JPS6336300B2 - - Google Patents
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- Publication number
- JPS6336300B2 JPS6336300B2 JP58245581A JP24558183A JPS6336300B2 JP S6336300 B2 JPS6336300 B2 JP S6336300B2 JP 58245581 A JP58245581 A JP 58245581A JP 24558183 A JP24558183 A JP 24558183A JP S6336300 B2 JPS6336300 B2 JP S6336300B2
- Authority
- JP
- Japan
- Prior art keywords
- sand
- storage tank
- hydrocyclone
- separated
- solids
- 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.)
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Description
本発明は、液体中に混入している固形物を遠心
力によつて効率よく分離し、固形物のみを回収す
る固形物等の分離回収方法に関するもので、従来
用いられている方法よりシステム的に一槽簡略化
し、固形物の回収効率ならびに回収固形物の性状
を飛躍的に向上させることを目的とするものであ
る。
さらに詳しくは、本発明は有機物及び砂分等を
含んだ下水等を処理するに当り、液体サイクロン
を用い固形物を分離し、該サイクロン下部に液体
サイクロンと気密に直結させた分離貯留槽内に固
形物を貯留し、前記分離貯留槽内の負圧により大
気下より吸引されるバブリング用空気を分離貯留
槽内に導入し、分離した固形物を洗滌し、洗滌分
離固形物を脱水すると共に系外に排出する方法と
からなり、固形物の回収効率の向上と、固形物の
洗滌ならびに液体サイクロンのアンダーフロー流
量を零とし連続的に固形物等の分離回収を行うこ
とを目的としたもので、その方法は簡単で、広範
囲にわたる液体中の固形物の分離、洗滌及び回収
操作を連続的に可能にした方法を提供するもので
ある。
従来一般に用いられている汚泥中等の除砂方法
を第1図に基いて説明する。第1図は汚泥除砂装
置の系統説明図である。図において、1は液体サ
イクロンで、汚泥と砂分を遠心力により分離する
機能を備えている。2はあらかじめ木片、金属等
の大きな夾雑物を除いた砂を含んだ汚泥、すなわ
ち、砂分を除去しようとする原汚泥の入口管であ
る。この入口管2からの流入流分Q2は液体サイ
クロン1の内部で遠心加速により砂分と泥分に分
離、分級され、そのうち比重の小さい泥分は、液
体サイクロン1の上部出口管3から流出流分Q3
となつて系外の次の工程へ排出される。他方、比
重の大きい砂分は、液体サイクロン1の下部出口
管4から流入流分Q4となつてアンダートラフ5
にて回収される。このアンダートラフ5は、下部
流出流分Q4に含有される泥分と砂分を再度沈降
分離する機能を有するが、泥分はアンダートラフ
5の上部出口管7から流出流分Q7となつて、前
段のプロセスすなわち流入流分Q2とほぼ同等の
泥質を有する箇所へ戻される。
一方、アンダートラフ5で沈降した砂分は、砂
分搬出用コンベア6によつて移送され、コンベア
6の運転諸元によつて差はあるが、傾斜の有する
位置エネルギーによりある程度の脱水機能が働
き、コンベア6の上部に設けた排出口8より回収
砂Sとして回収される。
以上が従来固形物として砂等を含有する汚泥中
より砂を分離回収する方法の例であるが、この場
合の問題点を以下に述べる。
前述の方法を用いた東京都内の某処理場の沈澱
池引抜き汚泥を用いた試験の典型的な処理結果で
は、円筒部の径D1が152mm(6吋)の液体サイク
ロン1を用いた場合、50%分離限界粒子径d50が
約140(μm)程度、液体サイクロン1の砂分回収
率は79.4%と比較的満足できるものであつた。し
かしながら、この79.4%の砂分と上部流出流分Q3
以外の泥分は、サイクロン1の下部流出流分Q4
としてアンダートラフ5へ圧送されるため、アン
ダートラフ5の面積、容量によつてはトラフの中
が撹乱状態となり、必ずしも希望する沈降分離が
行われず、満足する結果が得られない。
上記と同様の試験結果では、アンダートラフ5
における砂分回収率は54.6%と低いため、折角液
体サイクロン1において砂分回収率79.4%と比較
的満足できるものであつても系全体、すなわち回
収砂Sとして回収される砂量は、流入流分Q2に
よつて液体サイクロン1に流入する砂分に対して
79.4%×54.6%=43.4%と半分以下の砂回収量で
あり、甚だ低くまた回収砂も良質なものとは云い
難い。さらにアンダートラフ5の上部流出流分
Q7がサイクロン1の下部流出流分Q4とほぼ等し
い量となり、これが前段のプロセスに戻るため、
処理容量が繰り返しのため増大し、エネルギー的
にもまた装置の大型化する場合にも問題を生ず
る。
叙上の如く液体サイクロンを用いる従来の固形
物等の分離回収方法においては、液体サイクロン
の固形物回収率は高いものの、分離回収された固
形物の分離排出方法あるいは装置において固形物
の回収率が著しく低下するため、系全体としての
固形物回収率が50%以下と低い。そのため繰返し
処理量が液体サイクロン流入流分に対して10〜20
%程度に増加し大規模の汚泥処理においてはエネ
ルギー的にも問題があり、装置を大型化する上で
も複雑となつて好ましくない。更に良質な回収固
形物が得られない等の問題が内在しており、これ
らの問題点を解決するための固形物の分離回収方
法が望まれていた。
本発明は、上記のような従来方法の問題点を解
決するためになされたものであり、液体サイクロ
ンを用い、良質な固形物を高い回収率で回収しか
つ大容量処理に好適な固形物等の分離回収方法を
提供するものである。
本発明は、液体サイクロンの下部流出口と分離
物貯留槽と分離排出手段とを気密に連結して設け
てなる装置を用い、固形物を分離回収する方法に
おいて、
前記分離排出手段の排出口を前記分離物貯留槽
より高い位置に設け、前記液体サイクロンの入口
流入圧力と入口速度とを調節することにより、前
記分離物貯留槽内の圧力を負圧とし、該負圧エネ
ルギーにより前記分離排出手段の水位面より空気
を前記分離物貯留槽内に吸入せしめ、該分離物貯
留槽内の固形物を洗浄し前記排出手段により固形
分離物を排出せしめることを特徴とする固形物等
の分離回収方法である。
以下本発明を本発明の実施態様例である説明図
に基づき述べる。
第2図は本発明方法の原理的説明図である。
なお、第1図と同じ機能の部分は同じ符号で表
示し説明を省略する。本発明の構成上の特徴は、
第1図の従来装置で示したアンダートラフ5の容
積および形状を変えて液体サイクロン1と気密に
直結させ、液体サイクロン1によつて分離、分級
された砂分のみを沈降堆積させる分離物貯留槽9
(以下貯留槽9という)を気密に設けたことであ
る。
一般的な液体サイクロンで運転を行う場合、液
体サイクロンの入口管からの流入流分の圧力は1
〜2(Kg/cm2)程度が普通である。いま、第2図
に示す本発明の分離装置を運転した場合、流体は
液体サイクロン1の上部出口管3からのみ流出す
ることから、貯留槽9内に連通して設けた圧力計
11のゲージ圧力も、液体サイクロン1の入口管
2に設けた圧力計10のゲージ圧力とほぼ同様の
値を示すことが懸念される。しかしながら、本発
明者らは液体サイクロン1の内部の流体の流れ状
態に着目して研究の結果、通常の状態でもこの流
れが超乱流の渦を形成し、渦流れ場の中心が真空
状態となることから、液体サイクロン1の形状に
よつて定まる入口流入圧力と入口速度とを或る条
件に調節することにより、貯留槽9内の圧力を負
圧域にすることが可能であることを見知した。
この場合流体は、液体サイクロン1と貯留槽9
の壁面付近を渦運動を行いながら下降して下端に
達し、その後中心付近を上昇し、液体サイクロン
1の上部流出口3から系外へ排出される。
以上の前提にたち、発明者等は、第2図に示す
本発明に基く装置で、水による試験を行い、液体
サイクロン1の入口管2の流入圧力が通常使用す
る範囲の圧力の場合において、貯留槽9内の圧力
を負圧域にする特殊な構成および運転条件を見い
出した。すなわち、試験の結果によれば、液体サ
イクロン1の円筒部の径D1を380mm(15吋)入口
管2の径D2を107mm、上部出口管3の径D3を115
mm、下部出口管4の径D4を60mmとしたとき、液
体サイクロン1の入口速度が5.6m/secで流入圧
力が2.01Kg/cm2の場合貯留槽9内のゲージ圧力が
−0.90Kg/cm2という真空に近い値が得られ、なお
かつ、この貯留槽9内の圧力は、ある程度の範囲
内に設定し、調節することが可能であることがわ
かつた。
以上の結果をもとに、発明者等は本発明方法の
実用化試験を行うべく、第2図に示した原理的構
成を発展させ、連続運転を可能とするために、前
記液体サイクロンを用い、分離物貯留槽容積135
、回収砂排出口の高さH=2mの第3図に示す
ような実施例装置を完成し、試験を行つた。な
お、第3図において符号1〜8で示す部位は、第
1図および第2図に示したものと同様であり、砂
分搬出用クローズドポツト型スクリユーコンベア
6内の水位面12と回収砂排出口8までの高さH
が新たに書き加えられている。第2図の装置にお
ける試験結果を第3図の装置に適用すれば、貯留
槽9内の負圧の大小により、砂分搬出用コンベア
6内の水位面12をある範囲の適当な位置に設定
することが可能である。また貯留槽9内の負圧々
力にバランスする水位面12より高い位置に排出
口8を設けているので、砂分搬出用コンベア6の
上部排出口8からは、水の噴出を起させることな
く、脱水された砂分のみを回収することができ
る。
この方法は、第1図で述べた従来装置と比較し
て、系全体の砂分回収率は飛躍的に向上し、か
つ、砂分を分離した泥分のほとんどは、液体サイ
クロン1の流出流分Q3として上部出口管3から
次工程へ送出されることになり、第1図に示した
従来方法による装置におけるアンダートラフ上部
流出流分Q7を零にできることから画期的なもの
である。
更に本発明は、貯留槽9の負圧を高める条件で
装置を運転した場合、この負圧を利用し、砂分排
出用コンベア6の排出口8の高さHを分離物貯留
槽9より高い位置に設け水封することにより、砂
分排出用コンベア6内の空気を砂分排出用コンベ
ア6内の水位面12から吸入せしめ、分離物貯留
槽9の下部に導入することができる。この空気混
入により液体サイクロン1で分離、分級され、貯
留槽9に貯留されている砂分がパブリングされ、
砂粒子が衝突し合つて砂粒子に付着している有機
物を洗浄する。この結果、回収砂Sの有機物濃度
が低下し、含水率の低下、悪臭の低減等が行わ
れ、回収砂Sの後処理が容易になり、従来から行
われている二次処理水等による洗砂プロセスが省
力化あるいは簡略化されるため、洗砂工程を含ん
だ総合的な洗砂システムを実現できる。
後述の実施例1の結果によれば、貯留槽内圧力
−0.04Kg/cm2、空気吸入量1.10Nm3/minのとき
に、砂分回収率は87.3%、有機物の除去率は73.3
%の好成積を得ている。
本発明に係る方法の応用分野は、上述の汚泥除
砂用以外に、下水処理場あるいはポンプ所におけ
る下水、雨水沈砂池の代用、建設・土木等の各種
スラリー輸送分野における後段のスラリー除去用
としても使用することができる。
次に実施例について述べる。
実施例 1
東京都内某処理場の汚泥(有機物濃度24.5%、
砂分4.5g/)を第3図に示す実施例装置を用
いて処理試験を行ない第1表に示す試験成積を得
た。なおこの場合の装置仕様は次の通りである。
液体サイクロン 円筒部径(D1)380mm(15吋)
入口管径(D2)107mm
上部出口管径(D3)115mm
下部出口管径(D4)60mm
分離物貯留槽 容量135
実施例 2
下水処理場の下水に混入している砂分を下水二
次処理水で混合し、流入下水と同等の砂分濃度に
調整したもの(有機物濃度50%砂分3.8g/固
形物総量0.2%)を流入原水として、実施例1と
同じ装置で試験を行つた。その結果を第1表に示
す。第1表に示す如く砂分回収率、有機物濃度の
除去率も高く回収砂の含水率は低く良質の回収砂
が得られ下水処理場沈砂池の砂として再利用可能
なものであつた。
The present invention relates to a method for separating and recovering solids, etc., which efficiently separates solids mixed in a liquid by centrifugal force and recovers only the solids, which is more systematic than conventional methods. The purpose of this project is to simplify the single tank and dramatically improve the recovery efficiency and properties of the recovered solids. More specifically, when treating sewage containing organic matter, sand, etc., the present invention uses a liquid cyclone to separate solids, and stores the solids in a separation storage tank that is directly connected to the liquid cyclone at the bottom of the cyclone. Solids are stored, bubbling air sucked from the atmosphere by the negative pressure in the separation storage tank is introduced into the separation storage tank, the separated solids are washed, the washed and separated solids are dehydrated, and the system The purpose of this system is to improve the efficiency of collecting solids, to wash solids, and to continuously separate and collect solids by reducing the underflow flow rate of the liquid cyclone to zero. The method is simple and provides a continuous method for separating, washing and recovering solids in a wide range of liquids. A conventional method for removing sand from sludge and the like will be explained with reference to FIG. FIG. 1 is an explanatory diagram of the system of the sludge removal device. In the figure, 1 is a hydrocyclone, which has the function of separating sludge and sand by centrifugal force. 2 is an inlet pipe for sludge containing sand from which large impurities such as wood chips and metals have been removed, that is, raw sludge from which the sand content is to be removed. The inflow Q 2 from the inlet pipe 2 is separated and classified into sand and mud by centrifugal acceleration inside the hydrocyclone 1 , and the mud with lower specific gravity flows out from the upper outlet pipe 3 of the hydrocyclone 1 . flow Q 3
and is discharged to the next process outside the system. On the other hand, the sand with high specific gravity becomes an inflow flow Q4 from the lower outlet pipe 4 of the hydrocyclone 1 and flows into the undertrough 5.
It will be collected at This undertrough 5 has the function of re-sedimenting and separating the mud and sand contained in the lower outflow stream Q 4 , but the mud is transferred from the upper outlet pipe 7 of the undertrough 5 to the outflow stream Q 7 . Then, it is returned to the place where the mud quality is almost the same as the previous process, that is, the inflow stream Q2 . On the other hand, the sand that has settled in the undertrough 5 is transferred by the sand transport conveyor 6, and although there are differences depending on the operating specifications of the conveyor 6, a certain degree of dewatering function is activated due to the potential energy of the slope. The sand is collected as recovered sand S from a discharge port 8 provided at the top of the conveyor 6. The above is an example of a conventional method for separating and recovering sand from sludge containing sand as a solid substance, but the problems in this case will be described below. A typical treatment result of a test using the method described above using sludge drawn from a settling tank at a certain treatment plant in Tokyo shows that when using a hydrocyclone 1 with a cylindrical diameter D 1 of 152 mm (6 inches), The 50% separation limit particle diameter d50 was approximately 140 (μm), and the sand recovery rate of the hydrocyclone 1 was 79.4%, which was relatively satisfactory. However, this 79.4% sand content and upper runoff flow Q3
The mud other than the bottom flow of cyclone 1 is Q 4
Therefore, depending on the area and capacity of the undertrough 5, the inside of the trough may be disturbed, and the desired sedimentation separation may not necessarily take place, making it impossible to obtain a satisfactory result. Test results similar to those above show that undertrough 5
Since the sand recovery rate in hydrocyclone 1 is as low as 54.6%, even if the sand recovery rate in hydrocyclone 1 is relatively satisfactory at 79.4%, the entire system, that is, the amount of sand recovered as recovered sand S, is For the sand content flowing into hydrocyclone 1 by minute Q 2
The amount of sand recovered is less than half of 79.4% x 54.6% = 43.4%, which is extremely low and it is difficult to say that the recovered sand is of good quality. Furthermore, the upper outflow of undertrough 5
Q7 is approximately equal to the bottom outflow of cyclone 1 Q4 , which returns to the previous process, so
The processing capacity increases due to repetition, which causes problems in terms of energy and when the equipment becomes larger. As mentioned above, in the conventional method of separating and recovering solids using a liquid cyclone, although the liquid cyclone has a high solids recovery rate, the recovery rate of solids is low in the separation and discharge method or device for the separated and recovered solids. As a result, the solids recovery rate for the entire system is low at less than 50%. Therefore, the repeated processing amount is 10 to 20 times per hydrocyclone inlet flow.
%, and in large-scale sludge treatment, there is an energy problem, and it is undesirable to increase the size of the equipment because it becomes complicated. Furthermore, there are inherent problems such as the inability to obtain recovered solids of good quality, and a method for separating and recovering solids has been desired to solve these problems. The present invention was made in order to solve the problems of the conventional method as described above, and uses a liquid cyclone to recover high quality solids at a high recovery rate and solids etc. suitable for large-scale processing. This provides a separation and recovery method for The present invention provides a method for separating and recovering solids using a device in which a lower outlet of a hydrocyclone, a separated material storage tank, and a separating and discharging means are connected in an airtight manner. By adjusting the inlet inflow pressure and inlet velocity of the liquid cyclone, the liquid cyclone is provided at a higher position than the separated product storage tank, so that the pressure in the separated product storage tank is made negative, and the negative pressure energy is used to separate and discharge the liquid cyclone. A method for separating and recovering solids, etc., characterized in that air is sucked into the separated product storage tank from the water level of the tank, the solids in the separated product storage tank are washed, and the solid separated products are discharged by the discharge means. It is. The present invention will be described below based on explanatory drawings that are examples of embodiments of the present invention. FIG. 2 is an explanatory diagram of the principle of the method of the present invention. Note that parts having the same functions as those in FIG. 1 are indicated by the same reference numerals, and explanations thereof will be omitted. The structural features of the present invention are:
The volume and shape of the undertrough 5 shown in the conventional device shown in FIG. 1 are changed and the undertrough 5 is directly connected to the hydrocyclone 1 in an airtight manner, so that only the sand separated and classified by the hydrocyclone 1 is deposited in a separated storage tank. 9
(hereinafter referred to as storage tank 9) is provided in an airtight manner. When operating a general hydrocyclone, the pressure of the inflow from the inlet pipe of the hydrocyclone is 1
~2 (Kg/cm 2 ) is normal. Now, when the separator of the present invention shown in FIG. 2 is operated, the fluid flows out only from the upper outlet pipe 3 of the hydrocyclone 1. There is also a concern that the gauge pressure of the pressure gauge 10 provided in the inlet pipe 2 of the hydrocyclone 1 may be approximately the same as the gauge pressure. However, as a result of research focusing on the flow state of the fluid inside the hydrocyclone 1, the present inventors found that even under normal conditions, this flow forms a super turbulent vortex, and the center of the vortex flow field is in a vacuum state. Therefore, it was found that by adjusting the inlet inflow pressure and inlet velocity determined by the shape of the hydrocyclone 1 to certain conditions, it is possible to bring the pressure inside the storage tank 9 into the negative pressure range. I learned. In this case, the fluid flows between the hydrocyclone 1 and the storage tank 9.
It descends while performing a vortex motion near the wall surface of the liquid cyclone 1, reaches the lower end, then rises near the center, and is discharged from the upper outlet 3 of the hydrocyclone 1 to the outside of the system. Based on the above premise, the inventors conducted a water test using the apparatus according to the present invention shown in FIG. We have found a special configuration and operating conditions that bring the pressure inside the storage tank 9 into a negative pressure range. That is, according to the test results, the diameter D 1 of the cylindrical part of the hydrocyclone 1 is 380 mm (15 inches), the diameter D 2 of the inlet pipe 2 is 107 mm, and the diameter D 3 of the upper outlet pipe 3 is 115 mm.
mm, and when the diameter D 4 of the lower outlet pipe 4 is 60 mm, when the inlet speed of the hydrocyclone 1 is 5.6 m/sec and the inflow pressure is 2.01 Kg/cm 2 , the gauge pressure in the storage tank 9 is -0.90 Kg/cm 2 It was found that a value close to a vacuum of cm 2 was obtained, and that the pressure inside this storage tank 9 could be set and adjusted within a certain range. Based on the above results, the inventors developed the principle configuration shown in Figure 2 in order to conduct a practical test of the method of the present invention, and used the above-mentioned hydrocyclone to enable continuous operation. , Separate storage tank volume 135
An example device as shown in FIG. 3 in which the height H of the recovered sand outlet is 2 m was completed and tested. Note that the parts indicated by numerals 1 to 8 in Fig. 3 are the same as those shown in Figs. 1 and 2, and are the same as those shown in Figs. Height H to discharge port 8
has been newly added. If the test results for the device shown in FIG. 2 are applied to the device shown in FIG. 3, the water level 12 in the sand conveyor 6 can be set at an appropriate position within a certain range depending on the magnitude of the negative pressure in the storage tank 9. It is possible to do so. In addition, since the outlet 8 is provided at a position higher than the water level 12 that balances the negative pressure force in the storage tank 9, no water can be ejected from the upper outlet 8 of the sand conveyor 6. Instead, only the dehydrated sand can be recovered. Compared to the conventional device described in Figure 1, this method dramatically improves the sand recovery rate of the entire system, and most of the mud separated from the sand is transferred to the outflow of the hydrocyclone 1. This is revolutionary because it is able to reduce the undertrough upper part flow Q 7 to zero in the conventional method shown in Fig. . Furthermore, in the present invention, when the device is operated under conditions that increase the negative pressure in the storage tank 9, this negative pressure is utilized to increase the height H of the discharge port 8 of the sand discharge conveyor 6 to be higher than the separated product storage tank 9. By providing a water seal at the position, the air in the sand discharge conveyor 6 can be sucked in from the water level surface 12 in the sand discharge conveyor 6 and introduced into the lower part of the separated material storage tank 9. Due to this air mixture, the sand separated and classified by the liquid cyclone 1 and stored in the storage tank 9 is bubbled,
When the sand particles collide with each other, the organic matter adhering to the sand particles is washed away. As a result, the concentration of organic matter in the recovered sand S is reduced, the water content is lowered, and the odor is reduced, making post-treatment of the recovered sand S easier, and washing with secondary treated water, etc. Since the sand process is labor-saving or simplified, a comprehensive sand washing system including a sand washing process can be realized. According to the results of Example 1 described later, when the pressure inside the storage tank is -0.04 Kg/cm 2 and the air intake amount is 1.10 Nm 3 /min, the sand recovery rate is 87.3% and the organic matter removal rate is 73.3.
% of good sales. In addition to the above-mentioned sludge removal, the method of the present invention can be used as a substitute for sewage and rainwater settling basins in sewage treatment plants or pump stations, and for subsequent slurry removal in various slurry transportation fields such as construction and civil engineering. can also be used. Next, an example will be described. Example 1 Sludge from a certain treatment plant in Tokyo (organic matter concentration 24.5%,
A processing test was carried out using the apparatus shown in FIG. 3 to obtain the test deposits shown in Table 1. Note that the device specifications in this case are as follows. Hydrocyclone Cylindrical diameter (D 1 ) 380 mm (15 inches) Inlet pipe diameter (D 2 ) 107 mm Upper outlet pipe diameter (D 3 ) 115 mm Lower outlet pipe diameter (D 4 ) 60 mm Separate storage tank Capacity 135 Example 2 Sewage The sand mixed in the sewage from the treatment plant is mixed with secondary treated sewage water and adjusted to the same sand concentration as the inflowing sewage (organic matter concentration 50%, sand 3.8g/total solids 0.2%). The test was conducted using the same equipment as in Example 1 as the influent raw water. The results are shown in Table 1. As shown in Table 1, the sand recovery rate and the removal rate of organic matter concentration were high, and the moisture content of the recovered sand was low, and the recovered sand was of good quality and could be reused as sand for settling basins at sewage treatment plants.
【表】【table】
【表】
以上詳述したように、本発明方法は従来の液体
サイクロン利用による固形物の分離回収方法の問
題点をすべて解決したもので、システム的にも単
純であるために大量の処理を可能にするものであ
る。
また本発明によれば下水処理等における回収砂
の有機物を効果的に除去できるので、悪臭の低減
と相俟つてその回収砂の利用範囲を大幅に拡大で
きる等、実施上の効果が甚だ大である。[Table] As detailed above, the method of the present invention solves all the problems of the conventional separation and recovery method of solids using a liquid cyclone, and because the system is simple, it is possible to process a large amount. It is meant to be. In addition, according to the present invention, since organic matter can be effectively removed from recovered sand in sewage treatment, etc., it has great practical effects, such as reducing offensive odors and greatly expanding the scope of use of recovered sand. be.
第1図は従来の汚泥除砂装置の系統説明図、第
2図は本発明の原理的説明図、第3図は本発明実
施例の系統説明図である。
1……液体サイクロン、2……入口管、3……
上部出口管、4……下部出口管、6……砂分搬出
用コンベア、8……排出口、9……分離物貯留
槽、12……水位面。
FIG. 1 is a system explanatory diagram of a conventional sludge and sand removal apparatus, FIG. 2 is an explanatory diagram of the principle of the present invention, and FIG. 3 is a system explanatory diagram of an embodiment of the present invention. 1...Liquid cyclone, 2...Inlet pipe, 3...
Upper outlet pipe, 4...Lower outlet pipe, 6...Sand conveyor, 8...Discharge port, 9...Separated material storage tank, 12...Water level.
Claims (1)
と分離排出手段とを気密に連結して設けてなる装
置を用い、固形物を分離回収する方法において、 前記分離排出手段の排出口を前記分離物貯留槽
より高い位置に設け、前記液体サイクロンの入口
流入圧力と入口速度とを調節することにより、前
記分離物貯留槽内の圧力を負圧とし、該負圧エネ
ルギーにより前記分離排出手段の水位面より空気
を前記分離物貯留槽内に吸入せしめ、該分離物貯
留槽内の固形物を洗浄し前記排出手段により固形
分離物を排出せしめることを特徴とする固形物等
の分離回収方法。[Scope of Claims] 1. A method for separating and recovering solids using a device in which a lower outlet of a hydrocyclone, a separated material storage tank, and a separating and discharging means are connected in an airtight manner, comprising: By providing an outlet at a higher position than the separated product storage tank and adjusting the inlet inflow pressure and inlet velocity of the hydrocyclone, the pressure in the separated product storage tank is made negative, and the negative pressure energy causes the A method for discharging solid substances, etc., characterized in that air is sucked into the separated substance storage tank from the water level of the separation and discharge means, the solid substances in the separated substance storage tank are washed, and the solid separated substances are discharged by the discharge means. Separation and recovery method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP24558183A JPS6034757A (en) | 1983-12-28 | 1983-12-28 | Solid matter separation and recovery method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP24558183A JPS6034757A (en) | 1983-12-28 | 1983-12-28 | Solid matter separation and recovery method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6034757A JPS6034757A (en) | 1985-02-22 |
| JPS6336300B2 true JPS6336300B2 (en) | 1988-07-19 |
Family
ID=17135851
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP24558183A Granted JPS6034757A (en) | 1983-12-28 | 1983-12-28 | Solid matter separation and recovery method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6034757A (en) |
Families Citing this family (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP5916073B2 (en) * | 2011-06-28 | 2016-05-11 | 株式会社industria | Fine object removal apparatus and fine object removal system |
| JP7244349B2 (en) * | 2019-05-15 | 2023-03-22 | メタウォーター株式会社 | Screw separator and wastewater treatment system |
| JP7417987B2 (en) * | 2019-11-27 | 2024-01-19 | アクアインテック株式会社 | Driving method of solid-liquid separator |
| JP2021154229A (en) * | 2020-03-27 | 2021-10-07 | アクアインテック株式会社 | Driving method for solid-liquid separator, and solid-liquid separator |
| JP7555558B2 (en) * | 2020-03-27 | 2024-09-25 | アクアインテック株式会社 | Method for driving cleaning device and cleaning device |
| JP7588817B2 (en) * | 2020-10-19 | 2024-11-25 | アクアインテック株式会社 | Cleaning Equipment |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5721047U (en) * | 1980-07-07 | 1982-02-03 |
-
1983
- 1983-12-28 JP JP24558183A patent/JPS6034757A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6034757A (en) | 1985-02-22 |
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