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JP2023108648A - Sludge treatment method using heated flocculant - Google Patents

Sludge treatment method using heated flocculant Download PDF

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JP2023108648A
JP2023108648A JP2022009796A JP2022009796A JP2023108648A JP 2023108648 A JP2023108648 A JP 2023108648A JP 2022009796 A JP2022009796 A JP 2022009796A JP 2022009796 A JP2022009796 A JP 2022009796A JP 2023108648 A JP2023108648 A JP 2023108648A
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sludge
flocculant
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heated
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康昭 西原
Yasuaki Nishihara
純 多田
Jun Tada
隆広 坂東
Takahiro Bando
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Ishigaki Co Ltd
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Abstract

To provide a sludge treatment method using a heated flocculant to perform secondary flocculation by adding a heated flocculant to a concentrated sludge formed by primary flocculation and primary dehydration, and then perform secondary dehydration.SOLUTION: There is provided a sludge treatment method wherein after mixing a sludge and a first flocculant in a primary flocculating section 5 to form a primary flocculated floc, it is concentrated in a primary dehydrator 12, and after mixing the formed concentrated sludge with a second flocculant to form a secondary flocculated floc, it is dehydrated in a secondary dehydrator 14, in which by adding the heated second flocculant to the concentrated sludge, it is possible to efficiently disperse the second flocculant in the concentrated sludge, and since kneadability of the concentrated sludge and the second flocculant is enhanced, coarse and firm flocs can be formed.SELECTED DRAWING: Figure 1

Description

本発明は、下水、し尿、集落排水、工場等の排水処理施設から発生する汚泥を1次凝集した後、濃縮し、さらに2次凝集した後、脱水する汚泥処理方法に関し、特に、2次凝集時に加温した凝集剤を用いることを特徴とする加温凝集剤を用いた汚泥処理方法に関する。 The present invention relates to a sludge treatment method in which sludge generated from wastewater treatment facilities such as sewage, night soil, community wastewater, and factories is firstly flocculated, concentrated, further secondarily flocculated, and then dewatered. The present invention relates to a sludge treatment method using a heated flocculant, characterized in that the flocculant is sometimes heated.

従来、下水、し尿、集落排水、工場等の排水処理施設から発生する汚泥に高分子凝集剤、無機凝集剤を単独で、または組み合わせて供給し1次凝集した後、濃縮し、濃縮汚泥を2次凝集した後、脱水する汚泥処理方法は知られている。特許文献1には、凝集装置内の原液に高分子凝集剤を添加して1次凝集した後、濃縮装置で濃縮し、シュート内に供給された濃縮汚泥に無機凝集剤を添加して2次凝集した後、脱水装置で脱水する技術が開示されている。 Conventionally, a polymer flocculant or an inorganic flocculant is supplied alone or in combination to sludge generated from wastewater treatment facilities such as sewage, night soil, community wastewater, factories, etc., and after primary flocculation, it is concentrated, and concentrated sludge is produced twice. Sludge treatment methods are known in which sludge is dewatered after subsequent flocculation. In Patent Document 1, after primary flocculation by adding a polymer flocculant to the stock solution in the flocculating device, it is concentrated in a thickening device, and an inorganic flocculant is added to the concentrated sludge supplied into the chute for secondary flocculation. A technique for dewatering with a dehydrator after flocculation is disclosed.

特許文献2には、加温された上水で凝集剤を溶解し、生成された凝集剤溶液を脱水機に注入する技術が開示されている。 Patent Literature 2 discloses a technique of dissolving a coagulant in heated tap water and injecting the resulting coagulant solution into a dehydrator.

特許文献3には、凝集混和槽に接続された薬品供給管内で加温された高分子凝集剤を槽内の汚泥に添加する技術が開示されている。 Patent Document 3 discloses a technique of adding a polymer flocculant heated in a chemical feed pipe connected to a flocculation and mixing tank to sludge in the tank.

特許第5477373号公報Japanese Patent No. 5477373 特許第4177752号公報Japanese Patent No. 4177752 特開2019-10612号公報JP 2019-10612 A

従来、1次凝集及び2次凝集で使用する凝集剤に関し、一般的には常温の凝集剤を用いている。しかし、常温の凝集剤は粘度が高く流動性が低いため、汚泥中に分散し難く、凝集剤と汚泥を十分に混合できていなかった。また、特許文献1では、脱水工程を行う際、脱水装置に圧入される濃縮汚泥に圧力を付与しながら脱水するため、脱水工程前段で2次凝集を行い、強固なフロックを形成しておく必要があった。
Conventionally, regarding the flocculants used in primary aggregation and secondary aggregation, normal temperature flocculants are generally used. However, since the flocculant at room temperature has high viscosity and low fluidity, it is difficult to disperse in the sludge, and the flocculant and sludge cannot be sufficiently mixed. In addition, in Patent Document 1, when performing the dehydration process, the thickened sludge that is injected into the dehydrator is dehydrated while applying pressure, so it is necessary to perform secondary aggregation before the dehydration process to form strong flocs. was there.

特許文献2、特許文献3の技術は、加温した凝集剤を使用して汚泥を凝集するため、流動性の高い凝集剤が汚泥全体に作用する。しかし、特許文献2は、凝集溶解液と濃縮汚泥を別々に脱水機に供給する技術であり、凝集溶解液と濃縮汚泥を混合した後、脱水するものではない。凝集溶解液と濃縮汚泥の混合が脱水装置のみで行われるため、汚泥との混練性を高めることができない。また、加温の目的が上水の加温により凝集剤を効率よく溶解させることであり、汚泥との分散性を高めることが目的ではない。特許文献3は、1次凝集工程で使用する高分子凝集剤を加温するものであり、濃縮汚泥の2次凝集工程に関する記載や示唆はない。 In the techniques of Patent Documents 2 and 3, a heated flocculant is used to flocculate sludge, so the highly fluid flocculant acts on the entire sludge. However, Patent Document 2 is a technique for separately supplying a flocculated solution and thickened sludge to a dehydrator, and does not dehydrate after mixing the flocculated solution and thickened sludge. Since the flocculated solution and thickened sludge are mixed only in the dehydrator, kneadability with sludge cannot be improved. Moreover, the purpose of heating is to efficiently dissolve the flocculant by heating the tap water, and the purpose is not to improve dispersibility with sludge. Patent document 3 heats the polymer flocculant used in the primary flocculation step, and does not describe or suggest a secondary flocculation step for thickened sludge.

本発明は、一次凝集工程、濃縮工程を経て形成された濃縮汚泥に加温した凝集剤を添加した後、混合して2次凝集することで、強固な2次凝集フロックを形成できる加温凝集剤を用いた汚泥処理方法を提供する。 The present invention adds a heated flocculant to the thickened sludge formed through the primary flocculation process and the thickening process, and then mixes and secondary flocculates to form strong secondary flocculated flocs. Provided is a sludge treatment method using an agent.

1次凝集部で汚泥と第1凝集剤を混合し1次凝集フロックを形成した後、1次脱水部で濃縮し、形成された濃縮汚泥を第2凝集剤とともに混合して2次凝集フロックを形成した後、2次脱水部で脱水する汚泥処理方法において、濃縮汚泥に加温した第2凝集剤を添加することで、加温により粘度が低く流動性の高い第2凝集剤が濃縮汚泥全体に広く作用するため汚泥との混練性を高めることができ、SS分を多く含んだ強固な凝集フロックが形成可能となる。 After the sludge and the first flocculant are mixed in the primary flocculating section to form primary flocculated flocs, they are thickened in the primary dewatering section, and the formed thickened sludge is mixed with the second flocculant to form secondary flocculated flocs. In the sludge treatment method in which the second coagulant is added to the thickened sludge after it is formed and dewatered in the secondary dewatering section, the second coagulant having a low viscosity and high fluidity due to the heating is applied to the entire thickened sludge. Since it widely acts on , it is possible to improve the kneadability with sludge, and it is possible to form a strong flocculated floc containing a large amount of SS.

前記第2凝集剤を前記1次脱水部、2次凝集部及び2次脱水部のうち少なくとも1箇所に接続された第2薬品供給管の周面に設けた加温装置で加温することで、汚泥への分散性を高めることができるため第2凝集剤使用量の削減が可能となり、これに伴い第1凝集剤使用量も削減できる。 By heating the second coagulant with a heating device provided on the peripheral surface of a second chemical supply pipe connected to at least one of the primary dewatering section, the secondary coagulation section, and the secondary dehydration section. Since the dispersibility in sludge can be improved, the amount of the second flocculant used can be reduced, and the amount of the first flocculant used can be reduced accordingly.

本発明に係る加温凝集剤を用いた汚泥処理方法は、1次脱水部より排出された濃縮汚泥に加温した無機凝集剤からなる第2凝集剤を添加した後、混合することで、強固な凝集フロックを形成できる。脱水前段で強固な凝集フロックを形成しておくことで、フロックが脱水部のろ過面から目抜けすることなく、効率よく低含水率の脱水ケーキを生成できる。また、第2凝集剤を加温する加温装置は、薬品供給管に被覆させたシンプルな構成であるため既存設備に容易に適用可能なうえ、加温容量が少ないため省エネルギーで高効率な汚泥処理を実現できる。さらに加温装置にて直接加温される薬品供給管及び加温された第2凝集剤が供給されて間接的に加温される汚泥供給管が閉塞しない。 In the sludge treatment method using a heated coagulant according to the present invention, a second coagulant made of a heated inorganic coagulant is added to the thickened sludge discharged from the primary dehydration unit, and then mixed. agglomerated flocs can be formed. By forming strong aggregated flocs in the preceding stage of dehydration, it is possible to efficiently produce a dehydrated cake with a low moisture content without causing the flocs to slip through the filtration surface of the dehydration section. In addition, the heating device that heats the second flocculant has a simple structure that covers the chemical supply pipe, so it can be easily applied to existing equipment, and since the heating capacity is small, energy-saving and highly efficient sludge. processing can be realized. Further, the chemical supply pipe directly heated by the heating device and the sludge supply pipe indirectly heated by being supplied with the heated second coagulant are not clogged.

本発明の実施形態に係る汚泥処理方法の概略構成図である。BRIEF DESCRIPTION OF THE DRAWINGS It is a schematic block diagram of the sludge-treatment method which concerns on embodiment of this invention. 同じく、固液分離部の縦断側面図である。Similarly, it is a longitudinal side view of a solid-liquid separation part. 同じく、図2に示す1次脱水部の拡大図である。Similarly, it is an enlarged view of the primary dewatering part shown in FIG. 同じく、図2に示す2次凝集部の縦断面図である。Similarly, it is a longitudinal cross-sectional view of the secondary aggregation part shown in FIG. 同じく、他の実施形態に係る汚泥処理方法の概略構成図である。Similarly, it is a schematic configuration diagram of a sludge treatment method according to another embodiment. 同じく、他の実施形態に係る汚泥処理方法の概略構成図である。Similarly, it is a schematic configuration diagram of a sludge treatment method according to another embodiment.

図1は本発明の実施形態に係る汚泥処理方法の概略構成図である。
汚泥貯留槽2内の汚泥は、汚泥供給管3から汚泥供給ポンプ4を経て1次凝集部5に供給される。汚泥供給管3には、高分子凝集剤、無機凝集剤を単独で、あるいは、組み合わせた凝集剤を移送する第1薬品供給管7を接続しており、第1薬品槽6内の第1凝集剤を1次凝集部5に移送できる構成となっている。1次凝集部5は、凝集混和槽であり、移送された汚泥及び第1凝集剤を槽内の撹拌機にて混合撹拌し、1次凝集フロックを形成する。形成された1次凝集フロックは、1次凝集部5の後段に設置した固液分離部1に移送された後、固液分離される。固液分離部1は、1次脱水部12、2次凝集部13、2次脱水部14で構成してある。
FIG. 1 is a schematic configuration diagram of a sludge treatment method according to an embodiment of the present invention.
Sludge in the sludge storage tank 2 is supplied from the sludge supply pipe 3 to the primary coagulation section 5 via the sludge supply pump 4 . The sludge supply pipe 3 is connected to a first chemical supply pipe 7 for transferring a polymer flocculant or an inorganic flocculant alone or a combination of flocculants. It is configured such that the agent can be transferred to the primary aggregation section 5 . The primary flocculation section 5 is a flocculation and mixing tank, in which the transferred sludge and first flocculating agent are mixed and agitated by a stirrer in the tank to form primary flocculation flocs. The formed primary aggregated flocs are transferred to the solid-liquid separation unit 1 installed after the primary aggregation unit 5, and then solid-liquid separated. The solid-liquid separation section 1 is composed of a primary dewatering section 12 , a secondary aggregation section 13 and a secondary dehydration section 14 .

1次脱水部12では、例えば、回転濃縮機、ベルト濃縮機、遠心脱水機等の公知の機械を用いて濃縮が行われる。1次凝集部5から供給された1次凝集フロックを濃縮しながら濃縮ろ液を分離し、濃縮汚泥を形成する。形成された濃縮汚泥は、1次脱水部12の後段に設置した2次凝集部13に移送される。 In the primary dehydrator 12, concentration is performed using known machines such as a rotary concentrator, a belt concentrator, and a centrifugal dehydrator. A concentrated filtrate is separated while concentrating the primary flocculation flocs supplied from the primary flocculation unit 5 to form concentrated sludge. The formed thickened sludge is transferred to the secondary flocculation section 13 installed after the primary dehydration section 12 .

2次凝集部13では、1次脱水部12で形成された濃縮汚泥の凝集が行われる。凝集は、1次凝集部5でも行われるが、1次凝集部5で形成された1次凝集フロックは微小であり、濃縮後に2次脱水部14で脱水される際にろ材から目抜けする場合がある。そのため、2次凝集部13にて再度凝集し粗大なフロックを形成しておく。 In the secondary aggregation section 13, the thickened sludge formed in the primary dewatering section 12 is aggregated. Aggregation is also performed in the primary aggregation section 5, but the primary aggregation flocs formed in the primary aggregation section 5 are minute, and when dewatered in the secondary dehydration section 14 after concentration, the flocs may be removed from the filter medium. There is Therefore, they are aggregated again in the secondary aggregation section 13 to form coarse flocs.

2次凝集部13では、第2薬品槽9に貯留された第2凝集剤(無機凝集剤)を用いる。無機凝集剤は、濃縮汚泥に添加する前段で加温装置15にて加温しておく。無機凝集剤は、加温されることで粘度が低下し流動性が高くなる。そのため、加温した無機凝集剤を濃縮汚泥に添加することで汚泥中全体に作用させることができる。これにより、濃縮汚泥との混練性が高まり、緻密で強固な2次凝集フロックが形成される。形成された2次凝集フロックは、2次脱水部14に移送される。2次凝集部13は、後段で詳述する図2、図5、図6に示すように、使用する機械によって形態が相違する。 The secondary coagulant 13 uses the second coagulant (inorganic coagulant) stored in the second chemical tank 9 . The inorganic flocculant is heated by the heating device 15 before being added to the concentrated sludge. The inorganic flocculant becomes less viscous and more fluid when heated. Therefore, by adding a heated inorganic flocculant to thickened sludge, it can be made to act on the entire sludge. As a result, kneadability with thickened sludge is enhanced, and dense and strong secondary flocculation flocs are formed. The formed secondary aggregated flocs are transferred to the secondary dewatering section 14 . As shown in FIGS. 2, 5, and 6, which will be described later in detail, the secondary aggregation section 13 has a different form depending on the machine used.

2次脱水部14は、1次脱水部12と同様に、公知の脱水装置で構成してあり、供給された2次凝集フロックを圧搾脱水しながら脱水ろ液を分離し、脱水ケーキを生成する。 The secondary dehydration section 14, like the primary dehydration section 12, is composed of a known dehydrator, and separates the dehydrated filtrate while compressing and dewatering the supplied secondary aggregated flocs to produce a dehydrated cake. .

なお、第1薬品供給管7を1次凝集部5に接続し、第1凝集剤を直接供給してもよい。また、汚泥の混練性を高めるために、汚泥供給管3にラインミキサーを配設してもよい。 Alternatively, the first chemical supply pipe 7 may be connected to the primary aggregation section 5 to directly supply the first coagulant. In addition, a line mixer may be arranged in the sludge supply pipe 3 in order to improve the kneading property of the sludge.

図2は本発明の実施形態に係る固液分離部の縦断側面図、図3は図2に示す1次脱水部の拡大図、図4は図2に示す2次凝集部の縦断面図である。
図2に示すように、固液分離部1は、1次脱水部12、2次凝集部13、2次脱水部14からなり、1次脱水部12で形成された濃縮汚泥を、1次脱水部12の吐出し側及び2次脱水部14の供給側に連設された2次凝集部13で凝集した後、2次脱水部14で脱水できる構成としてある。
2 is a longitudinal side view of the solid-liquid separation section according to the embodiment of the present invention, FIG. 3 is an enlarged view of the primary dewatering section shown in FIG. 2, and FIG. 4 is a longitudinal sectional view of the secondary aggregation section shown in FIG. be.
As shown in FIG. 2, the solid-liquid separation unit 1 comprises a primary dehydration unit 12, a secondary aggregation unit 13, and a secondary dehydration unit 14. After aggregation in the secondary aggregation section 13 connected to the discharge side of the section 12 and the supply side of the secondary dehydration section 14 , the secondary dehydration section 14 is configured to dewater.

1次脱水部12は、図3に示すように、ろ過面を有する円筒状の外筒スクリーン16と、外筒スクリーン16の内周面に摺接しながら回転する螺旋状のスクリュー羽根17を巻き掛けたスクリュー軸18と、を有する回転濃縮機12を採用している。回転濃縮機12は、外筒スクリーン16端部に入口外筒フランジ37と出口外筒フランジ61を嵌着し、外筒スクリーン16とスクリュー軸18の間に濃縮室19を形成している。 As shown in FIG. 3, the primary dehydrator 12 has a cylindrical outer cylindrical screen 16 having a filtering surface and a spiral screw blade 17 that rotates while being in sliding contact with the inner peripheral surface of the outer cylindrical screen 16. A rotary concentrator 12 having a screw shaft 18 is employed. The rotary concentrator 12 has an inlet outer cylinder flange 37 and an outlet outer cylinder flange 61 fitted to the ends of the outer cylinder screen 16 to form a concentrating chamber 19 between the outer cylinder screen 16 and the screw shaft 18 .

濃縮室19を形成する外筒スクリーン16は、出口外筒フランジ61に連結させた外筒駆動軸24の回動に伴い回動する。一方、スクリュー軸18は、フロントフレーム20に支架された汚泥供給管21によって回動自在に軸支されている。外筒スクリーン16及びスクリュー軸18は、図示しない駆動機にて差速回転できるように構成してある。 The outer cylinder screen 16 forming the concentration chamber 19 rotates as the outer cylinder driving shaft 24 connected to the outlet outer cylinder flange 61 rotates. On the other hand, the screw shaft 18 is rotatably supported by a sludge supply pipe 21 supported by the front frame 20 . The outer cylinder screen 16 and the screw shaft 18 are constructed so as to be differentially rotated by a driving machine (not shown).

スクリュー軸18の内部には、濃縮室19と汚泥供給管21を連通する汚泥供給路22が形成してあり、周面には、複数の供給口23を有している。汚泥供給管3から圧入供給された1次凝集フロックは、汚泥供給路22を通った後、供給口23より濃縮室19に流入する。濃縮室19に流入した1次凝集フロックは、水分を多く含んでおり、固形物負荷よりも水負荷が大きいため、圧入直後に外筒スクリーン16から濃縮ろ液が分離される。そして、排出側に向かって搬送されながら重力ろ過され濃縮ろ液がさらに分離される。 Inside the screw shaft 18, a sludge supply passage 22 is formed to connect the thickening chamber 19 and the sludge supply pipe 21, and a plurality of supply ports 23 are provided on the peripheral surface. The primary coagulated flocs press-fitted and supplied from the sludge supply pipe 3 pass through the sludge supply channel 22 and then flow into the thickening chamber 19 from the supply port 23 . The primary flocculated flocs that have flowed into the concentration chamber 19 contain a large amount of water, and the water load is greater than the solids load. Then, the concentrated filtrate is further separated by gravity filtration while being transported toward the discharge side.

濃縮ろ液を分離した1次凝集フロックは、濃縮汚泥となり、出口外筒フランジ61に形成された複数の排出口(図示しない)から濃縮汚泥槽27に排出された後、2次凝集部13に送られる。 The primary flocculated flocs from which the concentrated filtrate is separated become thickened sludge, and after being discharged into the thickened sludge tank 27 through a plurality of outlets (not shown) formed in the outlet outer cylinder flange 61, the secondary flocculation unit 13 Sent.

2次凝集部13は、図4に示すように、濃縮汚泥槽27及び濃縮汚泥槽27の下部側壁に接続された濃縮汚泥供給ポンプ28で構成してある。濃縮汚泥槽27は、供給された濃縮汚泥を一時的に貯留するものであり、濃縮汚泥は濃縮汚泥供給ポンプ28によって2次脱水部14に圧入供給される。 As shown in FIG. 4, the secondary coagulation section 13 is composed of a thickened sludge tank 27 and a thickened sludge supply pump 28 connected to the lower side wall of the thickened sludge tank 27 . The thickened sludge tank 27 temporarily stores the supplied thickened sludge.

濃縮汚泥槽27の側面には、第2薬品供給管10を接続してあり、濃縮汚泥槽27内に第2凝集剤を添加できるように構成してある。第2薬品供給管10の周面には加温装置15を被覆させており、第2薬品供給管10を通って濃縮汚泥槽27に供給される無機凝集剤を加温する。第2薬品供給管10の周面から内部に熱を加えることで、無機凝集剤を効率よく加温できる。加温装置15は、第2薬品供給管10の濃縮汚泥槽27近傍部分を被覆し、無機凝集剤を濃縮汚泥槽27へ供給する直前で加温することが望ましい。これにより無機凝集剤が冷めることなく濃縮汚泥に供給することができる。また、加温された無機凝集剤を添加することで濃縮汚泥も間接的に加温されるため、濃縮汚泥の脱水性が向上する。 A second chemical supply pipe 10 is connected to the side surface of the thickened sludge tank 27 so that the second coagulant can be added to the thickened sludge tank 27 . The circumferential surface of the second chemical supply pipe 10 is covered with a heating device 15 to heat the inorganic flocculant supplied to the thickened sludge tank 27 through the second chemical supply pipe 10 . By applying heat to the inside from the peripheral surface of the second chemical supply pipe 10, the inorganic coagulant can be efficiently heated. It is desirable that the heating device 15 covers the portion of the second chemical supply pipe 10 near the thickened sludge tank 27 and heats the inorganic flocculant immediately before supplying it to the thickened sludge tank 27 . As a result, the inorganic flocculant can be supplied to the concentrated sludge without cooling. Moreover, since the thickened sludge is also indirectly heated by adding the heated inorganic flocculant, the dewaterability of the thickened sludge is improved.

なお、第2凝集剤は、40度~90度に加温しておくことが望ましい。該温度とすることで凝集剤の流動性が高くなり、濃縮汚泥に分散しやすくなる。また、無機凝集剤の代わりに高分子凝集剤を加温して濃縮汚泥に添加してもよい。加温装置15は公知の電気式ジャケットヒーターや、ジャケット部に温水、排ガス等の熱媒体を供給する温水式等、制限されない。その他、加温装置15を第2薬品槽9に配置し、第2薬品槽9内で無機凝集剤を加温する手段や、事前に加温した温水を無機凝集剤に供給して加温する手段をとってもよい。熱媒体を用いる場合には消化処理、焼却処理等、他の工程で発生する熱媒体を利用できるためエネルギーを有効利用できる。 It is desirable to heat the second flocculant to 40 to 90 degrees. At this temperature, the fluidity of the flocculant is increased, and it becomes easier to disperse in the thickened sludge. Further, instead of the inorganic flocculant, a polymer flocculant may be heated and added to the thickened sludge. The heating device 15 is not limited to a known electric jacket heater, a hot water type that supplies a heating medium such as hot water or exhaust gas to the jacket portion, or the like. In addition, a heating device 15 is arranged in the second chemical tank 9 to heat the inorganic coagulant in the second chemical tank 9, or preheated hot water is supplied to the inorganic coagulant to heat it. You can take measures. When a heat medium is used, energy can be effectively used because the heat medium generated in other processes such as digestion and incineration can be used.

濃縮汚泥供給ポンプ28は、一軸ねじポンプ等の容積型ねじポンプを採用している。濃縮汚泥槽27から供給された濃縮汚泥及び加温された無機凝集剤は、濃縮汚泥槽27下部に接続された吸込口29を通って、ロータ30とステータ31の間に形成された一定容積の空隙36に螺旋状に吸い込まれ下方に向かって混合されながら移動した後、駆動軸34周部に半径方向に突出した複数の撹拌翼32によってさらに混合撹拌される。空隙36を移動する濃縮汚泥は脈動しないため、2次凝集フロックは破壊されない。そのうえ、下方に位置する撹拌翼32によってさらに混合され凝集反応が進むため、強固で緻密な2次凝集フロックを形成できる。なお、ロータ30及び撹拌翼32は、駆動機33から延設された駆動軸34と連結し、回動自在に構成している。 The thickened sludge supply pump 28 employs a positive displacement screw pump such as a single screw pump. The thickened sludge and the heated inorganic flocculant supplied from the thickened sludge tank 27 pass through the suction port 29 connected to the bottom of the thickened sludge tank 27, and flow through the fixed volume of the rotor 30 and the stator 31 formed between the rotor 30 and the stator 31. After being spirally sucked into the gap 36 and moving downward while being mixed, the mixture is further mixed and stirred by a plurality of stirring blades 32 protruding radially around the driving shaft 34 . Since the thickened sludge moving through the voids 36 does not pulsate, the secondary flocculation flocs are not destroyed. In addition, since the agglomeration reaction proceeds by further mixing by the stirring blades 32 positioned below, strong and dense secondary agglomerated flocs can be formed. The rotor 30 and the stirring blades 32 are connected to a driving shaft 34 extending from a driving machine 33 so as to be rotatable.

なお、第2薬品供給管10を濃縮汚泥槽27に接続したが、吸込口29や濃縮汚泥供給ポンプ28の側面や、後述する2次脱水部14に接続してもよい。2次脱水部14に接続する場合は、例えば、図2の供給路51や、濃縮汚泥を受け入れるろ過室48の始端側等、2次脱水部の汚泥供給側に接続し、供給直後の濃縮汚泥に第2凝集剤を添加することが望ましい。さらに第2薬品供給管10を分岐させ、回転濃縮機12、濃縮汚泥供給ポンプ28、2次脱水部14に接続し、選択した複数箇所に無機凝集剤を同時もしくは交互に添加する構成としてもよい。 Although the second chemical supply pipe 10 is connected to the thickened sludge tank 27, it may be connected to the suction port 29, the side surface of the thickened sludge supply pump 28, or the secondary dehydrator 14, which will be described later. When connecting to the secondary dehydration unit 14, for example, it is connected to the sludge supply side of the secondary dehydration unit, such as the supply path 51 in FIG. It is desirable to add a second flocculant to. Furthermore, the second chemical supply pipe 10 may be branched and connected to the rotary concentrator 12, the thickened sludge supply pump 28, and the secondary dehydrator 14, and the inorganic flocculant may be added simultaneously or alternately to a plurality of selected locations. .

その他、図3に示すように、第2薬品供給管10をスクリュー駆動軸24に接続し、スクリュー軸18及びスクリュー駆動軸24の内部に配設された薬品供給路38に連通させ、濃縮室19に開口したスクリュー軸18のノズル孔39から加温した無機凝集剤を供給してもよい。スクリュー羽根18の最終ピッチ間の外筒スクリーン16には非透過性の環状筒40が連設してあり、回動する環状筒40の周面に沿って濃縮汚泥と加温した無機凝集剤が混合される。この形態も、濃縮汚泥供給ポンプ28の前段で無機凝集剤を添加するため、後段に位置する濃縮汚泥供給ポンプ28内で濃縮汚泥と無機凝集剤を効率よく混合することができる。このように、第2薬品供給管は、1次脱水部12、2次凝集部13及び後述する2次脱水部14のうち少なくとも1箇所に接続される。 In addition, as shown in FIG. 3, the second chemical supply pipe 10 is connected to the screw drive shaft 24 and communicated with the screw shaft 18 and the chemical supply path 38 disposed inside the screw drive shaft 24, and the concentration chamber 19 is A heated inorganic flocculant may be supplied from the nozzle hole 39 of the screw shaft 18 opened to the outside. An impermeable ring-shaped cylinder 40 is connected to the outer cylinder screen 16 between the final pitches of the screw blades 18, and the thickened sludge and the heated inorganic flocculant flow along the peripheral surface of the rotating ring-shaped cylinder 40. mixed. In this form as well, since the inorganic flocculant is added before the thickened sludge feed pump 28, the thickened sludge and the inorganic flocculant can be efficiently mixed in the thickened sludge feed pump 28 located at the latter stage. Thus, the second chemical supply pipe is connected to at least one of the primary dewatering section 12, the secondary aggregation section 13, and the secondary dehydration section 14, which will be described later.

2次凝集部13で形成された2次凝集フロックは、濃縮汚泥供給ポンプ28によって図2に示す2次脱水部14に圧入される。2次脱水部14は、ろ過面を有する円筒状の外筒スクリーン46と、外筒スクリーン46の内周を摺接しながら回転する螺旋状のスクリュー羽根47を巻き掛けたスクリュー軸45と、を有するスクリュープレス14を採用している。スクリュープレス14は、供給側を濃縮汚泥供給ポンプ28の吐出口35と連設するとともに、上方に載置した回転濃縮機12と一体的に構成してある。 The secondary coagulation flocs formed in the secondary coagulation section 13 are forced into the secondary dehydration section 14 shown in FIG. The secondary dehydrator 14 has a cylindrical outer cylindrical screen 46 having a filtering surface, and a screw shaft 45 around which a spiral screw blade 47 rotates while slidingly contacting the inner circumference of the outer cylindrical screen 46 . A screw press 14 is employed. The screw press 14 is connected on the supply side to the discharge port 35 of the thickened sludge supply pump 28 and is integrated with the rotary thickener 12 placed above.

外筒スクリーン46の内周面とスクリュー軸45の外周面との間には、スクリュー羽根47で螺旋状に仕切られたろ過室48が形成されている。また、汚泥の供給側から排出側に向かってテーパー状に拡開したスクリュー軸45を用いているため、ろ過室48は、汚泥の供給側から排出側に向かって縮小している。 Between the inner peripheral surface of the outer cylindrical screen 46 and the outer peripheral surface of the screw shaft 45, a filtration chamber 48 spirally partitioned by screw blades 47 is formed. Further, since the screw shaft 45 is tapered and expanded from the sludge supply side to the discharge side, the filtration chamber 48 is reduced from the sludge supply side to the discharge side.

ろ過室48を形成する外筒スクリーン46の供給側端部には、入口外筒フランジ41を嵌着しており、入口外筒フランジ41にはスプロケット42を外嵌している。スプロケット42は、フロントフレーム43に載置した正逆転可能な外筒駆動機44に連動連結されており、外筒スクリーン46が正逆に回動できる。一方、スクリュー軸45は、排出側端部にスクリュー駆動軸49を連結している。スクリュー駆動軸49は、スクリュー駆動機50の駆動によって回動可能に構成してある。
An inlet outer cylinder flange 41 is fitted to the feed side end of the outer cylinder screen 46 forming the filtration chamber 48 , and a sprocket 42 is fitted to the inlet outer cylinder flange 41 . The sprocket 42 is interlocked with a reversible outer cylinder driving device 44 placed on the front frame 43, so that the outer cylinder screen 46 can rotate reversibly. On the other hand, the screw shaft 45 has a screw drive shaft 49 connected to the discharge side end. The screw driving shaft 49 is configured to be rotatable by being driven by a screw driving machine 50 .

スクリュー軸45の始端側には供給路51を接続してあり、周面には複数の供給口52を開口させている。供給路51は、濃縮汚泥供給ポンプ28の吐出口に摺接させてあり、濃縮汚泥供給ポンプ28から圧入供給された2次凝集フロックは、供給路51を通った後、供給口52からろ過室48に流入する。流入した2次凝集フロックは、固形物負荷よりも水負荷が大きいため、外筒スクリーン46から大量の脱水ろ液が排出される。そして、ろ過室46が始端側から排出側に向かって容積が漸減しているため、排出側に向かって移送される2次凝集フロックはろ過室46の容積変化及び回動するスクリュー羽根47によるスラスト力を受けて内部圧力を上昇させながら圧搾脱水されて脱水ろ液を分離し、ケーキ化する。 A supply passage 51 is connected to the starting end side of the screw shaft 45, and a plurality of supply ports 52 are opened on the peripheral surface. The supply path 51 is in sliding contact with the discharge port of the thickened sludge supply pump 28, and the secondary flocculated flocs press-fitted and supplied from the thickened sludge supply pump 28 pass through the supply path 51 and then from the supply port 52 to the filter chamber. Flow into 48. Since the secondary flocculated floc that has flowed in has a larger water load than the solids load, a large amount of dewatered filtrate is discharged from the outer cylindrical screen 46 . Since the volume of the filtration chamber 46 gradually decreases toward the discharge side from the starting end side, the secondary flocculated flocs transferred toward the discharge side change the volume of the filtration chamber 46 and the thrust due to the rotating screw blades 47. The dehydrated filtrate is separated by compressing and dehydrating while increasing the internal pressure by receiving force to form a cake.

ろ過室48を移送する2次凝集フロックは、加温された無機凝集剤と混合されて粗大化するため、外筒スクリーン46から目抜けしない。そのうえ、SS含有率が高く緻密で強固であるため、スクリュープレス14の脱水性能を高め、短時間で低含水率の脱水ケーキを得ることができる。生成された脱水ケーキは、排出側に設けられシリンダー54に接続されたプレッサー53による背圧を受けてさらに圧搾され含水率を低下させた後、排出される。なお、脱水運転時に外筒スクリーン46を固定しているが、回動させてもよい。 The secondary coagulated flocs transported through the filtration chamber 48 are mixed with the heated inorganic coagulant and coarsened, so that the outer cylindrical screen 46 does not pass through. In addition, since the SS content is high and the cake is dense and firm, the dewatering performance of the screw press 14 is enhanced, and a dehydrated cake with a low moisture content can be obtained in a short time. The produced dehydrated cake is subjected to back pressure by a presser 53 provided on the discharge side and connected to the cylinder 54, and is further compressed to reduce the water content, and then discharged. Although the outer cylindrical screen 46 is fixed during the dewatering operation, it may be rotated.

本実施形態では、スクリュープレス14の上方に回転濃縮機12を載置し一体的に構成したが、上方にベルト濃縮機を載置する等、一体的に構成する1次脱水部12、2次脱水部13の機構は限定されない。また、スクリュープレス14の入口側に1次脱水部12を配置する構成や、外筒固定式スクリュープレス14の側面に濃縮汚泥供給ポンプ28を介して、1次脱水部12を接続してもよい。その他、固液分離部1を構成する各構成要素を配管で接続し、1次脱水部12と2次凝集部13の間に備えた配管に第2薬品供給管10を接続させる構成としてもよい。2次凝集部13の構成に関しても、1次脱水部12と2次脱水部14の間に公知のホッパーを配置し重力を利用して濃縮汚泥を2次脱水部14へ自然流下させて供給してもよい。 In this embodiment, the rotary concentrator 12 is placed above the screw press 14 and configured integrally. The mechanism of the dewatering section 13 is not limited. Alternatively, the primary dewatering unit 12 may be arranged on the inlet side of the screw press 14, or the primary dewatering unit 12 may be connected to the side surface of the fixed outer cylinder type screw press 14 via a thickened sludge supply pump 28. . Alternatively, each component constituting the solid-liquid separation unit 1 may be connected by a pipe, and the second chemical supply pipe 10 may be connected to the pipe provided between the primary dehydration unit 12 and the secondary aggregation unit 13. . Regarding the configuration of the secondary flocculation section 13, a known hopper is arranged between the primary dehydration section 12 and the secondary dehydration section 14, and the thickened sludge is naturally flowed down to the secondary dehydration section 14 using gravity and supplied. may

図5、図6は、他の実施形態に係る汚泥処理方法の概略構成図である。
図5は、1次凝集フロックを形成する1次凝集部5と、1次凝集フロック中の水分を自重によって脱水し濃縮汚泥を形成する1次脱水部12(ベルト濃縮機)と、形成された濃縮汚泥に加温した無機凝集剤を添加した後、混合し2次凝集フロックを形成する2次凝集部13と、2次凝集フロックをベルト間で挟んで圧搾脱水し脱水ケーキを生成する2次脱水部14(ベルトプレス)と、からなる固液分離部1を示している。1次脱水部12及び2次脱水部14は複数のローラー58にろ布59を走行自在に掛けまわして構成してある。
5 and 6 are schematic configuration diagrams of a sludge treatment method according to another embodiment.
FIG. 5 shows a primary flocculation unit 5 that forms primary flocculation flocs, and a primary dehydration unit 12 (belt thickener) that dehydrates water in the primary flocculation flocs by its own weight to form thickened sludge. After adding a heated inorganic flocculant to the thickened sludge, a secondary flocculation unit 13 that mixes to form secondary flocculation, and a secondary flocculation unit that sandwiches the secondary flocculation flocs between belts and compresses and dehydrates to produce a dehydrated cake. A dewatering section 14 (belt press) and a solid-liquid separation section 1 are shown. The primary dehydrating section 12 and the secondary dehydrating section 14 are constructed by movably winding a filter cloth 59 around a plurality of rollers 58 .

1次脱水部12から2次脱水部14へ供給される濃縮汚泥に加温した第2凝集剤(無機凝集剤)を添加することで、無機凝集剤が汚泥中に効率よく分散するため、短時間で緻密で強固な2次凝集フロックを形成できる。緻密で強固な2次凝集フロックは、SS分が多く含まれており流動性が低いため、サイドリークが生じない。サイドリークを防止することで、2次脱水部14における脱水性能を高めることも可能となる。 By adding a heated second coagulant (inorganic coagulant) to the thickened sludge supplied from the primary dehydration unit 12 to the secondary dehydration unit 14, the inorganic coagulant is efficiently dispersed in the sludge. Dense and strong secondary aggregated flocs can be formed in a short period of time. The dense and strong secondary aggregated flocs contain a large amount of SS and have low fluidity, so side leaks do not occur. By preventing side leaks, it is also possible to improve the dehydration performance in the secondary dehydration section 14 .

なお、第2凝集剤の添加手段は制限されず、例えば、濃縮汚泥が1次脱水部12から2次脱水部14に越流する際に噴射して添加する、1次脱水部12と2次脱水部14の間に凝集混和槽を設置し凝集混和槽内に添加する等、適宜選択する。 In addition, the means for adding the second flocculant is not limited, for example, the primary dehydration unit 12 and the secondary An aggregating-mixing tank is installed between the dewatering units 14, and the material is added to the aggregating-mixing tank.

図6は、固液分離部1に公知の遠心分離機を採用し、1次凝集部5で形成された1次凝集フロックを固液分離する際に加温した第2凝集剤(無機凝集剤)を添加するものである。1次凝集フロックは、回転する内胴55及び外胴56の間に形成された供給室57に供給された後、回転体に加わる径方向の遠心力によって質量密度の高い固形物が外胴56の内周面に沈降乃至堆積するとともに、固形物の内側に位置する質量密度の低い分離液が排出される。遠心分離機前段の1次脱水部12で遠心力によって1次凝集フロック中の水分を分離しながら濃縮汚泥を形成し、加温した第2凝集剤とともに混合されて2次凝集フロックを形成する。形成された2次凝集フロックは遠心分離機後段の2次脱水部14で遠心力によって2次凝集フロック中の水分をさらに分離し脱水ケーキとなる。なお、遠心分離機1は、図示しないモータにて回転する外胴56と、スクリュー60を有し外胴56内部で外胴56に対して差速回転する内胴55を軸支している。 FIG. 6 shows a second flocculant (inorganic flocculant ) is added. After the primary agglomerated flocs are supplied to a supply chamber 57 formed between the rotating inner drum 55 and outer drum 56 , the solid matter having a high mass density is transferred to the outer drum 56 by radial centrifugal force applied to the rotating body. A separated liquid with a low mass density located inside the solid matter is discharged while it settles or accumulates on the inner peripheral surface of the solid matter. In the primary dewatering section 12 at the front stage of the centrifuge, concentrated sludge is formed while separating moisture from the primary coagulated flocs by centrifugal force, and mixed with the heated second coagulant to form secondary coagulated flocs. The formed secondary flocculated flocs are subjected to centrifugal force in the secondary dewatering unit 14 at the latter stage of the centrifugal separator to further separate the moisture in the secondary flocs to form a dehydrated cake. The centrifuge 1 supports an outer shell 56 rotated by a motor (not shown) and an inner shell 55 having a screw 60 and rotating at a differential speed relative to the outer shell 56 inside the outer shell 56 .

加温した無機凝集剤を用いて2次凝集することで、遠心分離機内で効率よく1次凝集フロックと凝集剤を混合できるため短時間で強固な2次凝集フロックを形成できる。これに伴い、低含水率の脱水ケーキを短時間で生成できるため、内胴55及び外胴56を駆動するモータの駆動時間を削減できるため、ランニングコスト低減にもつながる。 By performing secondary aggregation using a heated inorganic coagulant, the primary aggregated flocs and the coagulant can be efficiently mixed in the centrifuge, so that strong secondary aggregated flocs can be formed in a short period of time. As a result, the dehydrated cake having a low water content can be produced in a short time, so that the driving time of the motors for driving the inner drum 55 and the outer drum 56 can be reduced, leading to a reduction in running costs.

なお、1次脱水、2次凝集及び2次脱水を1つの装置で実施しているが、2つの遠心分離機ないし遠心分離機とその他の脱水機を組み合わせて別々に実施する方法であってもよい。また、本実施例及び図5、図6は、1次凝集部5として凝集混和槽を採用しているが、これに限定されない。 Although the primary dehydration, secondary agglomeration and secondary dehydration are performed in one device, even if it is a method of separately performing two centrifuges or a combination of a centrifuge and another dehydrator good. In addition, although the present embodiment and FIGS. 5 and 6 employ the aggregating and mixing tank as the primary aggregating section 5, the present invention is not limited to this.

上述し、かつ図面に記載した本実施形態に限定されるものではなく、特許請求の範囲に記載した発明の要旨を逸脱しない範囲で変形実施を可能とする。
The present invention is not limited to the embodiments described above and illustrated in the drawings, and modifications can be made without departing from the gist of the invention described in the claims.

本発明に係る加温凝集剤を用いた汚泥処理方法は、2次凝集工程時に加温した凝集剤を用いて汚泥を凝集することで、汚泥との混練性を高めることが可能となり、短時間で粗大で強固な凝集フロックを形成できる。これにより、凝集剤使用量を削減できるとともに、凝集剤が汚泥と未反応のまま流れ出ることがない。そして、強固な凝集フロックを脱水装置に供給できるため、後段の脱水工程で効率よく脱水を行うことができる。脱水工程で使用する固液分離装置の運転時間が削減されることで燃料の使用量が減少するため、二酸化炭素排出量削減にもつながる。本発明は凝集剤使用量及び固液分離装置の運転時間を削減する脱水処理方法であり、環境に配慮した運転ができるものである。 In the sludge treatment method using a heated flocculant according to the present invention, by flocculating sludge using a heated flocculant during the secondary flocculation step, it is possible to improve the kneadability with the sludge and shorten the time. can form coarse and strong aggregated flocs. As a result, the amount of coagulant used can be reduced, and the coagulant does not flow out without reacting with the sludge. In addition, since strong aggregated flocs can be supplied to the dehydrator, dehydration can be efficiently performed in the subsequent dehydration step. The reduced operating time of the solid-liquid separator used in the dehydration process reduces the amount of fuel used, leading to a reduction in carbon dioxide emissions. INDUSTRIAL APPLICABILITY The present invention is a dehydration treatment method that reduces the amount of coagulant used and the operating time of a solid-liquid separator, and enables environmentally friendly operation.

5 1次凝集部
10 第2薬品供給管
12 1次脱水部
13 2次凝集部
14 2次脱水部
15 加温装置
5 Primary aggregation section 10 Second chemical supply pipe 12 Primary dehydration section 13 Secondary aggregation section 14 Secondary dehydration section 15 Heating device

Claims (2)

1次凝集部(5)で汚泥と第1凝集剤を混合し1次凝集フロックを形成した後、1次脱水部(12)で濃縮し、形成された濃縮汚泥を第2凝集剤とともに混合して2次凝集フロックを形成した後、2次脱水部(14)で脱水する汚泥処理方法において、
濃縮汚泥に加温した第2凝集剤を添加する
ことを特徴とする加温凝集剤を用いた汚泥処理方法。
After the sludge and the first flocculant are mixed in the primary flocculating section (5) to form primary flocculated flocs, they are concentrated in the primary dewatering section (12), and the thickened sludge thus formed is mixed with the second flocculant. In the sludge treatment method for forming secondary flocculated flocs and then dewatering in the secondary dewatering section (14),
A sludge treatment method using a heated coagulant, characterized by adding a heated second coagulant to thickened sludge.
前記第2凝集剤を前記1次脱水部(12)、2次凝集部(13)及び前記2次脱水部(14)のうち少なくとも1箇所に接続された第2薬品供給管(10)の周面に設けた加温装置(15)で加温する
ことを特徴とする請求項1に記載の加温凝集剤を用いた汚泥処理方法。
around a second chemical supply pipe (10) connected to at least one of the primary dehydration section (12), the secondary aggregation section (13) and the secondary dehydration section (14); The sludge treatment method using a heated flocculant according to claim 1, characterized in that the heating is performed by a heating device (15) provided on the surface.
JP2022009796A 2022-01-26 2022-01-26 Sludge treatment method using heated flocculant Pending JP2023108648A (en)

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Country Link
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