JP7647439B2 - Sludge treatment method - Google Patents
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- JP7647439B2 JP7647439B2 JP2021133351A JP2021133351A JP7647439B2 JP 7647439 B2 JP7647439 B2 JP 7647439B2 JP 2021133351 A JP2021133351 A JP 2021133351A JP 2021133351 A JP2021133351 A JP 2021133351A JP 7647439 B2 JP7647439 B2 JP 7647439B2
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- 239000010802 sludge Substances 0.000 title claims description 137
- 238000000034 method Methods 0.000 title claims description 28
- 239000002351 wastewater Substances 0.000 claims description 97
- 238000004065 wastewater treatment Methods 0.000 claims description 56
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 36
- 230000008719 thickening Effects 0.000 claims description 30
- 239000002245 particle Substances 0.000 claims description 27
- 239000000701 coagulant Substances 0.000 claims description 8
- 238000005406 washing Methods 0.000 claims description 6
- 102000001999 Transcription Factor Pit-1 Human genes 0.000 description 5
- 108010040742 Transcription Factor Pit-1 Proteins 0.000 description 5
- 238000007689 inspection Methods 0.000 description 5
- 239000007788 liquid Substances 0.000 description 5
- 238000010979 pH adjustment Methods 0.000 description 5
- 238000004062 sedimentation Methods 0.000 description 5
- 239000002440 industrial waste Substances 0.000 description 4
- 238000010248 power generation Methods 0.000 description 4
- 238000004140 cleaning Methods 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 230000015271 coagulation Effects 0.000 description 2
- 238000005345 coagulation Methods 0.000 description 2
- 238000004090 dissolution Methods 0.000 description 2
- 238000005189 flocculation Methods 0.000 description 2
- 230000016615 flocculation Effects 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 1
- 238000005192 partition Methods 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
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- Treatment Of Sludge (AREA)
Description
本発明は、例えば火力発電所等の発電施設が有する排水処理施設内における所定の排水貯槽に沈殿堆積した汚泥の処理方法に関する。 The present invention relates to a method for treating sludge that has settled and accumulated in a specified wastewater storage tank in a wastewater treatment facility at a power generation facility such as a thermal power plant.
濃縮槽と脱水機とを備えた排水処理施設の一例が特許文献1に示されており、この排水処理施設は、排煙脱硫排水を処理して生じたスラリーを濃縮槽に送って濃縮槽内で沈殿濃縮した後、脱水機に送り、脱水処理して所定の水分濃度まで下げてケーキ化し、トラックにてケーキを産業廃棄物として外部に搬出している。 One example of a wastewater treatment facility equipped with a thickening tank and a dehydrator is shown in Patent Document 1. In this wastewater treatment facility, the slurry generated by treating flue gas desulfurization wastewater is sent to a thickening tank where it is precipitated and thickened, then sent to the dehydrator where it is dehydrated to reduce the moisture concentration to a specified level and turned into a cake, which is then transported by truck to the outside as industrial waste.
一方で、例えば火力発電所等の発電施設が有する排水処理施設は、ボイラにおいて熱交換をする、空気予熱器(AH)と呼ばれる熱交換器が灰等で目詰まりするのを防止し、或いは熱交換器が灰等で目詰まりした状態を解消するために、前記空気予熱器(熱交換器)を水洗して生じた水等が送られる2つの並設された排水貯槽(例えば、一方がA排水貯槽、他方がB排水貯槽と称される。)が設置されている場合がある。 On the other hand, wastewater treatment facilities at power generation facilities such as thermal power plants may have two parallel wastewater storage tanks (for example, one is called wastewater storage tank A and the other is called wastewater storage tank B) to which water, etc. produced by rinsing the air preheater (heat exchanger) is sent to prevent the heat exchanger called an air preheater (AH), which exchanges heat in the boiler, from becoming clogged with ash, etc., or to eliminate a state in which the heat exchanger is clogged with ash, etc.
これらの2つの並設された排水貯槽には、空気予熱器(熱交換器)の水洗を繰り返すことに伴って、当該空気予熱器(熱交換器)の水洗により生じた粒子の大きな汚泥が時間の経過とともに沈殿し堆積していくこととなる。 In these two parallel wastewater storage tanks, as the air preheater (heat exchanger) is repeatedly washed with water, large particles of sludge produced by the washing of the air preheater (heat exchanger) settle and accumulate over time.
しかしながら、これまでは、このような排水貯槽に沈殿堆積されていく粒子の大きな汚泥の処理方法が確立していなかった。このため、2つの並設された排水貯槽について例えば2年間隔等の一定周期で交互に定期点検を行う必要があるところ、一方の排水貯槽の定期点検を行う場合には、一方の排水貯槽から他方の排水貯槽に沈殿堆積している汚泥を移送するという方法を採っていた。 However, until now, there has been no established method for treating the large-particle sludge that settles and accumulates in these wastewater storage tanks. For this reason, it has been necessary to alternately carry out regular inspections of the two parallel wastewater storage tanks at regular intervals, for example every two years. When carrying out regular inspections of one of the wastewater storage tanks, the method adopted has been to transfer the sludge that has settled and accumulated from one wastewater storage tank to the other.
もっとも、一方の排水貯槽から他方の排水貯槽に沈殿堆積している汚泥を移送するのみでは、排水貯槽に沈殿堆積している粒子の大きな汚泥に対する最終的な解決方法にはならない。このため、排水貯槽が汚泥の沈殿堆積により機能を果たさなくなる前に、排水貯槽からの汚泥の除去並びにかかる汚泥の処理を図る必要があり、汚泥の処理費用が高額になることが考えられる。また、双方の排水貯槽に沈殿堆積する粒子が大きな汚泥の総量も時間の経過により暫時多くなるので、一方の排水貯槽から他方の排水貯槽に汚泥を移送する時間も長くなるという不都合が生ずる。 However, simply transferring the sludge that has settled and accumulated from one wastewater storage tank to the other is not a final solution to the problem of large-particle sludge that has settled and accumulated in the wastewater storage tank. For this reason, it is necessary to remove the sludge from the wastewater storage tank and treat it before the wastewater storage tank becomes unable to function due to the settlement and accumulation of sludge, which is likely to result in high sludge treatment costs. In addition, the total amount of large-particle sludge that has settled and accumulated in both wastewater storage tanks will gradually increase over time, resulting in the inconvenience of it taking longer to transfer sludge from one wastewater storage tank to the other.
本発明は、かかる課題を解決するためになされたものであり、粒子の大きな汚泥は重く自然に沈殿するので、このような汚泥に対し沈殿可能な状態にするための工程を必要としないことに着目した汚泥の処理方法を提供することを主たる課題としている。 The present invention was made to solve these problems, and its main objective is to provide a sludge treatment method that focuses on the fact that since sludge with large particles is heavy and settles naturally, there is no need for a process to make such sludge settleable.
上記課題を達成するために、本発明の汚泥の処理方法は、所定の器具の水洗により生じた水が送られる排水貯槽と、前記排水貯槽に送られてきた水を処理する排水処理系統と、前記排水貯槽から前記排水処理系統を経由してきた水に含まれる汚泥を処理する第1の汚泥処理系統とを備え、前記排水処理系統は、当該排水処理系統を構成する設備として、前記排水貯槽から送られてきた水に含まれる汚泥を沈殿させる沈殿槽を有し、前記第1の汚泥処理系統は、当該第1の汚泥処理系統を構成する設備として、前記汚泥を所定の水分濃度まで脱水してケーキにする脱水機を有する排水処理施設で用いられる汚泥の処理方法であって、前記排水貯槽から前記排水処理系統を経由する水に含まれる汚泥よりも粒子の大きな汚泥を、前記排水貯槽から取り出す工程と、前記汚泥を、前記排水処理系統のうちの前記排水貯槽から前記沈殿槽までを経由せずに、前記汚泥に凝集剤を注入した状態で前記脱水機に送る工程とを有する第2の汚泥処理系統を形成したことを特徴としている。排水処理施設は、例えば火力発電所等の発電施設が有する排水処理施設である。所定の器具とは、例えばボイラにおいて熱交換をする空気予熱器と呼ばれる熱交換器である。排水貯槽とは、例えば、一方がA排水貯槽、他方がB排水貯槽と称される2つの並設された排水貯槽である。 In order to achieve the above object, the sludge treatment method of the present invention is a method for treating sludge used in a wastewater treatment facility, comprising a wastewater storage tank to which water generated by washing a specified appliance is sent, a wastewater treatment system for treating the water sent to the wastewater storage tank, and a first sludge treatment system for treating sludge contained in the water that has passed through the wastewater treatment system from the wastewater storage tank, the wastewater treatment system having a settling tank for settling the sludge contained in the water sent from the wastewater storage tank as a component of the wastewater treatment system, and the first sludge treatment system having a dehydrator for dehydrating the sludge to a predetermined moisture concentration to form a cake as a component of the first sludge treatment system, characterized in that a second sludge treatment system is formed having a step of removing from the wastewater storage tank sludge having larger particles than the sludge contained in the water that passes through the wastewater treatment system from the wastewater storage tank, and a step of sending the sludge to the dehydrator in a state in which a coagulant has been injected into the sludge, without passing through the wastewater storage tank to the settling tank of the wastewater treatment system. The wastewater treatment facility is, for example, a wastewater treatment facility in a power generation facility such as a thermal power plant. The specific equipment is, for example, a heat exchanger called an air preheater that performs heat exchange in a boiler. The wastewater storage tank is, for example, two wastewater storage tanks arranged in parallel, one of which is called wastewater storage tank A and the other is called wastewater storage tank B.
これにより、所定の器具の水洗により生じた、排水貯槽から排水処理系統に送られる水に含まれる汚泥よりも粒子の大きな汚泥について、第2の汚泥処理系統を形成することで前記排水貯槽から取り出して処理することが可能になった。しかも、排水貯槽の点検タイミングで、点検対象の排水貯槽内に堆積した粒子の大きな汚泥を排出することができるので、汚泥の排出作業に要する費用の低減を図ることが可能である。更には、第2の汚泥処理系統の工程で第1の汚泥処理系統の設備である脱水機を用いることが可能であるので、新たな設備を必要としない。 As a result, by forming a second sludge treatment system, it is possible to remove and treat sludge that is generated by washing certain equipment and has larger particles than the sludge contained in the water sent from the wastewater storage tank to the wastewater treatment system. Moreover, since the sludge with larger particles that has accumulated in the wastewater storage tank to be inspected can be discharged at the timing of the inspection of the wastewater storage tank, it is possible to reduce the cost required for the sludge discharge work. Furthermore, since the dehydrator, which is equipment of the first sludge treatment system, can be used in the process of the second sludge treatment system, no new equipment is required.
そして、本発明の汚泥の処理方法では、前記排水処理施設は、前記第1の汚泥処理系統を構成する設備として、前記脱水機で脱水される前の状態の汚泥が送られる濃縮槽を更に有すると共に、前記第2の汚泥処理系統として、前記排水貯槽から前記排水処理系統を経由する水に含まれる汚泥よりも粒子の大きな汚泥を、前記排水貯槽から取り出して前記濃縮槽に直接に送る工程と、前記汚泥が前記濃縮槽から前記脱水機に送られる間に前記汚泥に前記凝集剤を注入する工程とを有することを特徴としている。 In the sludge treatment method of the present invention, the wastewater treatment facility further includes a thickening tank to which sludge before being dewatered by the dehydrator is sent as equipment constituting the first sludge treatment system, and includes, as the second sludge treatment system, a process for removing sludge having larger particles than the sludge contained in the water passing through the wastewater treatment system from the wastewater storage tank and sending it directly to the thickening tank, and a process for injecting the coagulant into the sludge while it is being sent from the thickening tank to the dehydrator.
これにより、排水貯槽から取り出した、当該排水貯槽から排水処理系統に送られる水に含まれる汚泥よりも粒子の大きな汚泥を濃縮槽に沈殿させることが可能となり、濃縮槽に設けられたポンプや濃縮槽と脱水機とを接続する配管を利用して、前記汚泥を濃縮槽から脱水機に円滑に移送させることができる。しかも第2の汚泥処理系統の工程で第1の汚泥処理系統の設備である濃縮槽やその周辺設備を用いることが可能であるので、新たな設備を必要としない。 This makes it possible to settle in the thickening tank sludge that is larger in particles than the sludge contained in the water removed from the wastewater storage tank and sent from the wastewater storage tank to the wastewater treatment system, and the sludge can be smoothly transferred from the thickening tank to the dehydrator using a pump installed in the thickening tank and piping connecting the thickening tank and the dehydrator. Moreover, since the thickening tank and its peripheral equipment, which are the equipment of the first sludge treatment system, can be used in the process of the second sludge treatment system, no new equipment is required.
以上に述べたように、本発明の汚泥の処理方法によれば、所定の器具の水洗により生じた、排水貯槽から排水処理系統を経由する水に含まれる汚泥よりも粒子の大きな汚泥について、第2の汚泥処理系統を形成することで前記排水貯槽から取り出して処理することが可能になった。しかも、排水貯槽の点検タイミングで、点検対象の排水貯槽内に堆積した粒子の大きな汚泥を排出することができる。これに伴い、排水貯槽に沈殿堆積していた汚泥の処理費用の低減化が図られる。 As described above, according to the sludge treatment method of the present invention, it is possible to remove and treat sludge that is generated by washing certain equipment and has larger particles than the sludge contained in the water that passes from the wastewater tank through the wastewater treatment system by forming a second sludge treatment system. Furthermore, when the wastewater tank is inspected, the sludge with larger particles that has accumulated in the wastewater tank being inspected can be discharged. This reduces the cost of treating the sludge that has settled and accumulated in the wastewater tank.
特に請求項2に係る発明の汚泥の処理方法によれば、排水貯槽から取り出した、当該排水貯槽から排水処理系統に送られる水に含まれる汚泥よりも粒子の大きな汚泥を濃縮槽に沈殿させることが可能となり、濃縮槽に設けられたポンプや濃縮槽と脱水機とを接続する配管を利用して、前記汚泥を濃縮槽から脱水機に円滑に移送させることができる。 In particular, the sludge treatment method of the invention according to claim 2 makes it possible to settle in a thickening tank sludge that is larger in particle size than the sludge contained in the water sent from the wastewater storage tank to the wastewater treatment system, and the sludge can be smoothly transferred from the thickening tank to the dehydrator using a pump provided in the thickening tank and piping connecting the thickening tank and the dehydrator.
以下、本発明の実施形態を図面に基づいて説明する。 The following describes an embodiment of the present invention with reference to the drawings.
図1において、例えば火力発電所等の発電施設が有する排水処理施設1の一例が示されている。図1では、排水処理施設1の設備の全部ではなく、本発明に関連した設備が部分的に示されている。 In FIG. 1, an example of a wastewater treatment facility 1 is shown, which may be found in a power generation facility such as a thermal power plant. In FIG. 1, only a portion of the equipment related to the present invention is shown, rather than all of the equipment in the wastewater treatment facility 1.
排水処理施設1は、例えば排水ピット2から水等が送られるA排水貯槽3及びB排水貯槽4を有している。排水ピット2は、例えばボイラにおいて熱交換をする空気予熱器と呼ばれる熱交換器(図示せず)を水洗して生じた洗浄水等が送られるもので、更に、洗浄水は、この排水ピット2からA排水貯槽3及びB排水貯槽4のいずれか又は双方に送り込まれる。すなわち、熱交換器の洗浄水には、熱交換器内に目詰まり等して溜っていた灰や錆等が含まれるところ、図2(a)に示されるように、A排水貯槽3及びB排水貯槽4にて相対的に大きな粒子の汚泥Sとして沈殿堆積してきた。 The wastewater treatment facility 1 has, for example, an A wastewater storage tank 3 and a B wastewater storage tank 4 to which water, etc. is sent from a wastewater pit 2. The wastewater pit 2 is used to receive cleaning water, etc., generated when washing a heat exchanger (not shown) called an air preheater, which exchanges heat in a boiler, and the cleaning water is sent from the wastewater pit 2 to either or both of the A wastewater storage tank 3 and the B wastewater storage tank 4. In other words, the cleaning water for the heat exchanger contains ash, rust, etc. that has accumulated in the heat exchanger due to clogging, etc., and as shown in Figure 2(a), it has settled and accumulated as sludge S of relatively large particles in the A wastewater storage tank 3 and the B wastewater storage tank 4.
A排水貯槽3及びB排水貯槽4は、この実施例では、図2(a)でその一部が示されるように、上方が開放された排水貯槽であり、A排水貯槽3とB排水貯槽4とは、図示しないが例えば仕切り壁により2つに仕切られるかたちで並設されている。図1では、排水ピット2とA排水貯槽3、B排水貯槽4とを結ぶ配管に弁5、6、7が設けられているが、排水ピット2からA排水貯槽3とB排水貯槽4との一方或いは双方に水等を送ることがでれば、図1に示される弁の数や配置に限定されない。なお、図示しないが、A排水貯槽3及びB排水貯槽4とボイラ受水槽や排水槽ポンプ等とが適宜に配管接続されて、A排水貯槽3及びB排水貯槽4へ水等が送られてくると共にその配管の経路に弁が配置されている。 In this embodiment, the A drainage tank 3 and the B drainage tank 4 are drainage tanks with an open top, as shown in part in FIG. 2(a), and the A drainage tank 3 and the B drainage tank 4 are arranged side by side, separated into two by a partition wall (not shown). In FIG. 1, valves 5, 6, and 7 are provided on the piping connecting the drainage pit 2 and the A drainage tank 3 and the B drainage tank 4, but the number and arrangement of the valves shown in FIG. 1 are not limited as long as water, etc. can be sent from the drainage pit 2 to either or both of the A drainage tank 3 and the B drainage tank 4. Although not shown, the A drainage tank 3 and the B drainage tank 4 are appropriately connected to a boiler water tank, a drainage tank pump, etc., so that water, etc. is sent to the A drainage tank 3 and the B drainage tank 4, and valves are provided on the piping route.
A排水貯槽3、B排水貯槽4に送られてきた水について排水処理するための排水処理系統L1を構成する設備として、排水処理施設1は、この実施例では、PH調整槽10、凝集槽11、沈殿槽12、中間水槽13、及びろ過機14を有している。これらのPH調整槽10、凝集槽11、沈殿槽12、中間水槽13、及びろ過機14は、排水処理系統L1の一部である。 In this embodiment, the wastewater treatment facility 1 includes a pH adjustment tank 10, a flocculation tank 11, a sedimentation tank 12, an intermediate water tank 13, and a filter 14 as equipment constituting the wastewater treatment system L1 for treating the water sent to the A wastewater storage tank 3 and the B wastewater storage tank 4. The pH adjustment tank 10, the flocculation tank 11, the sedimentation tank 12, the intermediate water tank 13, and the filter 14 are part of the wastewater treatment system L1.
相対的に粒子の小さな汚泥を含む水は、A排水貯槽3、B排水貯槽4からポンプ8、9によりPH調整槽10に送られ、PH調整槽10で薬剤投入により水のPH調整が行われた後、凝集槽11で薬剤の投入によりフロックが形成される。更に、凝集槽で処理がされた水は、沈殿槽12に送られて、相対的に粒子の小さな汚泥であっても、沈殿槽12の下部に沈殿堆積することとなる。沈殿槽12で汚泥と分離された上済みの水は、中間水槽13に送られた後、更に、ポンプ15によりろ過機14に送られ、ろ過機14で異物の除去がなされて、ポンプ16により排水処理系統L1を構成する図示しない設備へと送られる。この実施例では、配管のポンプ8とPH調整槽10との間の経路に弁17が配置され、配管のポンプ9とPH調整槽10との間の経路に弁18が配置されると共に、配管のポンプ16に対してろ過機14側となる経路に弁19が配置され、配管のポンプ16に対してろ過機14とは反対側となる経路に弁20が配置されている。 Water containing sludge with relatively small particles is sent from the A wastewater storage tank 3 and the B wastewater storage tank 4 by pumps 8 and 9 to the pH adjustment tank 10, where the pH of the water is adjusted by adding chemicals, and then flocs are formed in the coagulation tank 11 by adding chemicals. The water treated in the coagulation tank is then sent to the settling tank 12, where even the sludge with relatively small particles settles and accumulates at the bottom of the settling tank 12. The topside water separated from the sludge in the settling tank 12 is sent to the intermediate water tank 13, and then further sent to the filter 14 by pump 15, where foreign matter is removed, and then sent to the equipment (not shown) that constitutes the wastewater treatment system L1 by pump 16. In this embodiment, valve 17 is placed in the path between pump 8 and pH adjustment tank 10, valve 18 is placed in the path between pump 9 and pH adjustment tank 10, valve 19 is placed in the path on the filter 14 side of pump 16, and valve 20 is placed in the path on the opposite side of pump 16 from filter 14.
沈殿槽12で水と分離された汚泥を処理するための通常の、第1の汚泥処理系統L2を構成する設備として、排水処理施設1は、この実施例では、濃縮槽21、凝集剤溶解液槽22及び脱水機23を有している。濃縮槽21は、沈殿槽12の下部からポンプ24により送られた汚泥を濃縮させるためのもので、図2(b)でその一部が示されるように、上方が開放された槽となっている。汚泥は、ポンプ24と濃縮槽21とを結ぶ配管内を通る際に、凝集剤溶解液槽22からポンプ25で送られてきた凝集剤が投入されて、濃縮槽21に送られる。そして、汚泥は、濃縮槽21の下部からポンプ26で脱水機23に送られて、脱水機23で所定の水分まで脱水されてケーキとなった後、ベルトコンベア27、28でケーキホッパ29、30まで送られ、産業廃棄物として排水処理施設1の外に運搬される。脱水機23は、遠心分離式のものと2つのベルトで挟んで水を抜くベルト式のものとがある。脱水機23は、遠心分離式では粒子の大きな汚泥での目詰まりが考えられるので、ベルト式の方がより好ましい。 In this embodiment, the wastewater treatment facility 1 has a thickening tank 21, a flocculant solution tank 22, and a dehydrator 23 as equipment constituting the first sludge treatment system L2, which is a normal equipment for treating sludge separated from water in the sedimentation tank 12. The thickening tank 21 is for thickening the sludge sent by the pump 24 from the bottom of the sedimentation tank 12, and is a tank with an open top, as shown in FIG. 2(b). When the sludge passes through the piping connecting the pump 24 and the thickening tank 21, the flocculant sent by the pump 25 from the flocculant solution tank 22 is added and the sludge is sent to the thickening tank 21. The sludge is then sent from the bottom of the thickening tank 21 to the dehydrator 23 by the pump 26, where it is dehydrated to a predetermined moisture content to become a cake, and then sent to the cake hopper 29, 30 by the belt conveyors 27, 28, and transported outside the wastewater treatment facility 1 as industrial waste. There are two types of dehydrators 23: a centrifugal type and a belt type that squeezes the sludge between two belts to extract water. The belt type is more preferable because the centrifugal type may become clogged with large sludge particles.
この実施例では、配管のポンプ24に対して沈殿槽12側となる経路に弁31が配置され、配管のポンプ24に対して濃縮槽21側となる経路に弁32が配置され、また、配管のポンプ25に対して凝集剤溶解液槽22側となる経路に弁33が配置され、配管のポンプ25に対して凝集剤溶解液槽22とは反対側となる経路に弁34が配置され、更に、配管のポンプ26に対して濃縮槽21側となる経路に弁35が配置され、配管のポンプ26に対して脱水機23側となる経路に弁36が配置されている。 In this embodiment, valve 31 is arranged in the path on the sedimentation tank 12 side of the piping relative to pump 24, valve 32 is arranged in the path on the concentration tank 21 side of the piping relative to pump 24, valve 33 is arranged in the path on the coagulant dissolution tank 22 side of the piping relative to pump 25, valve 34 is arranged in the path on the opposite side of the coagulant dissolution tank 22 relative to pump 25, valve 35 is arranged in the path on the concentration tank 21 side of the piping relative to pump 26, and valve 36 is arranged in the path on the dehydrator 23 side of pump 26.
本発明では、排水処理施設1は、排水処理系統L1を経由しないで汚泥を処理する第2の汚泥処理系統L3を有している。第2の汚泥処理系統L3は、A排水貯槽3、B排水貯槽4から排水処理系統L1を経由する水に含まれる汚泥よりも粒子の大きな汚泥Sの処理に対応したものである。 In the present invention, the wastewater treatment facility 1 has a second sludge treatment system L3 that treats sludge without passing through the wastewater treatment system L1. The second sludge treatment system L3 is designed to treat sludge S that has larger particles than the sludge contained in the water that passes through the wastewater treatment system L1 from the A wastewater storage tank 3 and the B wastewater storage tank 4.
より具体的には、第2の汚泥処理系統L3は、A排水貯槽3、B排水貯槽4に沈殿堆積した汚泥Sを、当該A排水貯槽3、B排水貯槽4から取り出す工程と、取り出された汚泥Sを、排水処理系統L1のうちのA排水貯槽3、B排水貯槽4から沈殿槽12までを経由しないで、第1の汚水処理系統L2を構成する濃縮槽21に直接に送る工程とを有する汚泥処理の方法となっている。濃縮槽21に送られた汚泥Sは、第1の汚泥処理系統L2と同様に、濃縮槽21から脱水機23に延びる配管を通るときに、凝集剤溶解液槽22からポンプ25で送られてきた凝集剤が投入される工程も有することから、脱水機23に送られてケーキ化され、その後の産業廃棄物としての処理が可能となる。 More specifically, the second sludge treatment system L3 is a sludge treatment method that includes a process of removing the sludge S that has settled and accumulated in the A wastewater storage tank 3 and the B wastewater storage tank 4 from the A wastewater storage tank 3 and the B wastewater storage tank 4, and a process of sending the removed sludge S directly to the thickening tank 21 that constitutes the first sewage treatment system L2, without passing through the A wastewater storage tank 3 and the B wastewater storage tank 4 to the settling tank 12 of the wastewater treatment system L1. As with the first sludge treatment system L2, the sludge S sent to the thickening tank 21 also includes a process in which a flocculant sent by a pump 25 from the flocculant dissolving liquid tank 22 is added when passing through a pipe extending from the thickening tank 21 to the dehydrator 23, so that the sludge S is sent to the dehydrator 23 and turned into a cake, and can then be treated as industrial waste.
汚泥Sは排水処理系統L1を経由する汚泥よりも粒子が大きく重いため自然に沈殿するので、沈殿可能な状態にするための工程を必要としないことから、汚泥Sについて沈殿槽12を経由しないでも、濃縮槽21以後の汚泥処理を行うことが可能である。 The particles of sludge S are larger and heavier than those of the sludge that passes through the wastewater treatment system L1, so it settles naturally. Therefore, no process is required to make the sludge settleable. Therefore, it is possible to carry out sludge treatment after the thickening tank 21 without passing the sludge S through the settling tank 12.
そして、図1に一例として示される排水処理施設1は、汚泥SをA排水貯槽3、B排水貯槽4から取り出す工程として、例えば図2(a)に示されるように、プロベスターと呼ばれる吸入/吐出装置101を有する車両100が用いられる。車両100は、吸入/吐出装置101から延びるホース102の先端部103をA排水貯槽3、B排水貯槽4の汚泥Sまで到達した状態で、吸入/吐出装置101を稼働させて、汚泥Sを吸入/吐出装置101に取り込む。これにより、汚泥SがA排水貯槽3、B排水貯槽4から取り出される。汚泥Sを吸入/吐出装置101に取り込んだ車両100は、図1の太い破線に示されるように、A排水貯槽3、B排水貯槽4から濃縮槽21まで移動した後、例えば図2(b)に示されるように、吸入/吐出装置101から延びるホース102の先端部103を濃縮槽21内に入れて、汚泥Sを濃縮槽21に上方から送り出す。汚泥Sは上述したように粒子が大きく重いので、そのまま濃縮槽21の下方に沈殿していく。このような第2の排水処理系統L3としたことにより、第1の排水処理施設の濃縮槽21や脱水機23を用い、更に凝集剤溶解液槽22から凝集剤を注入する経路も既存のものを用いることが可能である。しかも、しかも、A排水貯槽3、B排水貯槽4の定期点検等の点検タイミングで、点検対象の排水貯槽3、4内に堆積した粒子の大きな汚泥を排出することができる。よって、第2の排水処理系統L3を採用することに伴う費用を抑制することが可能である。 In the wastewater treatment facility 1 shown as an example in Figure 1, a vehicle 100 having a suction/discharge device 101 called a prober is used in the process of removing sludge S from the A wastewater storage tank 3 and the B wastewater storage tank 4, as shown in Figure 2(a), for example. When the tip 103 of a hose 102 extending from the suction/discharge device 101 reaches the sludge S in the A wastewater storage tank 3 and the B wastewater storage tank 4, the vehicle 100 operates the suction/discharge device 101 to take in the sludge S into the suction/discharge device 101. As a result, the sludge S is removed from the A wastewater storage tank 3 and the B wastewater storage tank 4. The vehicle 100 that has taken in the sludge S into the suction/discharge device 101 moves from the A wastewater storage tank 3 and the B wastewater storage tank 4 to the concentration tank 21 as shown by the thick dashed line in FIG. 1, and then, for example, as shown in FIG. 2(b), the tip 103 of the hose 102 extending from the suction/discharge device 101 is inserted into the concentration tank 21 to send the sludge S to the concentration tank 21 from above. As described above, the sludge S is large and heavy, so it settles directly to the bottom of the concentration tank 21. By using such a second wastewater treatment system L3, it is possible to use the concentration tank 21 and the dehydrator 23 of the first wastewater treatment facility, and further to use the existing route for injecting the coagulant from the coagulant dissolving liquid tank 22. Moreover, at the timing of inspection such as regular inspection of the A wastewater storage tank 3 and the B wastewater storage tank 4, it is possible to discharge the sludge with large particles that has accumulated in the wastewater storage tanks 3 and 4 to be inspected. Therefore, it is possible to reduce the cost associated with adopting the second wastewater treatment system L3.
図3において、図1に示された第2の排水系統L3とは異なる態様の第2の排水系統L3を用いた態様が示されている。図3に示される第2の排水系統L3は、例えば排水処理施設1自体を新設する場合に好適なものであり、また、汚泥Sの直接の送り先を、濃縮槽21を経由しないかたちで脱水機23にしたものとなっている。 Figure 3 shows an embodiment using a second drainage system L3 that is different from the second drainage system L3 shown in Figure 1. The second drainage system L3 shown in Figure 3 is suitable, for example, when the wastewater treatment facility 1 itself is newly constructed, and the sludge S is sent directly to the dehydrator 23 without passing through the thickening tank 21.
図3の第2の排水処理系統L3では、A排水貯槽3、B排水貯槽4に沈殿堆積した汚泥Sを、A排水貯槽3、B排水貯槽4から取り出す工程として、ポンプ41、42でA排水貯槽3、B排水貯槽4から吸い上げる工程が用いられている。ポンプ41、42は、例えば排水貯槽3、4内に設置された水中ポンプであっても、排水貯槽3、4の周囲を囲むようにレールを敷設して、このレール上を移動可能なポンプ車であっても良い。 In the second wastewater treatment system L3 in FIG. 3, the sludge S that has settled and accumulated in the A wastewater storage tank 3 and the B wastewater storage tank 4 is removed from the A wastewater storage tank 3 and the B wastewater storage tank 4 by a process of sucking it up from the A wastewater storage tank 3 and the B wastewater storage tank 4 using pumps 41 and 42. The pumps 41 and 42 may be, for example, submersible pumps installed in the wastewater storage tanks 3 and 4, or pump vehicles that can move on rails laid around the periphery of the wastewater storage tanks 3 and 4.
ポンプ41、42は、この実施例では、配管により脱水機23と接続されているので、ポンプ41、42でA排水貯槽3、B排水貯槽4から取り出された汚泥Sが、配管を通って脱水機23まで送られるという工程が行われる。そして、ポンプ41、42と脱水機23との間で凝集剤溶解液槽22からポンプ43により送られてきた凝集剤が汚泥Sに注入される。これにより、図3の排水処理系統L3でも、汚泥Sは凝集剤が注入された状態で脱水機23に送られるので、脱水機23で適宜にケーキ化され、産業廃棄物として外部に搬出される。 In this embodiment, the pumps 41 and 42 are connected to the dehydrator 23 by piping, so that the sludge S removed from the A wastewater storage tank 3 and the B wastewater storage tank 4 by the pumps 41 and 42 is sent to the dehydrator 23 through the piping. Then, between the pumps 41 and 42 and the dehydrator 23, the flocculant sent by the pump 43 from the flocculant dissolving liquid tank 22 is injected into the sludge S. As a result, in the wastewater treatment system L3 in FIG. 3, the sludge S is sent to the dehydrator 23 with the flocculant injected, so that the sludge S is appropriately caked in the dehydrator 23 and transported to the outside as industrial waste.
この実施例では、配管のポンプ41と脱水機23との間の経路に弁44が配置され、配管のポンプ42と脱水機23との間の経路に弁45が配置されると共に、配管のポンプ43に対して凝集剤溶解液槽22側となる経路に弁46が配置され、配管のポンプ43に対して凝集剤溶解液槽22とは反対側となる経路に弁47が配置されている。 In this embodiment, a valve 44 is arranged in the path between the pump 41 of the piping and the dehydrator 23, a valve 45 is arranged in the path between the pump 42 of the piping and the dehydrator 23, a valve 46 is arranged in the path on the side of the flocculant dissolving liquid tank 22 relative to the pump 43 of the piping, and a valve 47 is arranged in the path on the opposite side of the flocculant dissolving liquid tank 22 relative to the pump 43 of the piping.
なお、図1に示される排水処理施設1においても、図示しないが、ポンプ41、42を設け、且つ、A排水貯槽3、B排水貯槽4から取り出された汚泥Sを濃縮槽21まで送るための配管を設け、配管の開口部から濃縮槽21内に汚泥が送り込まれるようにしても良い。 In addition, even in the wastewater treatment facility 1 shown in FIG. 1, pumps 41 and 42 (not shown) may be provided, and piping may be provided to transport the sludge S removed from the A wastewater storage tank 3 and the B wastewater storage tank 4 to the concentration tank 21, so that the sludge is sent into the concentration tank 21 from the opening of the piping.
1 排水処理施設
3 A排水貯槽
4 B排水貯槽
12 沈殿槽
21 濃縮槽
23 脱水機
L1 排水処理系統
L2 第1の汚泥処理系統
L3 第2の汚泥処理系統
S 汚泥
1 Wastewater treatment facility 3 A wastewater storage tank 4 B wastewater storage tank 12 Settling tank 21 Thickening tank 23 Dehydrator L1 Wastewater treatment system L2 First sludge treatment system L3 Second sludge treatment system S Sludge
Claims (2)
前記排水処理系統は、当該排水処理系統を構成する設備として、前記排水貯槽から送られてきた水に含まれる汚泥を沈殿させる沈殿槽を有し、
前記第1の汚泥処理系統は、当該第1の汚泥処理系統を構成する設備として、前記汚泥を所定の水分濃度まで脱水してケーキにする脱水機を有する排水処理施設で用いられる汚泥の処理方法であって、
前記排水貯槽から前記排水処理系統を経由する水に含まれる汚泥よりも粒子の大きな汚泥を、前記排水貯槽から取り出す工程と、前記汚泥を、前記排水処理系統のうちの前記排水貯槽から前記沈殿槽までを経由せずに、前記汚泥に凝集剤を注入した状態で前記脱水機に送る工程とを有する第2の汚泥処理系統を形成したことを特徴とする汚泥の処理方法。 a wastewater storage tank to which water generated by washing a predetermined appliance is sent, a wastewater treatment system that treats the water sent to the wastewater storage tank, and a first sludge treatment system that treats sludge contained in the water that has passed from the wastewater storage tank through the wastewater treatment system;
The wastewater treatment system includes a settling tank for settling sludge contained in the water sent from the wastewater storage tank as a component of the wastewater treatment system,
The first sludge treatment system is a sludge treatment method used in a wastewater treatment facility having a dehydrator that dehydrates the sludge to a predetermined moisture concentration to form a cake as equipment constituting the first sludge treatment system,
A sludge treatment method characterized by forming a second sludge treatment system, the method comprising the steps of: removing sludge from the wastewater storage tank, the sludge having larger particles than the sludge contained in the water passing through the wastewater treatment system from the wastewater storage tank; and sending the sludge to the dehydrator after injecting a coagulant into the sludge, without passing through the wastewater treatment system from the wastewater storage tank to the settling tank.
前記第2の汚泥処理系統として、前記排水貯槽から前記排水処理系統を経由する水に含まれる汚泥よりも粒子の大きな汚泥を、前記排水貯槽から取り出して前記濃縮槽に直接に送る工程と、前記汚泥が前記濃縮槽から前記脱水機に送られる間に前記汚泥に前記凝集剤を注入する工程とを有することを特徴とする請求項1に記載の汚泥の処理方法。
The wastewater treatment facility further includes a thickening tank to which sludge before being dewatered by the dehydrator is sent as equipment constituting the first sludge treatment system,
The sludge treatment method according to claim 1, characterized in that the second sludge treatment system includes a step of removing sludge having larger particles than the sludge contained in the water passing through the wastewater treatment system from the wastewater storage tank and sending it directly to the thickening tank, and a step of injecting the coagulant into the sludge while the sludge is being sent from the thickening tank to the dewatering machine.
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| JP2003010860A (en) | 2001-07-03 | 2003-01-14 | Ebara Engineering Service Co Ltd | Incinerator demolition cleaning wastewater treatment equipment |
| JP2019093354A (en) | 2017-11-24 | 2019-06-20 | 月島機械株式会社 | Sludge concentration equipment and sludge concentration method |
| JP2020114569A (en) | 2019-01-17 | 2020-07-30 | 三機工業株式会社 | Water content estimation method of dehydrated cake, and sludge treatment system |
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| JPS58143897A (en) * | 1982-02-17 | 1983-08-26 | Ebara Infilco Co Ltd | Dehydration of sludge |
| JPH03275200A (en) * | 1990-03-26 | 1991-12-05 | Kurita Water Ind Ltd | Organic sludge concentration and dehydration method |
| JPH05111698A (en) * | 1991-10-23 | 1993-05-07 | Satake Eng Co Ltd | Rice washing waste water disposal equipment |
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| JP2003010860A (en) | 2001-07-03 | 2003-01-14 | Ebara Engineering Service Co Ltd | Incinerator demolition cleaning wastewater treatment equipment |
| JP2019093354A (en) | 2017-11-24 | 2019-06-20 | 月島機械株式会社 | Sludge concentration equipment and sludge concentration method |
| JP2020114569A (en) | 2019-01-17 | 2020-07-30 | 三機工業株式会社 | Water content estimation method of dehydrated cake, and sludge treatment system |
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