JPH0224600B2 - - Google Patents
Info
- Publication number
- JPH0224600B2 JPH0224600B2 JP56059179A JP5917981A JPH0224600B2 JP H0224600 B2 JPH0224600 B2 JP H0224600B2 JP 56059179 A JP56059179 A JP 56059179A JP 5917981 A JP5917981 A JP 5917981A JP H0224600 B2 JPH0224600 B2 JP H0224600B2
- Authority
- JP
- Japan
- Prior art keywords
- screw
- sludge
- dewatering
- section
- dehydration
- 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 - Lifetime
Links
- 239000010802 sludge Substances 0.000 claims description 42
- 230000018044 dehydration Effects 0.000 claims description 27
- 238000006297 dehydration reaction Methods 0.000 claims description 27
- 238000010438 heat treatment Methods 0.000 claims description 14
- 238000000034 method Methods 0.000 claims description 14
- 239000007789 gas Substances 0.000 description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- 229920000620 organic polymer Polymers 0.000 description 5
- 230000007423 decrease Effects 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 230000000813 microbial effect Effects 0.000 description 4
- 125000002091 cationic group Chemical group 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 230000006835 compression Effects 0.000 description 2
- 238000007906 compression Methods 0.000 description 2
- 239000008394 flocculating agent Substances 0.000 description 2
- 230000016615 flocculation Effects 0.000 description 2
- 238000005189 flocculation Methods 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 239000002912 waste gas Substances 0.000 description 2
- 238000004220 aggregation Methods 0.000 description 1
- 230000002776 aggregation Effects 0.000 description 1
- 125000000129 anionic group Chemical group 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 239000010800 human waste Substances 0.000 description 1
- 238000004080 punching Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
Landscapes
- Treatment Of Sludge (AREA)
Description
本発明は好気性微生物処理装置や、嫌気性微生
物処理装置などから発生する有機性汚泥をスクリ
ユープレス型脱水機を用いて脱水する方法に関す
るものである。
従来から用いられているスクリユープレス型脱
水機はたとえば第1図に示したようなものであ
り、一端にホツパーなどを付設した汚泥の投入口
1を有し、他端に脱水ケーキの排出口2を有する
パンチングメタルなどからなる外筒3内に、軸受
4,5によつて回転自在に支持したスクリユー軸
6を付設し、当該スクリユー軸6に排出口2側の
径を大とし、投入口1側の径を小としたスクリユ
ー胴7を装着するとともに、当該スクリユー胴7
にスクリユー羽根8をスパイラル状に巻設したも
のである。このようなスクリユープレス型脱水機
で汚泥を脱水処理する場合は、あらかじめ有機高
分子凝集剤などで凝集せしめた凝集汚泥を投入口
1から投入しつつスクリユー軸6を減速機を介し
たモータ(図示せず)などでゆつくり回転させる
もので、このようにすると凝集汚泥中の比較的離
脱しやすい水分は投入口1近辺の自然脱水部Aに
おいてまず過作用により外筒3の過孔9から
除かれる。次いで凝集汚泥はスクリユー羽根8に
よつて排出口2の方向に押し出されるが、スクリ
ユー胴7と外筒3とから形成される圧搾脱水部B
において、その容積が排出部2に近ずくにつれて
除々に小さくなつているので、凝集汚泥も徐々に
圧搾され、当該汚泥に残留している水分が外筒3
の過孔9から滲出して脱水がなされ、脱水ケー
キが排出口2より押出されてくる。また従来のス
クリユープレス型脱水機においては第1図に示し
たようにスクリユー軸6の一端に付設した送気管
10からたとえば蒸気などの加熱ガスを流入し、
当該加熱ガスをスクリユー軸6とスクリユー胴7
とから構成される空間部11に噴出口13から噴
出せしめ、廃ガスを排気管12から排出すること
により、当該脱水機内部の凝集汚泥全体を加熱し
ながら脱水処理することも行なわれており、この
ようにすると水の粘度が低下したり、汚泥に添加
した有機高分子凝集剤と汚泥との凝集反応速度が
速くなつたりして脱水性が向上するとされてい
る。
好気性微生物処理装置や嫌気性微生物処理装置
などから発生する有機性汚泥を当該脱水機によつ
て脱水処理する場合も以上のような理由により、
従来から当該汚泥に各種の有機高分子凝集剤を加
えて凝集せしめた後、脱水機内部の凝集汚泥全体
を加熱しながら脱水処理しているが、上記したよ
うな有機性汚泥と有機高分子凝集剤とが反応して
生じた凝集汚泥の場合はこれを加熱すると特に投
入口近辺の自然脱水部Aにおける過作用による
脱水効果が低下し、全体の脱水率を低下せしめる
原因となることを知見した。
ただし、まつたく加熱しないと圧搾脱水部Bに
おける脱水効果が低下するので、有機性汚泥の場
合は汚泥の入口側付近を加熱せずに、圧搾脱水部
Bのみを加熱する時だけが最も脱水効果が上昇す
ることを知見した。
本発明は以上の知見に基づいて構成したもの
で、過孔を多数有する外筒内に、スクリユー羽
根を付設したスクリユー胴を回転可能に設けると
ともに、汚泥の投入口より排出口に向つて汚泥の
自然脱水部と圧搾脱水部を形成したスクリユープ
レス型脱水機を用いて有機性汚泥を脱水するにあ
たり、当該自然脱水部を加熱することなく、圧搾
脱水部のみを加熱して脱水処理することを特徴と
する有機性汚泥の脱水方法に関するものである。
以下に本発明を図面に従つて詳細に説明する。
第2図は本発明の脱水方法に用いるスクリユー
プレス型脱水機の一例を示す断面図であり、1は
投入口、2は排出口、3はパンチングメタルなど
からなる外筒、4,5は軸受、6はスクリユー
軸、7はスクリユー胴、8はスクリユー羽根、9
は過孔であり、この部分の構成は従来のスクリ
ユープレス型脱水機と全く同様である。但し、本
発明に用いる当該脱水機は第2図に示したよう
に、投入口1近辺の自然脱水部Aと外筒3とスク
リユー胴7から形成する圧搾脱水部Bとの間の、
スクリユー軸6とスクリユー胴7とから構成する
空間部11内に熱遮蔽壁14を付設することによ
り当該空間部を11aおよび11bに分割し、ま
たスクリユー胴6の一端に付設する送気管10を
延長し、その噴出口13を空間部11b内に付設
し、自然脱水部Aを加熱しないように構成する。
なお12は廃ガスの排気管であり一端を排出口2
側の空間部11b内に開口させ、他端を外部で開
口させる。なお加熱ガスとして蒸気を用いる場合
は排気管12の他端にスチームトラツプ(図示せ
ず)を付設する。
次に本発明の脱水方法を説明すると、有機性汚
泥にカチオン性、アニオン性あるいはノニオン性
から選ばれる1種ないし2種の有機高分子凝集剤
を添加撹拌して凝集せしめ、当該凝集汚泥を投入
口1から投入する。またスクリユー軸6をゆつく
り回転させ、かつ送気管10から蒸気などの加熱
ガスを流入する。前述したように当該脱水機にお
いては空間部11aには加熱ガスが接触しないの
で自然脱水部A内の凝集汚泥は加熱されず当該汚
泥に共存している比較的離脱しやすい水分を過
作用により効率よく脱水する。次いでこのように
水分が低下した凝集汚泥は圧搾脱水部Bへと次々
に押出すが、凝集汚泥は当該圧搾脱水部Bに到達
してはじめて加熱され、この加熱により凝集汚泥
中に残留している水分が滲出しやすくなり過孔
9より残留水分が滲出し、脱水ケーキを排出口2
から排出する。なお加熱温度としては有機性汚泥
の種類によつても多少変わるが、空間部11b内
の凝集物の汚泥が40〜90℃となるようにするとよ
い。
以上説明したように本発明の脱水方法は汚泥の
投入ホツパー近辺の自然脱水部Aを加熱しないの
で、従来のスクリユープレス型脱水機に生じてい
た自然脱水部Aにおける脱水効率の低下が解消
し、他の部分はまつたく同一条件とした従来の脱
水方法と比較して排出口2から排出される脱水ケ
ーキの含水率を低下させることができる。また従
来の脱水方法は空間部11aも加熱していたの
で、送気管10から流入する熱ガス中の熱量の1
部分が自然脱水部Aに共存する多量の水分の温度
を上昇させるために消費され、熱量的に不経済で
あつたが、本発明では自然脱水部Aにおいてあら
かじめ脱水した凝集汚泥のみを圧搾脱水部Bに到
達してはじめて加熱するのでそれだけ水分が低下
しており、したがつて加熱ガスとして蒸気を用い
る場合は当該蒸気の使用量を節約でき、ランニン
グコストも低下せしめることができるという効果
も奏する。
なお第2図に示した実施態様においては圧搾脱
水部Bを加熱するのに加熱ガスを用いたが、これ
にかぎらず、たとえば圧搾脱水部Bに相当するス
クリユー胴7の内面に電熱線を付設して加熱して
もさしつかえない。また場合によつては熱遮蔽板
14をやや圧搾脱水部Bよりに付設し、比較的低
圧の圧搾脱水部Bも加熱しないようにしてもさし
つかえない。
以下に本発明の効果をより明確にするために実
施例を説明する。
実施例
し尿処理場の余剰活性汚泥(外観茶褐色、PH
7.2、MLSS1.8%、強熱減量76.1%)を用い、カ
チオン性有機高分子凝集剤を固形物に対して0.6
%添加して凝集処理し、この凝集汚泥を下記の条
件で脱水処理した。
(1) 使用したスクリユープレス型脱水機
外筒の内径 300mm
スクリユー胴の全長 3000mm
スクリユー胴の小径 180mm
スクリユー胴の大径 260mm
(2) スクリユー胴の回転速度 0.36rpm
(3) 凝集物のフイード量 0.96m3/H
以上の様な条件で本発明方法として第2図に示
したようにスクリユー胴の途中から蒸気を導入
し、自然脱水部を加熱することなく、圧搾脱水部
に存在する凝集汚泥が80℃になるように加熱して
脱水処理した。また従来方法として第1図に示し
たようにスクリユー胴の小径部付近から蒸気を導
入し、自然脱水部も加熱するとともに、圧搾脱水
部に存在する凝集汚泥が80℃になるように加熱し
たもの、およびスクリユー胴に蒸気を導入するこ
となく常温にて脱水処理したものの2者について
行なつた。これらの脱水結果を第1表に示した。
The present invention relates to a method for dewatering organic sludge generated from an aerobic microbial treatment device, an anaerobic microbial treatment device, etc. using a screw press type dehydrator. A conventionally used screw press type dehydrator is, for example, as shown in Figure 1, and has a sludge inlet 1 equipped with a hopper at one end, and a dewatered cake outlet at the other end. A screw shaft 6 rotatably supported by bearings 4 and 5 is attached to an outer cylinder 3 made of punching metal or the like having a diameter of 1. A screw cylinder 7 with a smaller diameter on the first side is installed, and the screw cylinder 7
A screw blade 8 is wound around the screw blade 8 in a spiral shape. When dewatering sludge using such a screw press type dehydrator, flocculated sludge that has been flocculated with an organic polymer flocculant or the like is fed into the input port 1, and the screw shaft 6 is moved by a motor ( (not shown), etc. In this way, the water in the flocculated sludge that is relatively easy to separate is first released from the through hole 9 of the outer cylinder 3 due to overaction in the natural dewatering section A near the inlet 1. removed. Next, the flocculated sludge is pushed out in the direction of the discharge port 2 by the screw blades 8, but the flocculated sludge is pushed out in the direction of the discharge port 2 by the screw cylinder 7 and the outer cylinder 3.
Since the volume of the sludge gradually decreases as it approaches the discharge section 2, the flocculated sludge is also gradually squeezed, and the water remaining in the sludge is removed from the outer cylinder 3.
Water oozes out from the through hole 9, dewatering is performed, and a dehydrated cake is extruded from the discharge port 2. Furthermore, in the conventional screw press type dehydrator, as shown in FIG.
The heated gas is transferred to the screw shaft 6 and the screw barrel 7.
The waste gas is ejected from the spout 13 into the space 11 composed of It is said that when this is done, the viscosity of water is reduced, the rate of aggregation reaction between the organic polymer flocculant added to the sludge and the sludge is increased, and the dewatering performance is improved. For the reasons mentioned above, when organic sludge generated from an aerobic microbial treatment device or an anaerobic microbial treatment device is dehydrated using the dehydrator,
Traditionally, various organic polymer flocculants have been added to the sludge to cause it to flocculate, and then the entire flocculated sludge inside the dehydrator is heated and dehydrated. It was found that heating the flocculated sludge produced by the reaction with the sludge reduces the dewatering effect due to overaction, especially in the natural dewatering section A near the input port, which causes a decrease in the overall dewatering rate. . However, if you do not heat the sludge thoroughly, the dehydration effect in the press dewatering section B will decrease, so in the case of organic sludge, the best dehydration effect is achieved only when only the press dewatering section B is heated without heating the vicinity of the sludge inlet side. was found to increase. The present invention was constructed based on the above findings, and includes a rotatable screw barrel equipped with screw blades in an outer cylinder having a large number of perforations, and a screw cylinder equipped with screw blades that is rotatably disposed within an outer cylinder having a large number of perforations. When dewatering organic sludge using a screw press type dehydrator that has a natural dehydration section and a press dehydration section, it is possible to perform dehydration by heating only the press dehydration section without heating the natural dehydration section. The present invention relates to a method for dewatering organic sludge. The present invention will be explained in detail below with reference to the drawings. FIG. 2 is a sectional view showing an example of a screw press type dehydrator used in the dewatering method of the present invention, in which 1 is an inlet, 2 is an outlet, 3 is an outer cylinder made of punched metal, etc., and 4 and 5 are Bearing, 6 is screw shaft, 7 is screw body, 8 is screw blade, 9
is a through hole, and the structure of this part is exactly the same as that of a conventional screw press type dehydrator. However, as shown in FIG. 2, the dehydrator used in the present invention has a dewatering section between the natural dehydrating section A near the input port 1 and the compressing dehydrating section B formed from the outer cylinder 3 and the screw body 7.
By installing a heat shielding wall 14 in the space 11 consisting of the screw shaft 6 and the screw body 7, the space is divided into 11a and 11b, and the air pipe 10 attached to one end of the screw body 6 is extended. However, the spout 13 is provided inside the space 11b, and the natural dehydration section A is configured not to be heated.
Note that 12 is an exhaust pipe for waste gas, and one end is connected to the exhaust port 2.
It is opened into the side space 11b, and the other end is opened outside. If steam is used as the heating gas, a steam trap (not shown) is attached to the other end of the exhaust pipe 12. Next, to explain the dewatering method of the present invention, one or two types of organic polymer flocculants selected from cationic, anionic, or nonionic are added to organic sludge and stirred to cause flocculation, and the flocculated sludge is introduced. Insert from mouth 1. Further, the screw shaft 6 is slowly rotated, and heated gas such as steam is introduced from the air pipe 10. As mentioned above, in this dehydrator, the heated gas does not come into contact with the space 11a, so the flocculated sludge in the natural dewatering section A is not heated, and the water coexisting in the sludge that is relatively easy to separate is efficiently removed by overaction. Dehydrate well. Next, the flocculated sludge whose water content has been reduced in this way is pushed out one after another to the press dewatering section B, but the flocculated sludge is heated only after reaching the press dewatering section B, and due to this heating, the flocculated sludge remains in the flocculated sludge. Moisture easily oozes out, and residual moisture oozes out from through hole 9, and the dehydrated cake is discharged from outlet 2.
discharge from. Although the heating temperature varies somewhat depending on the type of organic sludge, it is preferable that the temperature of the aggregated sludge in the space 11b is 40 to 90°C. As explained above, since the dewatering method of the present invention does not heat the natural dewatering section A near the sludge input hopper, the decrease in dewatering efficiency in the natural dewatering section A that occurs in conventional screw press type dehydrators is eliminated. The moisture content of the dehydrated cake discharged from the discharge port 2 can be lowered compared to the conventional dehydration method under the same conditions in other parts. In addition, in the conventional dehydration method, the space 11a was also heated, so 1 of the amount of heat in the hot gas flowing from the air pipe 10
However, in the present invention, only the flocculated sludge that has been previously dehydrated in the natural dewatering section A is transferred to the compressed dewatering section. Since heating is performed only after reaching B, the moisture content is reduced accordingly. Therefore, when steam is used as the heating gas, the amount of steam used can be saved, and running costs can also be reduced. In the embodiment shown in FIG. 2, heating gas is used to heat the compression dehydration section B, but the present invention is not limited to this. For example, heating wires may be attached to the inner surface of the screw barrel 7 corresponding to the compression dehydration section B. It is okay to heat it. Further, in some cases, the heat shielding plate 14 may be attached slightly closer to the compressing and dehydrating section B so that the relatively low pressure compressing and dehydrating section B is not heated. Examples will be described below to make the effects of the present invention more clear. Example Surplus activated sludge from a human waste treatment plant (brown in appearance, PH
7.2, MLSS 1.8%, loss on ignition 76.1%), and a cationic organic polymer flocculant of 0.6% for solids.
% was added for flocculation treatment, and the flocculated sludge was dehydrated under the following conditions. (1) Inner diameter of the outer cylinder of the screw press type dehydrator used: 300 mm Total length of the screw cylinder: 3000 mm Small diameter of the screw cylinder: 180 mm Large diameter of the screw cylinder: 260 mm (2) Rotational speed of the screw cylinder: 0.36 rpm (3) Feed amount of aggregates 0.96m 3 /H Under the above conditions, the method of the present invention introduces steam from the middle of the screw barrel as shown in Figure 2, and removes the flocculated sludge present in the press dewatering section without heating the natural dewatering section. The sample was heated to 80°C for dehydration. In addition, as a conventional method, as shown in Figure 1, steam is introduced from near the small diameter part of the screw barrel to heat the natural dewatering section as well as the flocculated sludge present in the press dewatering section to a temperature of 80°C. , and one which was dehydrated at room temperature without introducing steam into the screw barrel. The dehydration results are shown in Table 1.
【表】
第1表に示したごとく本発明方法は自然脱水
部、圧搾脱水部ともに加熱しないもの、あるいは
自然脱水部、圧搾脱水部ともに加熱したものの従
来の脱水方法と比較してケーキの含水率は小さ
く、また自然脱水部、圧搾脱水部ともに加熱する
従来の脱水方法と比較して蒸気の使用量を6.5割
も節約することができ、脱水処理のランニングコ
ストを低下させることができた。[Table] As shown in Table 1, the method of the present invention has a higher cake moisture content compared to conventional dehydration methods in which neither the natural dehydration section nor the press dehydration section is heated, or when both the natural dehydration section and the press dehydration section are heated. The system is small, and compared to the conventional dehydration method that heats both the natural dehydration section and the compressed dehydration section, the amount of steam used can be reduced by 6.50%, reducing the running cost of the dehydration process.
第1図は従来のスクリユープレス型脱水機の断
面図、第2図は本発明に用いるスクリユープレス
型脱水機の断面図を示す。
1……投入口、2……排出口、3……外筒、
4,5……軸受、6……スクリユー軸、7……ス
クリユー胴、8……スクリユー羽根、9……過
孔、10……送気管、11……空間部、12……
排気管、13……噴出口、14……遮蔽壁、A…
…自然脱水部、B……圧搾脱水部。
FIG. 1 is a sectional view of a conventional screw press type dehydrator, and FIG. 2 is a sectional view of a screw press type dehydrator used in the present invention. 1... Input port, 2... Outlet port, 3... Outer cylinder,
4, 5... Bearing, 6... Screw shaft, 7... Screw body, 8... Screw blade, 9... Through hole, 10... Air supply pipe, 11... Space, 12...
Exhaust pipe, 13... spout, 14... shielding wall, A...
... Natural dehydration section, B... Pressure dehydration section.
Claims (1)
根を付設したスクリユー胴を回転可能に設けると
ともに、汚泥の投入口より排出口に向つて汚泥の
自然脱水部と圧搾脱水部を形成したスクリユープ
レス型脱水機を用いて有機性汚泥を脱水するにあ
たり、当該自然脱水部を加熱することなく、圧搾
脱水部のみを加熱して脱水処理することを特徴と
する有機性汚泥の脱水方法。1. A screw press in which a screw barrel equipped with screw blades is rotatably installed in an outer cylinder having a large number of through holes, and a natural sludge dewatering section and a pressing dewatering section are formed from the sludge input port toward the discharge port. A method for dewatering organic sludge, which is characterized in that when organic sludge is dehydrated using a type dehydrator, the dewatering process is performed by heating only the press dehydration part without heating the natural dehydration part.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56059179A JPS57174198A (en) | 1981-04-21 | 1981-04-21 | Dehydrating method for organic sludge |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56059179A JPS57174198A (en) | 1981-04-21 | 1981-04-21 | Dehydrating method for organic sludge |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS57174198A JPS57174198A (en) | 1982-10-26 |
| JPH0224600B2 true JPH0224600B2 (en) | 1990-05-30 |
Family
ID=13105907
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP56059179A Granted JPS57174198A (en) | 1981-04-21 | 1981-04-21 | Dehydrating method for organic sludge |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS57174198A (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS59135891U (en) * | 1983-03-02 | 1984-09-11 | 荏原インフイルコ株式会社 | Screw press type dehydrator |
| KR100442810B1 (en) * | 2002-03-27 | 2004-08-04 | 주식회사 덕진엔지니어링 | Dehydrate process and apparatus of erosional refuse for sewage disposal |
| JP6639330B2 (en) * | 2016-05-30 | 2020-02-05 | 水ing株式会社 | Dehydration system and dehydration method |
-
1981
- 1981-04-21 JP JP56059179A patent/JPS57174198A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS57174198A (en) | 1982-10-26 |
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