottom shelf, drained there for several days, and the ones that have been dropped are sequentially moved to the upper shelf. . When the shelves are full, it is only necessary to remove the uppermost dried sludge-containing filtration container from the shelf, and then place the next sludge-containing filtration container on the upper shelf.

【0012】この請求項2の発明の汚泥乾燥方法では、
上下に重合する複数の棚上でそれぞれ汚泥入り濾過容器
を乾燥させるようにしているので、単位敷地面積当たり
の汚泥乾燥処理量が多くなり、敷地を有効利用できる。本願請求項3の発明 本願請求項3の発明は、上記請求項1の汚泥乾燥方法に
おいて、汚泥入り濾過容器を上下に間隔をもって重合配
置させた複数の棚上にそれぞれ載せて、各汚泥入り濾過
容器をそれぞれ定位置で天日乾燥させるようにしてい
る。
In the method for drying sludge according to the second aspect of the present invention,
Since the sludge-containing filtration container is dried on a plurality of shelves vertically polymerized, the sludge drying treatment amount per unit site area increases, and the site can be used effectively. The invention according to claim 3 of the present invention is directed to the method for drying sludge according to claim 1, wherein the sludge-containing filtration containers are placed on a plurality of shelves, each of which is superimposed and arranged at an interval above and below, and each sludge-containing filtration container is filtered. Each container is dried in the sun in a fixed position.

【0013】又、この請求項3の汚泥乾燥方法では、上
下の棚間に屋根板を配置して、上段棚に載せられた汚泥
入り濾過容器から滴下する水が下段棚に載せられている
汚泥入り濾過容器内に入らないようにしながら天日乾燥
させる。
In the method for drying sludge according to the third aspect of the present invention, the roof plate is disposed between the upper and lower shelves, and the water dropped from the filter container containing the sludge placed on the upper shelf is placed on the lower shelf. Dry in the sun while keeping out of the filter container.

【0014】この請求項3の汚泥乾燥方法では、各棚に
は水切りしていない汚泥入り濾過容器がそのまま載せら
れるために汚泥中の水が濾過容器の濾布を通して滴下す
るが、その滴下した水はその上段棚と下段棚との間に設
置している屋根板で受け止められる。従って、上段棚上
の汚泥入り濾過容器側から滴下した水が下段棚上の汚泥
入り濾過容器内に入ることがなく、それぞれ各棚(定位
置)で乾燥させるようにしたものであっても、滴下する
水で下段側の汚泥の乾燥速度が遅くなることがない。
尚、この請求項3の汚泥乾燥方法でも、上下に重合する
複数の棚上でそれぞれ汚泥入り濾過容器を乾燥させるよ
うにしているので、小さい敷地面積で効率よく天日乾燥
させることができる。
In the sludge drying method according to the third aspect of the present invention, the water in the sludge is dropped through the filter cloth of the filter container because the filter container with sludge which has not been drained is placed on each shelf as it is. Is received by the shingle installed between the upper shelf and the lower shelf. Therefore, even if the water dropped from the sludge-filled filter container on the upper shelf does not enter the sludge-filled filter container on the lower shelf, the water is dried on each shelf (fixed position). The dripping water does not slow down the drying speed of the lower sludge.
In the sludge drying method according to the third aspect, the sludge-containing filtration container is dried on a plurality of shelves that vertically polymerize, so that the sun can be efficiently dried in a small site area.

【0015】[0015]

【発明の実施の形態】図1〜図6を参照して本願実施形
態の汚泥乾燥方法を説明すると、図1及び図2には第1
実施形態(請求項1に対応する)が示され、図3及び図
4には第2実施形態(請求項2に対応する)が示され、
図5及び図6には第3実施形態(請求項3に対応する)
が示されている。第1実施形態 第1実施形態の汚泥乾燥方法は、例えば図1に示すよう
な濾過容器10を使用して行う。この濾過容器10は、
細鉄筋を四角形の浅皿状に組付けて形成した受け籠11
と、その受け籠11内に収容される浅皿容器形の濾布1
2とで構成されている。尚、濾過容器10の大きさ及び
形状は、特に限定するものではないが、図1及び図2に
示す実施形態では、2m×3m程度の面積を有する四角
形で高さが20cm程度の大きさのものを使用している。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The sludge drying method according to an embodiment of the present invention will be described with reference to FIGS.
An embodiment (corresponding to claim 1) is shown, and FIGS. 3 and 4 show a second embodiment (corresponding to claim 2),
5 and 6 show a third embodiment (corresponding to claim 3).
It is shown. First Embodiment The sludge drying method according to the first embodiment is performed using, for example, a filtration container 10 as shown in FIG. This filtration container 10
Receiving basket 11 formed by assembling fine steel bars in a rectangular shallow dish shape
And a shallow dish-shaped filter cloth 1 housed in the receiving basket 11
And 2. The size and shape of the filtration container 10 are not particularly limited, but in the embodiment shown in FIGS. 1 and 2, a square having an area of about 2 m × 3 m and a height of about 20 cm is used. Use things.

【0016】濾布12は、砂の通過を阻止する一方、液
体及び空気の通過を許容するようなメッシュ状の濾材で
形成されている。受け籠11は、濾布12の保形性を確
保するためのものであり、濾布12が受け籠11内に過
不足なく収まるようになっている。
The filter cloth 12 is formed of a mesh-shaped filter medium that blocks passage of sand and allows passage of liquid and air. The receiving basket 11 is for ensuring the shape retention of the filter cloth 12, and the filter cloth 12 fits in the receiving basket 11 without any excess or shortage.

【0017】図2に示す第1実施形態の汚泥乾燥方法
は、次のようにして行う。まず、図1に示す受け籠11
内に濾布12を組付けで濾過容器10を構成しておき、
その濾過容器10内に所定量(例えば15cm程度の厚
さ)の汚泥Aを収容する。次に、その汚泥入り濾過容器
1を棚13上に載せて地面から離間させる。すると、初
期段階では、汚泥A中の水が符号Wで示すように濾布1
2を通して自然滴下するが、例えば汚泥Aの厚さが10
〜15cm程度であれば、2〜3日程度で水Wの滴下が停
止する。そして、その後は、汚泥A中の残余の水分を、
それぞれ符号Sで示すように大気に開放された上面側及
び濾布接触面(側周面及び下面)から蒸発させながら天
日乾燥させる。
The sludge drying method of the first embodiment shown in FIG. 2 is performed as follows. First, the receiving basket 11 shown in FIG.
The filter container 10 is configured by assembling the filter cloth 12 therein,
A predetermined amount (for example, a thickness of about 15 cm) of the sludge A is stored in the filtration container 10. Next, the sludge-containing filtration container 1 is placed on the shelf 13 and separated from the ground. Then, in the initial stage, as shown by the symbol W, the water in the sludge A
2 is dropped naturally, for example, when the thickness of sludge A is 10
If it is about 15 cm, the dripping of water W stops in about 2 to 3 days. And after that, the residual moisture in the sludge A is
As indicated by reference symbol S, the solar cell is dried in the sun while evaporating from the upper surface side and the filter cloth contact surface (side peripheral surface and lower surface) opened to the atmosphere.

【0018】従って、本願第1実施形態の汚泥乾燥方法
によれば、汚泥を天日乾燥させるのに、汚泥Aを濾過容
器10に入れて乾燥させるようにしているので、汚泥A
が外気に接触する面積(水分の蒸発面積)が大幅に広く
なり、汚泥中の水分の蒸発効率が良好となる(乾燥時間
が短縮される)。
Therefore, according to the sludge drying method of the first embodiment of the present invention, the sludge A is put into the filtration vessel 10 and dried in order to dry the sludge in the sun.
However, the area (evaporation area of water) in contact with the outside air is greatly increased, and the efficiency of evaporation of water in the sludge is improved (the drying time is shortened).

【0019】尚、汚泥Aを濾過容器10内に15cm程度
の厚さで収容した場合の実験では、4〜5日程度経過し
たときに乾燥汚泥Aに亀裂が発生し始め、外気に接触す
る面積が一層広くなって蒸発作用がさらに促進された。
そして、1カ月後には汚泥Aの含水率が23.6%にな
った。ところで、汚泥Aがここまで乾燥すると、粉砕す
れば汚泥成分がパウダー状になる。従って、この乾燥汚
泥を例えばレンガの原料として使用するときには、他の
材料との混和性が良好となる。第2実施形態 図3及び図4に示す第2実施形態の汚泥乾燥方法は、上
記第1実施形態の汚泥乾燥方法(汚泥Aを濾過容器10
内に入れて乾燥させる方法)を複数の棚上を移動させな
がら天日乾燥させるようにしたものである。
In the experiment in which the sludge A was stored in the filtration container 10 at a thickness of about 15 cm, cracks began to be generated in the dried sludge A after about 4 to 5 days, and the area in contact with the outside air was started. And the evaporation effect was further promoted.
Then, one month later, the water content of the sludge A became 23.6%. By the way, when the sludge A is dried so far, the sludge component becomes powdery when crushed. Therefore, when this dried sludge is used, for example, as a raw material for bricks, the miscibility with other materials is improved. Second Embodiment The sludge drying method according to the second embodiment shown in FIG. 3 and FIG.
(The method of drying by placing in a cabinet) and drying on the sun while moving on a plurality of shelves.

【0020】即ち、この第2実施形態では、複数の棚2
1〜24を上下に重合配置させた乾燥棟2を使用して行
う。即ち、図3及び図4に示す実施形態では、乾燥棟2
は、上下に4段の棚21,22,23,24を有し、且
つ各棚21〜24にそれぞれ3枚の汚泥入り濾過容器1
を載せるスペースを有している。又、この乾燥棟2の左
右各端部には、汚泥入り濾過容器1を各段の棚21〜2
4の高さまで昇降させるためのリフター装置25L,2
5Rがそれぞれ配置されている。この各リフター装置2
5L,25Rは、汚泥入り濾過容器1を載せるための載
せ台26L(又は26R)を昇降させるためのもので、
図示例ではパンタグラフ式のものを採用している。そし
て、各リフター装置25L,25Rにより、左右の載せ
台26L,26Rをそれぞれ図4に符号L1〜L4(又は
1〜R4)で示すように各段の棚21〜24と同高さに
合致させ得るようにしている。又、各載せ台26L,2
6Rには、それぞれ汚泥入り濾過容器1を各棚21〜2
4に出し入れするための給排装置27L(又は27R)
が設けられている。
That is, in the second embodiment, a plurality of shelves 2
The drying is performed by using a drying ridge 2 in which 1 to 24 are arranged one above the other. That is, in the embodiment shown in FIG. 3 and FIG.
Has four shelves 21, 22, 23, and 24 at the top and bottom, and each of the shelves 21 to 24 has three filtration containers 1 containing sludge.
Has a space for mounting. At the left and right ends of the drying building 2, filtration containers 1 containing sludge are placed on shelves 21 to 2 of each stage.
Lifter device 25L, 2 for raising and lowering to the height of 4
5R are arranged respectively. This lifter device 2
5L and 25R are for raising and lowering the mounting table 26L (or 26R) for mounting the sludge-containing filtration container 1, and
In the illustrated example, a pantograph type is adopted. Each lifter device 25L, the 25R, left and right of the platform 26L, code L 1 26R to each view 4 ~L 4 (or R 1 to R 4) flush with the shelf 21 to 24 of each stage, as shown by So that it can be matched. Also, each mounting table 26L, 2
6R, the filtration container 1 containing sludge is placed on each of the shelves 21 to 2
Supply / discharge device 27L (or 27R) for taking in and out of 4
Is provided.

【0021】そして、この第2実施形態の汚泥乾燥方法
は、次のようにして行う。まず、高含水の汚泥Aを濾過
容器10に入れ、→その汚泥入り濾過容器1を左側リフ
ター装置25Lの載せ台26Lに載せ、→その汚泥入り
濾過容器1を給排装置27Lで第1段棚21の入口21
aから該第1段棚21上に送り込む。同様に、第1段棚
21上には、順次玉突き状に3つの汚泥入り濾過容器1
を送り込む。この状態では、第1段棚21に載せられて
いる各汚泥入り濾過容器1,1,1の汚泥A(図2)中
の水が濾布12(図1、図2)を通して滴下し、2〜3
日後には汚泥入り濾過容器1からの水の滴下が終了す
る。
Then, the sludge drying method of the second embodiment is performed as follows. First, the sludge A having a high water content is put into the filtration vessel 10, and the filtration vessel 1 containing the sludge is placed on the mounting table 26L of the left lifter device 25L. The filtration vessel 1 containing the sludge is placed on the first shelf by the supply / discharge device 27L. 21 entrance 21
a to the first shelf 21. Similarly, on the first shelf 21, three sludge-filled filtration containers 1 are sequentially stacked in a bead shape.
Send. In this state, water in the sludge A (FIG. 2) of each of the sludge-containing filtration containers 1, 1, 1 placed on the first shelf 21 drops through the filter cloth 12 (FIGS. 1, 2), and ~ 3
After a day, the dripping of the water from the sludge-containing filtration container 1 ends.

【0022】その後に、左側載せ台26Lに次の高含水
汚泥入り濾過容器1を載せてその汚泥入り濾過容器1を
第1段棚21の入口21a側に送り込む。すると、第1
段棚21の出口21bにある水切り済みの汚泥入り濾過
容器1が右側載せ台26R上に押し出され、→その汚泥
入り濾過容器1を載せた右側載せ台26Rを右側リフタ
ー装置25Rで第2段棚22の高さ(符号R2の高さ)
まで上昇させ、→給排装置27Rを送り込み側に作動さ
せて汚泥入り濾過容器1を第2段棚22の入口22aに
送り込む。同様に、第1段棚21の入口21aへの高含
水汚泥入り濾過容器1の送り込み動作と、第1段棚21
の出口21bからの水切り済み汚泥入り濾過容器1の右
側載せ台26R上への排出動作とを行わせ、→右側載せ
台26Rを符号R2の高さまで上昇させ、→その汚泥入
り濾過容器を第2段棚22の入口22a側に送り込む。
そのとき、先に第2段棚22上に載せられている汚泥入
り濾過容器1は、玉突き状に奥側に押される。
Thereafter, the next filtration container 1 containing high-humidity sludge is placed on the left-hand support 26L, and the filtration container 1 containing sludge is sent to the inlet 21a side of the first shelf 21. Then, the first
The drained sludge-containing filtration container 1 at the outlet 21b of the step shelf 21 is pushed out onto the right-side support 26R, and the right-side support 26R on which the sludge-containing filter container 1 is mounted is moved to the second stage shelf by the right lifter device 25R. height of 22 (height of the sign R 2)
And the supply / discharge device 27R is operated to the feed side to feed the sludge-containing filtration container 1 to the inlet 22a of the second shelf 22. Similarly, the operation of feeding the filtration container 1 containing high-humidity sludge into the inlet 21a of the first shelf 21 and the operation of the first shelf 21
To perform the discharge operation and from the outlet 21b to the draining already sludge containing filtering vessel 1 of the right stand 26R on, raising the → right stand 26R to the height of the code R 2, → the sludge containing the filtering vessel first It is sent to the entrance 22a side of the second shelf 22.
At this time, the sludge-containing filtration container 1 previously placed on the second shelf 22 is pushed to the back side in a ball-shaped manner.

【0023】順次、同様にして、第1段棚21の入口2
1aから高含水汚泥入り濾過容器1を送り込むととも
に、各段の棚にある汚泥入り濾過容器1を順次水平移動
又は段上げさせて、最終的に図4に示す各段の棚21〜
24にそれぞれ汚泥入り濾過容器1を満杯にして天日乾
燥させる。尚、汚泥入り濾過容器1が、第1段棚21の
入口21aに送り込まれた後、最上段棚24の出口24
bから押し出されるまでに1ケ月程度をかけて移動させ
るようにすると、濾過容器10内の汚泥Aを十分な乾燥
度合いまで乾燥させることができる。
In the same manner, the entrance 2 of the first shelf 21
1a, the filtration container 1 containing high water content sludge is sent in, and the filtration container 1 containing sludge in each shelf is sequentially moved or raised horizontally, and finally the shelves 21 to 21 shown in FIG.
24, the sludge-filled filtration container 1 is filled and dried in the sun. After the sludge-containing filtration container 1 is sent into the inlet 21a of the first shelf 21, the outlet 24 of the uppermost shelf 24 is turned off.
If it takes about one month to be extruded before being extruded from b, the sludge A in the filtration container 10 can be dried to a sufficient degree of drying.

【0024】最上段棚24の出口24b部分にある乾燥
済みの汚泥入り濾過容器1は、次のようにして排出され
る。即ち、左側載せ台26Lを符号L4の高さまで上動
させておき、第3段棚23の出口23bから排出される
汚泥入り濾過容器1を右側載せ台26Rに載せた状態で
符号R4の高さまで上動させ、右側載せ台26R上の汚
泥入り濾過容器1を給排装置27Rで最上段棚24の入
口24a側に送り込むことで、最上段棚24の出口24
bにあった乾燥済みの汚泥入り濾過容器1を玉突き状に
左側載せ台26L上に移乗させる。尚、高さL4の位置
において左側載せ台26L上に載せた汚泥入り濾過容器
1は、該左側載せ台26Lを降下させる途中で自動的に
反転(裏返し)させて、濾過容器10内の乾燥汚泥Aを
所定の容器(あるいはトラック荷台)に移し替えるよう
にしてもよい。
The dried sludge-containing filtration container 1 at the outlet 24b of the uppermost shelf 24 is discharged as follows. That is, the left stand 26L up to the height of the code L 4 allowed to move upward, the sign R 4 in a state carrying the sludge-containing filtration container 1 is discharged from the outlet 23b of the third Dantana 23 to the right stand 26R The sludge-filled filtration container 1 on the right-hand mounting table 26R is sent to the inlet 24a side of the uppermost shelf 24 by the supply / discharge device 27R.
Then, the dried sludge-containing filtration container 1 corresponding to b is transferred to the left-hand mounting table 26L in the shape of a bead. Incidentally, the sludge-containing filtration container 1 placed on the left stand 26L at the position of the height L 4 are, halfway automatically invert (turn over) to lower the left side stand 26L, drying of the filter vessel 10 The sludge A may be transferred to a predetermined container (or truck bed).

【0025】このように、汚泥入り濾過容器1を各段棚
21〜24の下段側から上段側に順次移動させながら天
日乾燥させるようにすると、当初の高含水汚泥入り濾過
容器1から滴下する水が第1段棚21部分で完全に切れ
てしまい、第2段棚22以上の高さに載せられている汚
泥入り濾過容器1から水が滴下することがない。又、上
下に重合する複数の棚21〜24上でそれぞれ汚泥入り
濾過容器1を乾燥させるようにしているので、単位敷地
面積当たりの汚泥乾燥処理量が多くなり、敷地を有効利
用できる。第3実施形態 図5及び図6に示す第3実施形態の汚泥乾燥方法は、上
記第1実施形態の汚泥乾燥方法(汚泥Aを濾過容器10
内に入れて乾燥させる方法)を複数の棚上にそれぞれ定
置状態で載せて天日乾燥させるようにしたものである。
As described above, when the sludge-containing filtration container 1 is dried in the sun while being sequentially moved from the lower stage to the upper stage of each of the shelves 21 to 24, the sludge is dropped from the initial filtration container 1 containing high water content sludge. Water is completely cut off at the first shelf 21 and water does not drop from the sludge-containing filtration container 1 placed at a height higher than the second shelf 22. In addition, since the sludge-containing filtration container 1 is dried on a plurality of shelves 21 to 24 that are vertically polymerized, the sludge drying treatment amount per unit site area increases, and the site can be used effectively. Third Embodiment The sludge drying method according to the third embodiment shown in FIG. 5 and FIG.
And drying it in the sun by placing it on a plurality of shelves in a fixed state.

【0026】この第3実施形態では、例えば上下2段の
棚31,32を有した乾燥棟3を使用する。この乾燥棟
3の各段の棚31,32には、図5に示すように前後に
3区画と図6に示すように左右に2区画の合計6区画づ
つの汚泥入り濾過容器1の載置スペースを設けている。
尚、他の実施形態では、乾燥棟3における棚31,32
の段数や各棚31,32における汚泥入り濾過容器1の
載置スペース数は、適宜に設計変更できることは勿論で
ある。
In the third embodiment, for example, a drying building 3 having two upper and lower shelves 31, 32 is used. On the shelves 31 and 32 of each stage of the drying building 3, there are placed the sludge-containing filtration container 1 having a total of six sections, three sections in front and rear as shown in FIG. 5 and two sections on the left and right as shown in FIG. Space is provided.
In other embodiments, the shelves 31, 32 in the drying building 3 are used.
Of course, and the number of spaces for placing the sludge-containing filtration container 1 on each of the shelves 31 and 32 can of course be changed as appropriate.

【0027】又、この第3実施形態では、図6に示すよ
うに左右2基のリフター装置25L,25Rを使用して
いるが、この各リフター装置25L,25Rは、乾燥棟
3の長さ方向(図5の左右方向)に走行可能となってい
る。尚、このリフター装置の構造は、基本的に図4のも
のとほぼ同機能を有しており、各棚31,32に汚泥入
り濾過容器1を出し入れし得るようになっている。
In the third embodiment, two left and right lifters 25L and 25R are used as shown in FIG. (The left-right direction in FIG. 5). The structure of the lifter device basically has substantially the same function as that shown in FIG. 4, and the sludge-containing filtration container 1 can be taken in and out of the shelves 31 and 32.

【0028】この乾燥棟3には、上下の棚31,32間
に屋根板33を配置している。この各棚31,32間の
屋根板33は、上段棚32に載せられた汚泥入り濾過容
器1から滴下する水が下段棚31載せられる汚泥入り濾
過容器1上に入るのを防止するものであり、上段棚32
の面積をカバーできる面積を有している。
In the drying building 3, a roof plate 33 is arranged between upper and lower shelves 31, 32. The roof plate 33 between the shelves 31 and 32 prevents water dripping from the sludge-filled filtration container 1 placed on the upper shelf 32 from entering the sludge-filled filtration container 1 placed on the lower shelf 31. , Upper shelf 32
Has an area that can cover the area of

【0029】そして、この第3実施形態の汚泥乾燥方法
では、各棚31,32には水切りしていない汚泥入り濾
過容器1をそのまま載せるが、そのとき、汚泥A(図
2)中の水が濾過容器10の濾布12を通して滴下す
る。ところが、その滴下した水は、その上段棚32と下
段棚31との間に設置している屋根板33で受け止めら
れ、上段棚32上の汚泥入り濾過容器1側から滴下した
水が下段棚31上の汚泥入り濾過容器1内に入ることが
ない。従って、汚泥入り濾過容器1をそれぞれ各棚3
1,32上の定位置で乾燥させるようにしたものであっ
ても、滴下する水で下段側の汚泥の乾燥速度が遅くなる
ことがない。尚、この第3実施形態の汚泥乾燥方法で
も、上下に重合する複数の棚31,32上でそれぞれ汚
泥入り濾過容器1を乾燥させるようにしているので、小
さい敷地面積で効率よく天日乾燥させることができる。
Then, in the sludge drying method of the third embodiment, the sludge-filled filtration container 1 which is not drained is placed on the shelves 31 and 32 as it is, and at this time, water in the sludge A (FIG. 2) is discharged. The solution is dropped through the filter cloth 12 of the filter container 10. However, the dropped water is received by the roof plate 33 installed between the upper shelf 32 and the lower shelf 31, and the water dropped from the sludge-filled filtration container 1 on the upper shelf 32 becomes the lower shelf 31. It does not enter the upper sludge-containing filtration container 1. Therefore, the sludge-containing filtration container 1 is stored in each of the shelves 3
Even if the drying is performed at a fixed position on the first and the second 32, the dripping water does not slow down the drying speed of the lower sludge. In the sludge drying method of the third embodiment as well, the sludge-containing filtration container 1 is dried on a plurality of shelves 31 and 32 which are vertically polymerized, so that the sun is efficiently dried on a small site area. be able to.

【0030】[0030]

【発明の効果】本願発明の汚泥乾燥方法は、次のような
効果がある。請求項1の発明の効果 本願請求項1の発明の汚泥乾燥方法は、濾布12を敷い
た濾過容器10内に汚泥Aを収容し、その汚泥入り濾過
容器1を地面から離間させて汚泥A中の水を濾布12を
通して自然滴下させた後、汚泥A中の残余の水分を天日
乾燥させるようにしている。
The sludge drying method of the present invention has the following effects. According to the method for drying sludge of the present invention, sludge A is contained in a filter container 10 covered with a filter cloth 12, and the sludge-containing filter container 1 is separated from the ground to remove sludge A. After allowing the water inside to drop naturally through the filter cloth 12, the remaining water in the sludge A is dried in the sun.

【0031】従って、本願請求項1の汚泥乾燥方法によ
れば、高含水汚泥A中の水を濾布12で水切りでき、さ
らにそれに続いて天日乾燥させるときに、汚泥Aの上面
からだけでなく濾布12の側周面及び底面からも汚泥中
の水分を蒸発させることができるので、汚泥の乾燥効率
が良好となる(乾燥日数を短くできる)という効果があ
る。請求項2の発明の効果 本願請求項2の発明は、上記請求項1の濾過容器10を
使用した汚泥乾燥方法において、汚泥入り濾過容器1
を、上下に間隔をもって重合配置させた複数の棚上をそ
の下段棚21側から上段棚24側へ順次移動させながら
天日乾燥させるようにしている。
Therefore, according to the sludge drying method of the first aspect of the present invention, the water in the highly hydrated sludge A can be drained by the filter cloth 12, and then when it is dried in the sun, only from the upper surface of the sludge A. In addition, since the water in the sludge can be evaporated from the side peripheral surface and the bottom surface of the filter cloth 12, there is an effect that the drying efficiency of the sludge is improved (the drying days can be shortened). According to the second aspect of the present invention, in the method for drying sludge using the filtration container 10 according to the first aspect, the filtration container 1 containing sludge is used.
Are dried in the sun while being sequentially moved from the lower shelf 21 side to the upper shelf 24 side on a plurality of shelves which are superposed and arranged at intervals vertically.

【0032】従って、この請求項2の汚泥乾燥方法で
は、高含水の汚泥入り濾過容器1は、最下段の棚21上
で水切りできるとともに、複数段の各棚上でそれぞれ汚
泥入り濾過容器1を乾燥させることができるので、単位
敷地面積当たりの汚泥乾燥処理量が多くなり、敷地を有
効利用できるという効果がある。請求項3の発明の効果 本願請求項3の発明は、上記請求項1の濾過容器10を
使用した汚泥乾燥方法において、汚泥入り濾過容器1
を、上下に間隔をもって重合配置させた複数の棚31,
32上にそれぞれ載せるとともに、上下の棚31,32
間に屋根板33を配置して、上段棚32に載せられた汚
泥入り濾過容器1から滴下する水が下段棚31に載せら
れている汚泥入り濾過容器1内に入らないようにしなが
ら天日乾燥させるようにしている。
Therefore, in the sludge drying method of the present invention, the high-water content sludge filtration container 1 can be drained on the lowermost shelf 21 and the sludge-containing filtration container 1 can be separated on each of a plurality of stages. Since it can be dried, the sludge drying treatment amount per unit site area increases, and there is an effect that the site can be used effectively. Effect of the invention of claim 3 The invention of claim 3 of the present application is directed to a method for drying sludge using the filtration container 10 according to claim 1, wherein the filtration container 1 with sludge is provided.
, A plurality of shelves 31,
32, and the upper and lower shelves 31, 32
A roof plate 33 is interposed between the filters to prevent the water dripping from the sludge-filled filter container 1 placed on the upper shelf 32 from entering the sludge-filled filter container 1 placed on the lower shelf 31 while drying in the sun. I try to make it.

【0033】このように、上下の棚31,32間に屋根
板33を配置しておくと、上段棚上の汚泥入り濾過容器
側から滴下した水が下段棚上の汚泥入り濾過容器内に入
ることがなく、それぞれ各棚の定位置で乾燥させるよう
にしたものであっても、滴下する水で下段側の汚泥の乾
燥速度が遅くなることがない。又、この請求項3の汚泥
乾燥方法でも、上下に重合する複数の棚31,32上で
それぞれ汚泥入り濾過容器1を乾燥させるようにしてい
るので、小さい敷地面積で効率よく天日乾燥させること
ができるという効果がある。
As described above, when the roof plate 33 is disposed between the upper and lower shelves 31 and 32, water dropped from the sludge-containing filtration container on the upper shelf enters the sludge-containing filtration container on the lower shelf. Therefore, even if each shelf is dried at a fixed position on each shelf, the dripping water does not slow down the drying speed of the lower sludge. Also, in the sludge drying method of the third aspect, since the sludge-containing filtration container 1 is dried on the plurality of shelves 31 and 32 that are vertically polymerized, it is possible to efficiently dry the sun on a small site area. There is an effect that can be.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本願第1実施形態の汚泥乾燥方法で使用される
濾過容器の斜視図である。
FIG. 1 is a perspective view of a filtration container used in a sludge drying method according to a first embodiment of the present application.

【図2】図1の濾過容器を使用して行う汚泥乾燥方法の
説明図である。
FIG. 2 is an explanatory diagram of a sludge drying method performed using the filtration container of FIG.

【図3】本願第2実施形態の汚泥乾燥方法で使用される
乾燥棟の平面図である。
FIG. 3 is a plan view of a drying building used in a sludge drying method according to a second embodiment of the present application.

【図4】図3のIV−IV矢視図である。FIG. 4 is a view taken in the direction of arrows IV-IV in FIG. 3;

【図5】本願第3実施形態の汚泥乾燥方法で使用される
乾燥棟の側面図である。
FIG. 5 is a side view of a drying building used in a sludge drying method according to a third embodiment of the present application.

【図6】図5のVI−VI矢視図である。6 is a view taken in the direction of arrows VI-VI in FIG. 5;

【符号の説明】[Explanation of symbols]

1は汚泥入り濾過容器、2は乾燥棟、3は乾燥棟、10
は濾過容器、11は受け籠、12は濾布、21〜24は
棚、31〜32は棚、Aは汚泥である。
1 is a filtration container containing sludge, 2 is a drying building, 3 is a drying building, 10
Is a filter container, 11 is a receiving basket, 12 is a filter cloth, 21 to 24 are shelves, 31 to 32 are shelves, and A is sludge.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 砂の通過を阻止し且つ水及び空気の通過
を許容する濾布(12)を敷いた濾過容器(10)内に
汚泥(A)を収容し、その汚泥入り濾過容器(1)を地
面から離間させて汚泥(A)中の水を濾布(12)を通
して自然滴下させた後、汚泥(A)中の残余の水分を大
気に開放された上面側及び濾布(12)の接触面からそ
れぞれ蒸発させながら天日乾燥させるようにしたことを
特徴とする汚泥乾燥方法。
A sludge (A) is accommodated in a filter container (10) provided with a filter cloth (12) for preventing the passage of sand and allowing the passage of water and air, and the filter container (1) containing the sludge. ) Is separated from the ground, and the water in the sludge (A) is allowed to drop naturally through the filter cloth (12). Then, the remaining moisture in the sludge (A) is removed from the upper surface and the filter cloth (12) which are open to the atmosphere. A method for drying sludge, characterized in that it is dried in the sun while evaporating from respective contact surfaces of the sludge.
【請求項2】 請求項1において、汚泥入り濾過容器
(1)を、上下に間隔をもって重合配置させた複数の棚
(21〜24)上をその下段棚(21)側から上段棚
(24)側へ順次移動させながら天日乾燥させるように
したことを特徴とする汚泥乾燥方法。
2. The upper shelf (24) according to claim 1, wherein a plurality of shelves (21 to 24) in which the sludge-containing filtration containers (1) are polymerized and arranged at intervals vertically are arranged from the lower shelf (21) side. A sludge drying method characterized by drying in the sun while sequentially moving to the side.
【請求項3】 請求項1において、汚泥入り濾過容器
(1)を、上下に間隔をもって重合配置させた複数の棚
(31,32)上にそれぞれ載せるとともに、上下の棚
(31,32)間に屋根板(33)を配置して、上段棚
(32)に載せられた汚泥入り濾過容器(1)から滴下
する水が下段棚(31)に載せられている汚泥入り濾過
容器(1)内に入らないようにしながら天日乾燥させる
ようにしたことを特徴とする汚泥乾燥方法。
3. The sludge-containing filter container (1) according to claim 1, wherein the sludge-containing filter container (1) is placed on a plurality of shelves (31, 32), which are vertically arranged at intervals, and between the upper and lower shelves (31, 32). The roof plate (33) is arranged on the upper shelf (32), and water dripping from the sludge-containing filtration container (1) placed on the upper shelf (32) is placed in the sludge-containing filtration container (1) placed on the lower shelf (31). A method for drying sludge, characterized in that it is dried in the sun while not entering the sludge.
JP2000007637A 2000-01-17 2000-01-17 Sludge drying equipment Expired - Lifetime JP3616738B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000007637A JP3616738B2 (en) 2000-01-17 2000-01-17 Sludge drying equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000007637A JP3616738B2 (en) 2000-01-17 2000-01-17 Sludge drying equipment

Publications (2)

Publication Number Publication Date
JP2001198600A true JP2001198600A (en) 2001-07-24
JP3616738B2 JP3616738B2 (en) 2005-02-02

Family

ID=18536010

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000007637A Expired - Lifetime JP3616738B2 (en) 2000-01-17 2000-01-17 Sludge drying equipment

Country Status (1)

Country Link
JP (1) JP3616738B2 (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007160215A (en) * 2005-12-14 2007-06-28 Mk:Kk Method and apparatus for drying sludge
JP2007160214A (en) * 2005-12-14 2007-06-28 Mk:Kk Method and apparatus for automatically carrying treated sludge to drying container
JP2007160211A (en) * 2005-12-14 2007-06-28 Mk:Kk Method and apparatus for automatically carrying treated sludge to drying container
JP2009101276A (en) * 2007-10-22 2009-05-14 Metawater Co Ltd Sludge dryer and sludge drying method
JP2010234271A (en) * 2009-03-31 2010-10-21 Fujita Corp Method for drying and storing organic material
CN109734235A (en) * 2019-02-25 2019-05-10 北京朗净时代环境科技有限公司 A kind of desulfurization wastewater zero discharge filtering apparatus

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007160215A (en) * 2005-12-14 2007-06-28 Mk:Kk Method and apparatus for drying sludge
JP2007160214A (en) * 2005-12-14 2007-06-28 Mk:Kk Method and apparatus for automatically carrying treated sludge to drying container
JP2007160211A (en) * 2005-12-14 2007-06-28 Mk:Kk Method and apparatus for automatically carrying treated sludge to drying container
JP4625758B2 (en) * 2005-12-14 2011-02-02 株式会社エムケイ Method and apparatus for automatically carrying treated sludge into a drying container
JP4625759B2 (en) * 2005-12-14 2011-02-02 株式会社エムケイ Method and apparatus for automatically carrying treated sludge into a drying container
JP4637012B2 (en) * 2005-12-14 2011-02-23 株式会社エムケイ Sludge drying method and drying apparatus
JP2009101276A (en) * 2007-10-22 2009-05-14 Metawater Co Ltd Sludge dryer and sludge drying method
JP2010234271A (en) * 2009-03-31 2010-10-21 Fujita Corp Method for drying and storing organic material
CN109734235A (en) * 2019-02-25 2019-05-10 北京朗净时代环境科技有限公司 A kind of desulfurization wastewater zero discharge filtering apparatus
CN109734235B (en) * 2019-02-25 2024-05-07 北京朗净时代环境科技有限公司 Desulfurization waste water zero release filter equipment

Also Published As

Publication number Publication date
JP3616738B2 (en) 2005-02-02

Similar Documents

Publication Publication Date Title
CA2529073A1 (en) Greening apparatus
EP1301441B1 (en) Process using an oriented structure for treating waste water
JP2001198600A (en) Sludge drying method
CN105464169A (en) Inserting-type micro water retention accumulation regulating module
JP3107724U (en) Sludge drying equipment
CN107628693A (en) A kind of multistage filtering absorbing treatment device for life low-pollution water
CN108751479A (en) A kind of Multifunctional rural sewage treatment device
GB2453149A (en) A Reed Bed formed of Reed bed modules
KR20140078884A (en) The bottom fountain of grass
CN2446123Y (en) Water purifying appts.
US20220212968A1 (en) Trickling filter system
JPH0737759Y2 (en) Biological filtration equipment
JP3113242U (en) Sludge dehydration drying equipment
Carpenter Sludge drying on open and covered drying beds
RU2264372C2 (en) Vermicomposting device for a complete purification plant
JPS6244798Y2 (en)
JP2001162295A (en) Sewage treatment apparatus
CN211987388U (en) Novel sewage treatment system
CN211733999U (en) Emergency water storage tank structure of water dispenser with separation function
CN211570387U (en) Integrated sewage treatment device
CN220736393U (en) Novel plant extract sewage purification treatment device
CN218810937U (en) Building site rain sewage purification recycle device
CN207296599U (en) Environmental protection wall component and environmental protection wall
CN210065356U (en) Solid-liquid separation device for environmental improvement
CA2410541C (en) An oriented structure for treating a fluid

Legal Events

Date Code Title Description
A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20040709

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20040727

A521 Written amendment

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20040913

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: 20041012

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20041108

R150 Certificate of patent or registration of utility model

Free format text: JAPANESE INTERMEDIATE CODE: R150

Ref document number: 3616738

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: 20071112

Year of fee payment: 3

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

Free format text: PAYMENT UNTIL: 20081112

Year of fee payment: 4

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

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

Free format text: PAYMENT UNTIL: 20081112

Year of fee payment: 4

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

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

Free format text: PAYMENT UNTIL: 20081112

Year of fee payment: 4

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

Free format text: PAYMENT UNTIL: 20091112

Year of fee payment: 5

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: 20101112

Year of fee payment: 6

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: 20101112

Year of fee payment: 6

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

Free format text: PAYMENT UNTIL: 20111112

Year of fee payment: 7

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: 20111112

Year of fee payment: 7

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

Free format text: PAYMENT UNTIL: 20121112

Year of fee payment: 8

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: 20121112

Year of fee payment: 8

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

Free format text: PAYMENT UNTIL: 20131112

Year of fee payment: 9

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

EXPY Cancellation because of completion of term