JP7441078B2 - Sewage treatment system and method - Google Patents

Sewage treatment system and method Download PDF

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JP7441078B2
JP7441078B2 JP2020037167A JP2020037167A JP7441078B2 JP 7441078 B2 JP7441078 B2 JP 7441078B2 JP 2020037167 A JP2020037167 A JP 2020037167A JP 2020037167 A JP2020037167 A JP 2020037167A JP 7441078 B2 JP7441078 B2 JP 7441078B2
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俊貴 福嶋
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Metawater Co Ltd
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本発明は、下水処理システムおよび下水処理方法に関するものである。 The present invention relates to a sewage treatment system and a sewage treatment method.

近年、下水処理場では、下水処理水の放流先の水域で行われる養殖業等に配慮し、冬季に下水処理水中の栄養塩類(窒素やリン)濃度を上げることで、冬季に不足しがちな窒素やリンを放流先水域に供給するなど、地域のニーズに応じ季節毎に水質を能動的に管理する季節別運転管理の取組が行われている(例えば、非特許文献1参照)。 In recent years, sewage treatment plants have increased the concentration of nutrients (nitrogen and phosphorus) in sewage treatment water during the winter, taking into consideration the aquaculture and other activities that take place in the water areas where treated sewage water is discharged. Efforts are being made to actively manage water quality seasonally according to local needs, such as by supplying nitrogen and phosphorus to water bodies into which water is discharged (for example, see Non-Patent Document 1).

そして、季節別運転管理を行う下水処理場における放流水の水質の能動的な管理は、下水道法等の法令・条例で定められた範囲内で、例えば反応槽における生物処理の条件を調整することにより行っている(例えば、特許文献1参照)。 Active management of the water quality of effluent at a sewage treatment plant that performs seasonal operation management includes, for example, adjusting the biological treatment conditions in reaction tanks within the scope stipulated by laws and ordinances such as the Sewerage Act. (For example, see Patent Document 1).

特開2019-141763号公報JP 2019-141763 Publication

国土交通省水管理・国土保全局下水道部編、「下水放流水に含まれる栄養塩類の能動的管理のための運転方法に係る手順書(案)」、平成27年9月Ministry of Land, Infrastructure, Transport and Tourism, Water Management and Land Conservation Bureau, Sewage Department, “Procedures (Draft) for Operational Methods for Active Management of Nutrients Contained in Sewage Discharge Water,” September 2015.

しかし、生物処理の条件を調整することにより放流水の水質の能動的管理を行う上記従来の技術には、生物処理に用いられる微生物の性状を適切に調節することが難しく、放流水の水質を所望のレベルに制御し難いという点において改善の余地があった。 However, with the above-mentioned conventional technology that actively manages the quality of effluent by adjusting the conditions of biological treatment, it is difficult to appropriately control the properties of the microorganisms used in biological treatment, and the quality of effluent cannot be controlled. There was room for improvement in that it was difficult to control to a desired level.

また、近年、下水処理場には、積極的にエネルギーを創出するエネルギー供給拠点として機能することも期待されているところ、季節別運転管理を行う下水処理場においても同様に、エネルギー供給機能を発揮することが望まれていた。 In addition, in recent years, sewage treatment plants are expected to function as energy supply bases that actively create energy, and sewage treatment plants that perform seasonal operation management can also perform the same energy supply function. It was desired to do so.

そこで、本発明は、放流水の水質の能動的管理を容易に行うことができ、且つ、エネルギーの創出も可能にする下水処理システムおよび下水処理方法を提供することを目的とする。 SUMMARY OF THE INVENTION Therefore, an object of the present invention is to provide a sewage treatment system and a sewage treatment method that make it easy to actively manage the quality of effluent water and also make it possible to generate energy.

この発明は、上記課題を有利に解決することを目的とするものであり、本発明の下水処理システムは、下水を処理し、栄養塩類を含む下水処理水を排出する下水処理設備と、前記下水処理設備から流出した前記下水処理水を放流先へと放流する第一放流路と、水生植物を用いて前記下水処理水中の栄養塩類を回収する栄養塩類回収設備を有し、前記下水処理水から栄養塩類を回収してなる処理水を前記放流先へと放流する第二放流路と、前記下水処理設備から前記第一放流路へと流入する下水処理水量および前記下水処理設備から前記第二放流路へと流入する下水処理水量を調節する流量調節機構と、前記栄養塩類回収設備から前記水生植物を回収し、回収した水生植物を原料として用いて発電を行う発電設備とを備えることを特徴とする。このように、第一放流路と、水生植物を用いた栄養塩類回収設備を有する第二放流路と、流量調節機構とを設ければ、放流水の水質の能動的管理を容易に行うことができる。また、水生植物を原料として用いて発電を行う発電設備を設ければ、放流水中の栄養塩類の能動的管理と、エネルギーの創出とを達成することができる。 The purpose of the present invention is to advantageously solve the above problems, and the sewage treatment system of the present invention includes: a sewage treatment facility that processes sewage and discharges treated sewage water containing nutrients; A first discharge channel for discharging the treated sewage water flowing out from the treatment equipment to a destination, and a nutrient salt recovery facility for recovering nutrients in the treated sewage water using aquatic plants, a second discharge channel for discharging treated water obtained by recovering nutrients to the discharge destination; an amount of treated sewage water flowing from the sewage treatment equipment into the first discharge route; and a second discharge from the sewage treatment equipment. The system is characterized by comprising a flow rate adjustment mechanism that adjusts the amount of treated sewage water flowing into the road, and a power generation facility that collects the aquatic plants from the nutrient salt recovery facility and generates electricity using the collected aquatic plants as a raw material. do. In this way, by providing the first discharge channel, the second discharge channel having a nutrient recovery facility using aquatic plants, and the flow rate adjustment mechanism, active management of the water quality of the discharge water can be easily carried out. can. Furthermore, by installing a power generation facility that generates power using aquatic plants as raw materials, it is possible to actively manage nutrients in effluent water and generate energy.

ここで、本発明の下水処理システムは、前記流量調節機構が、前記第一放流路へと流入する下水処理水量および前記第二放流路へと流入する下水処理水量を時季に応じて制御する制御装置を備えることが好ましい。このような制御装置を設ければ、季節別運転管理を適切に行うことができる。 Here, in the sewage treatment system of the present invention, the flow rate adjustment mechanism controls the amount of treated sewage water flowing into the first discharge channel and the amount of treated sewage water flowing into the second discharge channel according to the season. Preferably, a device is provided. If such a control device is provided, seasonal operation management can be appropriately performed.

また、本発明の下水処理システムは、前記流量調節機構が、前記第一放流路へと流入する下水処理水量および前記第二放流路へと流入する下水処理水量を、前記放流先で要求される栄養塩類の量に基づいて制御する制御装置を備えることが好ましい。このような制御装置を設ければ、放流先で要求される栄養塩類の量に応じて放流水の水質の能動的管理を適切に行うことができる。 Further, in the sewage treatment system of the present invention, the flow rate adjustment mechanism adjusts the amount of treated sewage water flowing into the first discharge channel and the amount of treated sewage water flowing into the second discharge channel as required at the discharge destination. It is preferable to include a control device that controls based on the amount of nutrient salts. If such a control device is provided, the quality of the discharged water can be appropriately managed actively according to the amount of nutrients required at the discharge destination.

そして、本発明の下水処理システムでは、前記制御装置が、前記放流先への栄養塩類の年間排出量が所定値以下になるように前記第一放流路へと流入する下水処理水量および前記第二放流路へと流入する下水処理水量を制御することが好ましい。このような制御装置を設ければ、下水道法等の法令・条例を適切に遵守することができる。 In the sewage treatment system of the present invention, the control device controls the amount of treated sewage water flowing into the first discharge channel and the second It is preferable to control the amount of treated sewage water flowing into the outlet. If such a control device is provided, laws and ordinances such as the Sewerage Law can be properly complied with.

また、本発明の下水処理システムは、前記栄養塩類回収設備が、前記処理水中の栄養塩類の量が目標値に近づくように前記水生植物の量を調節する制御装置を備えることが好ましい。このような制御装置を設ければ、放流水の水質の能動的管理と、水生植物を用いたエネルギーの創出とを高いレベルで両立することができる。 Further, in the sewage treatment system of the present invention, it is preferable that the nutrient salt recovery equipment includes a control device that adjusts the amount of the aquatic plants so that the amount of nutrient salts in the treated water approaches a target value. If such a control device is provided, it is possible to achieve a high level of both active management of the quality of discharged water and generation of energy using aquatic plants.

また、この発明は、上記課題を有利に解決することを目的とするものであり、本発明の下水処理方法は、下水を処理し、栄養塩類を含む下水処理水を得る下水処理工程と、前記下水処理工程で得られた前記下水処理水について、そのまま、および/または、水生植物を用いて栄養塩類を回収した後に放流先へと放流する放流工程と、前記放流工程において、そのまま放流する下水処理水の量と、栄養塩類を回収した後に放流する下水処理水の量とを決定する分配工程と、前記水生植物を回収し、回収した水生植物を原料として用いて発電を行う発電工程とを含むことを特徴とする。このように、放流工程および分配工程を実施すれば、放流水の水質の能動的管理を容易に行うことができる。また、水生植物を原料として用いて発電を行う発電工程を実施すれば、放流水中の栄養塩類の能動的管理と、エネルギーの創出とを達成することができる。 Further, the present invention aims to advantageously solve the above problems, and the sewage treatment method of the present invention includes a sewage treatment step of treating sewage to obtain treated sewage water containing nutrients; A discharge step in which the treated sewage water obtained in the sewage treatment step is discharged as it is and/or after recovering nutrients using aquatic plants to a destination; and a sewage treatment in which the treated sewage water is discharged as it is in the discharge step. The method includes a distribution step of determining the amount of water and the amount of treated sewage water to be discharged after collecting nutrients, and a power generation step of collecting the aquatic plants and generating power using the collected aquatic plants as a raw material. It is characterized by By performing the discharge process and the distribution process in this way, the quality of the discharged water can be easily managed actively. Furthermore, by implementing a power generation process that uses aquatic plants as raw materials to generate electricity, active management of nutrients in the effluent and generation of energy can be achieved.

ここで、本発明の下水処理方法において、前記分配工程では、そのまま放流する下水処理水の量と、栄養塩類を回収した後に放流する下水処理水の量とを、時季に応じて決定することが好ましい。そのまま放流する下水処理水の量と、栄養塩類を回収した後に放流する下水処理水の量とを時季に応じて決定すれば、季節別運転管理を適切に行うことができる。 Here, in the sewage treatment method of the present invention, in the distribution step, the amount of treated sewage water to be discharged as is and the amount of treated sewage water to be discharged after recovering nutrients may be determined depending on the season. preferable. If the amount of treated sewage water to be discharged as is and the amount of treated sewage water to be discharged after recovering nutrients are determined according to the season, seasonal operation management can be performed appropriately.

また、本発明の下水処理方法において、前記分配工程では、そのまま放流する下水処理水の量と、栄養塩類を回収した後に放流する下水処理水の量とを、前記放流先で要求される栄養塩類の量に基づいて決定することが好ましい。このようにすれば、放流先で要求される栄養塩類の量に応じて放流水の水質の能動的管理を適切に行うことができる。 Further, in the sewage treatment method of the present invention, in the distribution step, the amount of treated sewage water to be discharged as is and the amount of treated sewage water to be discharged after recovering nutrients are adjusted to meet the requirements of the nutrient salts at the discharge destination. Preferably, the determination is based on the amount of In this way, the quality of the discharged water can be appropriately managed in accordance with the amount of nutrients required at the discharge destination.

更に、本発明の下水処理方法は、前記分配工程では、そのまま放流する下水処理水の量と、栄養塩類を回収した後に放流する下水処理水の量とを、前記放流先への栄養塩類の年間排出量が所定値以下になるように決定することが好ましい。放流先への栄養塩類の年間排出量が所定値以下になるようにすれば、下水道法等の法令・条例を適切に遵守することができる。 Furthermore, in the sewage treatment method of the present invention, in the distribution step, the amount of treated sewage water to be discharged as is and the amount of treated sewage water to be discharged after recovering nutrients are determined based on the annual distribution of nutrients to the discharge destination. It is preferable to determine so that the discharge amount is equal to or less than a predetermined value. By keeping the annual amount of nutrient salts discharged to the destination below a predetermined value, laws and ordinances such as the Sewerage Act can be properly complied with.

そして、本発明の下水処理方法は、前記放流工程において前記水生植物を用いて前記下水処理水から栄養塩類を回収して得られる処理水中の栄養塩類の量が目標値に近づくように前記放流工程で用いる前記水生植物の量を調節する水生植物量調節工程を更に含むことが好ましい。処理水中の栄養塩類の量が目標値に近づくように水生植物の量を調節すれば、放流水中の栄養塩類の能動的管理と、水生植物を用いたエネルギーの創出とを達成することができる。 In the sewage treatment method of the present invention, the discharge step is such that the amount of nutrients in the treated water obtained by recovering nutrients from the treated sewage water using the aquatic plants in the discharge step approaches a target value. Preferably, the method further includes a step of adjusting the amount of aquatic plants used in the method. By adjusting the amount of aquatic plants so that the amount of nutrients in the treated water approaches the target value, active management of nutrients in the effluent and generation of energy using aquatic plants can be achieved.

本発明の下水処理システムおよび下水処理方法によれば、放流水中の栄養塩類の能動的管理を容易に行うことができると共に、エネルギーの創出も可能になる。 According to the sewage treatment system and sewage treatment method of the present invention, it is possible to easily actively manage nutrients in effluent water, and it is also possible to generate energy.

下水処理システムの一例の概略構成を示す説明図である。FIG. 1 is an explanatory diagram showing a schematic configuration of an example of a sewage treatment system.

以下、本発明の実施の形態を、図面に基づき詳細に説明する。
ここで、本発明の下水処理システムおよび下水処理方法は、特に限定されることなく、例えば下水処理場において地域のニーズに応じて季節毎に放流水の水質を能動的に管理する季節別運転管理を行う際に好適に用いることができる。
Hereinafter, embodiments of the present invention will be described in detail based on the drawings.
Here, the sewage treatment system and sewage treatment method of the present invention are not particularly limited, and include, for example, seasonal operation management in which the quality of discharged water is actively managed seasonally according to local needs at a sewage treatment plant. It can be suitably used when carrying out.

(下水処理システム)
本発明の下水処理システムの一例は、概略構成を図1に示すように、下水を処理して下水処理水を排出する下水処理設備10と、下水処理設備10から流出した下水処理水を放流先へと放流する放流路21と、放流路21から分岐すると共に分岐位置よりも下流側(放流先側)で再び放流路21に合流するバイパス流路23と、バイパス流路23に設けられた栄養塩類回収設備30とを備えている。また、図1に示す下水処理システム100の放流路21およびバイパス流路23には、それぞれ、流路内を流れる下水処理水の流量の調節に使用し得る第一流量調節弁22および第二流量調節弁24が設けられている。更に、下水処理システム100は、栄養塩類回収設備30において栄養塩類の回収に用いられる水生植物を栄養塩類回収設備30へと供給する水生植物供給機構31と、栄養塩類回収設備30から余剰の水生植物を回収して発電を行う発電設備32と、第一流量調節弁22、第二流量調節弁24、水生植物供給機構31および発電設備32の動作を制御する制御装置40とを備えている。
(Sewage treatment system)
An example of the sewage treatment system of the present invention, as schematically shown in FIG. a bypass channel 23 that branches from the discharge channel 21 and joins the discharge channel 21 again on the downstream side (discharge destination side) of the branch position; It is equipped with salt recovery equipment 30. Moreover, the discharge path 21 and the bypass flow path 23 of the sewage treatment system 100 shown in FIG. A regulating valve 24 is provided. Furthermore, the sewage treatment system 100 includes an aquatic plant supply mechanism 31 that supplies aquatic plants used for recovering nutrients in the nutrient salt recovery facility 30 to the nutrient salt recovery facility 30, and an aquatic plant supply mechanism 31 that supplies aquatic plants used for recovering nutrients from the nutrient salt recovery facility 30. The control device 40 controls the operation of the first flow rate control valve 22, the second flow rate control valve 24, the aquatic plant supply mechanism 31, and the power generation facility 32.

下水処理設備10は、流入した下水を処理し、栄養塩類(窒素および/またはリン)を含む下水処理水を排出する。ここで、下水処理設備10としては、流入した下水を処理することが可能であれば特に限定されることなく、任意の構成の下水処理設備を用いることができる。具体的には、下水処理設備10としては、特に限定されることなく、例えば、最初沈殿池と、最初沈殿池の後段に設けられて流入水を生物処理する反応槽と、反応槽の後段に設けられた最終沈殿池とを備える下水処理設備などを用いることができる。なお、下水処理設備10での消費エネルギーをできるだけ少なくするようにする観点からは、下水処理設備10は、流入した下水を硝化抑制運転により処理するものであることが好ましい。 The sewage treatment facility 10 processes inflowing sewage and discharges treated sewage water containing nutrients (nitrogen and/or phosphorus). Here, the sewage treatment equipment 10 is not particularly limited as long as it is capable of treating inflowing sewage, and any configuration of sewage treatment equipment can be used. Specifically, the sewage treatment equipment 10 is not particularly limited, and includes, for example, a primary sedimentation tank, a reaction tank provided downstream of the primary sedimentation tank for biologically treating inflow water, and a downstream stage of the reaction tank. A sewage treatment facility with a final settling tank provided therein, etc. can be used. In addition, from the viewpoint of reducing the energy consumption in the sewage treatment equipment 10 as much as possible, it is preferable that the sewage treatment equipment 10 treats inflowing sewage by nitrification suppression operation.

なお、放流水の水質の能動的管理を可能にする観点から、下水処理設備10では、得られる下水処理水中に栄養塩類が残存するように下水を処理する。下水処理水100では、下水処理水中に栄養塩類を意図的に残存させることで、後述するようにして放流水の水質の能動的管理が可能になる。
ここで、下水処理水中の窒素濃度は、流入する下水の水質にもよるが、30mg-N/L以上40mg-N/L以下とすることができる。窒素濃度を上記下限値以上とすれば、下水処理水をそのまま放流することで放流先に栄養塩類を十分に供給することができる。また、窒素濃度を上記上限値以下とすれば、放流先への栄養塩類の供給が不要な場合に栄養塩類回収設備30で栄養塩類を十分に回収してから放流することができる。
In addition, from the viewpoint of enabling active management of the water quality of effluent water, the sewage treatment facility 10 treats the sewage so that nutrients remain in the obtained sewage treatment water. In the treated sewage water 100, by intentionally leaving nutrients in the treated sewage water, the quality of the discharged water can be actively managed as described below.
Here, the nitrogen concentration in the sewage treatment water can be set to 30 mg-N/L or more and 40 mg-N/L or less, although it depends on the quality of the inflowing sewage water. When the nitrogen concentration is equal to or higher than the above lower limit, nutrient salts can be sufficiently supplied to the discharge destination by discharging treated sewage water as it is. Moreover, if the nitrogen concentration is set to be below the above upper limit value, when it is not necessary to supply nutrients to the discharge destination, the nutrients can be sufficiently recovered by the nutrients recovery equipment 30 before being discharged.

第一流量調節弁22を有する放流路21は、下水処理設備10と、放流先とを直接接続する。即ち、図示例ではバイパス流路23が分岐する位置よりも下流側に設けられた第一流量調節弁22を開くことで、放流路21は、下水処理設備10から流出した下水処理水を放流先へと放流する第一放流路として機能させることができる。 The discharge path 21 having the first flow rate control valve 22 directly connects the sewage treatment equipment 10 and the discharge destination. That is, in the illustrated example, by opening the first flow rate control valve 22 provided downstream of the branching position of the bypass channel 23, the discharge channel 21 directs the treated sewage water flowing out from the sewage treatment equipment 10 to the discharge destination. It can be made to function as a first discharge path for discharging water to.

第二流量調節弁24および栄養塩類回収設備30を有するバイパス流路23では、第二流量調節弁24を開き、栄養塩類回収設備30へと下水処理水を流入させることで、下水処理水から栄養塩類を回収してなる処理水を得ることができる。即ち、図示例では、第二流量調節弁24を開くことで、放流路21のうちのバイパス流路23が分岐する位置よりも上流側およびバイパス流路23が合流する位置よりも下流側と、バイパス流路23とを、下水処理水から栄養塩類を回収してなる処理水を放流先へと放流する第二放流路として機能させることができる。 In the bypass channel 23 having the second flow rate control valve 24 and the nutrient recovery equipment 30, the second flow rate control valve 24 is opened and the treated sewage water is allowed to flow into the nutrient recovery equipment 30. Treated water can be obtained by recovering salts. That is, in the illustrated example, by opening the second flow rate control valve 24, the upstream side of the position where the bypass flow path 23 branches out of the discharge path 21 and the downstream side of the position where the bypass flow path 23 joins, The bypass channel 23 can be made to function as a second discharge channel for discharging treated water obtained by recovering nutrients from treated sewage water to a destination.

そして、下水処理システム100では、第一流量調節弁22および第二流量調節弁24が、放流先へとそのまま放流される下水処理水の量(即ち、第一放流路としての放流路21を流れる下水処理水量)と、栄養塩類を回収した後に放流先へと放流される下水処理水の量(即ち、放流路21の一部およびバイパス流路23からなる第二放流路を流れる下水処理水量)とを調節する流量調節機構として機能する。従って、下水処理システム100では、第一流量調節弁22および第二流量調節弁24の開度を調節し、栄養塩類を回収されてから放流される下水処理水の割合を変更することで、放流水中に含まれている栄養塩類の量を能動的に制御することができる。 In the sewage treatment system 100, the first flow rate control valve 22 and the second flow rate control valve 24 control the amount of treated sewage water that is discharged as it is to the discharge destination (i.e., the amount of treated sewage water that flows through the discharge channel 21 as the first discharge channel). The amount of treated sewage water that is discharged to the discharge destination after recovering nutrients (i.e., the amount of treated sewage water that flows through the second discharge channel consisting of a part of the discharge channel 21 and the bypass channel 23) It functions as a flow rate adjustment mechanism to adjust the flow rate. Therefore, in the sewage treatment system 100, by adjusting the opening degrees of the first flow rate control valve 22 and the second flow rate control valve 24 and changing the ratio of treated sewage water that is discharged after recovering nutrients, The amount of nutrients contained in water can be actively controlled.

なお、図1に示す例では、下水処理水を放流先にそのまま放流する第一放流路と、栄養塩類回収設備において下水処理水から栄養塩類を回収して得られる処理水を放流先に放流する第二放流路との一部が共通している場合を示したが、本発明の下水処理システムでは、第一放流路と第二放流路とが個別に設けられていてもよい。 In the example shown in Figure 1, there is a first discharge channel in which treated sewage water is directly discharged to the discharge destination, and a first discharge channel in which the nutrient salts are recovered from the treated sewage water in the nutrient recovery equipment and the treated water is discharged to the discharge destination. Although the case where a part is common with the second discharge channel has been shown, in the sewage treatment system of the present invention, the first discharge channel and the second discharge channel may be provided separately.

栄養塩類回収設備30は、水生植物を用いて下水処理水中の栄養塩類を回収し、栄養塩類が回収された処理水を排出する。ここで、水生植物としては、下水処理水中の栄養塩類を回収可能であれば特に限定されることなく、例えば、栄養塩類を取り込んで固定化可能なウキクサや微細藻類等を用いることができる。また、栄養塩類回収設備30としては、特に限定されることなく、ウキクサや微細藻類などの水生植物を培養可能な水槽などを用いることができる。 The nutrient salt recovery equipment 30 recovers nutrient salts from treated sewage water using aquatic plants, and discharges the treated water from which the nutrient salts have been recovered. Here, the aquatic plants are not particularly limited as long as they can recover nutrients from treated sewage water, and for example, duckweed, microalgae, etc. that can take in and immobilize nutrients can be used. Further, the nutrient salt recovery equipment 30 is not particularly limited, and an aquarium or the like in which aquatic plants such as duckweed and microalgae can be cultured can be used.

なお、栄養塩類回収設備30で栄養塩類を回収して得られる処理水中の窒素濃度は、流入する下水処理水の水質にもよるが、5mg-N/L以上15mg-N/L以下とすることができる。窒素濃度が上記範囲内であれば、栄養塩類回収設備30の適切な運転・管理により、放流先への栄養塩類の年間排出量を所定値以下になるように容易に調整することができる。 Note that the nitrogen concentration in the treated water obtained by recovering nutrients in the nutrient salt recovery equipment 30 should be 5 mg-N/L or more and 15 mg-N/L or less, although it depends on the quality of the inflowing sewage treated water. I can do it. If the nitrogen concentration is within the above range, by appropriately operating and managing the nutrient salt recovery equipment 30, the annual discharge amount of nutrient salts to the discharge destination can be easily adjusted to a predetermined value or less.

水生植物供給機構31は、特に限定されることなく、例えば、水生植物を貯蔵する貯蔵庫と、貯蔵庫から栄養塩類回収設備へと水生植物を搬送する搬送装置とを備えている。そして、水生植物供給機構31は、例えば、栄養塩類回収設備30において下水処理水を処理する際に用いられる水生植物の量が不足した際に、水生植物を栄養塩類回収設備30へと供給する。 The aquatic plant supply mechanism 31 is not particularly limited, and includes, for example, a storage for storing aquatic plants and a transport device for transporting the aquatic plants from the storage to the nutrient salt recovery facility. The aquatic plant supply mechanism 31 supplies aquatic plants to the nutrient salt recovery equipment 30, for example, when the amount of aquatic plants used when treating sewage water in the nutrient salt recovery equipment 30 is insufficient.

発電設備32としては、栄養塩類回収設備30から回収した水生植物を原料として用いて発電をすることが可能であれば特に限定されることなく、例えば、栄養塩類回収設備30から余剰の水生植物を回収する回収機構と、回収した水生植物を嫌気性消化して消化ガスを得る消化槽と、消化ガスを用いて発電を行う発電機とを備える発電設備を用いることができる。余剰の水生植物を原料として用いて発電を行えば、放流水中に含まれている栄養塩類の量の能動的管理を行いつつ、電気エネルギーを創出することができる。
なお、発電設備32では、水生植物に加えて、下水処理設備10から排出される初沈汚泥等を原料として用いて発電を行ってもよい。
The power generation equipment 32 is not particularly limited as long as it is possible to generate electricity using the aquatic plants collected from the nutrient salt recovery equipment 30 as raw materials, and for example, the power generation equipment 32 may be used to collect surplus aquatic plants from the nutrient salt recovery equipment 30. A power generation facility can be used that includes a collection mechanism for collection, a digestion tank for obtaining digested gas by anaerobically digesting the collected aquatic plants, and a generator for generating power using the digested gas. By using surplus aquatic plants as a raw material to generate electricity, electrical energy can be created while actively managing the amount of nutrients contained in the effluent.
In addition, in addition to aquatic plants, the power generation equipment 32 may use initial settling sludge discharged from the sewage treatment equipment 10 as a raw material to generate power.

制御装置40は、第一流量調節弁22、第二流量調節弁24、水生植物供給機構31および発電設備32の動作を制御する。具体的には、制御装置40は、流量調節機構としての第一流量調節弁22および第二流量調節弁24の開度を制御し、放流先へとそのまま放流される下水処理水と、栄養塩類を回収されてから放流される下水処理水との割合を変更することで、放流水中に含まれている栄養塩類の量を能動的に制御する。また、制御装置40は、水生植物供給機構31から供給される水生植物の量および発電設備32(特に、発電設備32の回収機構)により回収される水生植物の量を制御し、栄養塩類回収設備30において栄養塩類の回収に用いられる水生植物の量を調節することで、処理水中の栄養塩類の量を適切に管理する。 The control device 40 controls the operations of the first flow rate control valve 22, the second flow rate control valve 24, the aquatic plant supply mechanism 31, and the power generation equipment 32. Specifically, the control device 40 controls the opening degree of the first flow rate control valve 22 and the second flow rate control valve 24 as a flow rate control mechanism, and controls the amount of nutrient salts and treated sewage water that is directly discharged to the discharge destination. The amount of nutrients contained in the effluent can be actively controlled by changing the ratio of recovered sewage water to the treated sewage water that is discharged. The control device 40 also controls the amount of aquatic plants supplied from the aquatic plant supply mechanism 31 and the amount of aquatic plants collected by the power generation equipment 32 (in particular, the collection mechanism of the power generation equipment 32), and The amount of nutrient salts in the treated water is appropriately managed by adjusting the amount of aquatic plants used for recovering nutrient salts in step 30.

ここで、制御装置40における、そのまま放流される下水処理水と、栄養塩類を回収されてから放流される下水処理水の割合の決定は、時季に応じて行ってもよいし、放流先で要求される栄養塩類の量に基づいて行ってもよい。 Here, the control device 40 may determine the ratio of treated sewage water that is discharged as is and treated sewage water that is discharged after recovering nutrients, depending on the season, or may be determined at the discharge destination. This may be done based on the amount of nutrient salts used.

具体的には、例えば、制御装置40は、放流先において栄養塩類が不足しがちな冬季(1~3月)にはそのまま放流される下水処理水の量を増やし、夏季(7~9月)には栄養塩類を回収されてから放流される下水処理水の量を増やすように制御をおこなってもよい。このようにすれば、季節別運転管理を適切に行うことができる。 Specifically, for example, the control device 40 increases the amount of treated sewage water that is directly discharged during the winter (January to March) when nutrients tend to be insufficient at the discharge destination, and increases the amount of treated sewage water that is discharged as is during the summer (July to September). Control may be performed to increase the amount of treated sewage water that is discharged after nutrient salts have been recovered. In this way, seasonal operation management can be appropriately performed.

また、制御装置40は、放流先で要求される栄養塩類の量が多い場合にはそのまま放流される下水処理水の量を増やし、放流先で要求される栄養塩類の量が少ない場合には栄養塩類を回収されてから放流される下水処理水の量を増やすように制御をおこなってもよい。このようにすれば、放流先の水質に応じて栄養塩類の供給量の能動的管理を適切に行うことができる。
なお、放流先で要求される栄養塩類の量は、例えば、放流先の水域の栄養塩類の濃度を測定し、放流先の水域の栄養塩類の濃度の目標値と測定値との差を算出することにより決定することができる。
In addition, the control device 40 increases the amount of treated sewage water that is directly discharged when the amount of nutrients required at the discharge destination is large, and increases the amount of sewage treated water that is discharged as is when the amount of nutrients required at the discharge destination is small. Control may be performed to increase the amount of treated sewage water that is discharged after salts have been recovered. In this way, the amount of nutrients supplied can be appropriately managed in accordance with the quality of the water at the destination.
The amount of nutrients required at the destination is determined by, for example, measuring the concentration of nutrients in the destination water area and calculating the difference between the target value and the measured value of the nutrient concentration in the destination area. It can be determined by

更に、例えば放流先の水域に放出可能な栄養塩類の総量が下水道法等の法令・条例により規定されている場合などには、制御装置40は、放流先への栄養塩類の年間排出量が所定値以下になるように、そのまま放流される下水処理水の量と、栄養塩類を回収されてから放流される下水処理水の量との比率を制御してもよい。具体的には、制御装置40は、例えば、年間運転計画を立案すると共に、放流水中の栄養塩類の濃度および放流水の流量を測定して放流先への栄養塩類の供給量の積算値を算出しておき、冬季の供給量を十分確保すべく当該積算値が法令や条例の規制値を超えないように、あらかじめ夏季に供給量を抑制するものとすることができる。 Furthermore, for example, if the total amount of nutrient salts that can be discharged into the water area of the discharge destination is specified by laws and ordinances such as the Sewerage Act, the control device 40 can control the annual amount of nutrient salts that can be discharged to the discharge destination from a predetermined amount. The ratio between the amount of treated sewage water that is discharged as is and the amount of treated sewage water that is discharged after nutrient salts have been recovered may be controlled so as to be equal to or less than this value. Specifically, the control device 40, for example, creates an annual operation plan, measures the concentration of nutrients in the effluent and the flow rate of the effluent, and calculates the integrated value of the amount of nutrient salts supplied to the destination. Then, in order to ensure a sufficient supply amount in the winter, the supply amount can be suppressed in advance in the summer so that the integrated value does not exceed the regulated value of laws and ordinances.

また、制御装置40を用いた水生植物の量の調節は、例えば、栄養塩類回収設備30から流出する処理水中の栄養塩類の量が目標値に近づくように行うことができる。具体的には、栄養塩類回収設備30に流入する下水処理水の量および/または下水処理水中の栄養塩類の濃度が増加した場合には、水生植物供給機構31が栄養塩類回収設備30へと水生植物を供給するようにして栄養塩類回収設備30で回収可能な栄養塩類の量を増加させることができる。また、栄養塩類回収設備30に流入する下水処理水の量および/または下水処理水中の栄養塩類の濃度が減少した場合には、発電設備32(特に、発電設備32の回収機構)により回収される水生植物の量を増加させることにより、処理水の水質を維持しつつ発電設備32における発電量を増加させることができる。
なお、処理水中の栄養塩類の量の目標値は、特に限定されることなく、放流先の水域で要求される栄養塩類の量や、法令や条例に規定されている規制値などに基づいて適宜に設定することができる。
Further, the amount of aquatic plants can be adjusted using the control device 40, for example, so that the amount of nutrients in the treated water flowing out from the nutrient recovery equipment 30 approaches a target value. Specifically, when the amount of sewage treatment water flowing into the nutrient salt recovery equipment 30 and/or the concentration of nutrient salts in the sewage treatment water increases, the aquatic plant supply mechanism 31 supplies aquatic plants to the nutrient salt recovery equipment 30. By supplying plants, the amount of nutrient salts that can be recovered by the nutrient salt recovery equipment 30 can be increased. Additionally, when the amount of sewage treated water flowing into the nutrient salt recovery equipment 30 and/or the concentration of nutrient salts in the sewage treatment water decreases, the nutrient salts are recovered by the power generation equipment 32 (in particular, the recovery mechanism of the power generation equipment 32). By increasing the amount of aquatic plants, the amount of power generated in the power generation facility 32 can be increased while maintaining the quality of the treated water.
The target value for the amount of nutrient salts in treated water is not particularly limited, and may be set as appropriate based on the amount of nutrient salts required in the water area to which it is discharged, and the regulatory values stipulated in laws and ordinances. Can be set to .

(下水処理方法)
本発明の下水処理方法は、特に限定されることなく、本発明の下水処理システムにおいて下水を処理する際に好適に用いることができる。そして、本発明の下水処理方法は、下水を処理し、栄養塩類を含む下水処理水を得る下水処理工程と、下水処理工程で得られた下水処理水について、そのまま、および/または、水生植物を用いて栄養塩類を回収した後に放流先へと放流する放流工程と、放流工程において、そのまま放流する下水処理水の量と、栄養塩類を回収した後に放流する下水処理水の量とを決定する分配工程と、水生植物を回収し、回収した水生植物を原料として用いて発電を行う発電工程とを含むことを特徴とする。このように、放流工程および分配工程を実施すれば、放流水の水質の能動的管理を容易に行うことができる。また、発電工程を実施すれば、放流水の水質の能動的管理と、エネルギーの創出とを達成することができる。
(Sewage treatment method)
The sewage treatment method of the present invention is not particularly limited, and can be suitably used when treating sewage in the sewage treatment system of the present invention. The sewage treatment method of the present invention includes a sewage treatment process in which sewage is treated to obtain sewage treated water containing nutrients, and the sewage treated water obtained in the sewage treatment process is treated as it is and/or is treated with aquatic plants. A discharge process in which the nutrients are collected using a water bottle and then discharged to a destination, and a distribution process in which the amount of treated sewage water to be discharged as is and the amount of treated sewage water to be discharged after recovering the nutrients are determined in the discharge process. and a power generation step of collecting aquatic plants and generating electricity using the collected aquatic plants as raw materials. By performing the discharge process and the distribution process in this way, the quality of the discharged water can be easily managed actively. Also, by implementing the power generation process, active management of the quality of the effluent and energy generation can be achieved.

ここで、下水処理工程では、例えば上述したような下水処理設備を用いて下水を処理し、栄養塩類(窒素および/またはリン)を含む下水処理水を得る。なお、下水処理水中の窒素濃度は、下水処理システムに関して上述したのと同様とすることができる。 Here, in the sewage treatment step, sewage is treated using, for example, the above-mentioned sewage treatment equipment to obtain treated sewage water containing nutrients (nitrogen and/or phosphorus). Note that the nitrogen concentration in the sewage treatment water can be the same as described above regarding the sewage treatment system.

また、放流工程では、分配工程で決定された量比となるように、下水処理水を、そのまま、または、栄養塩類を回収してから放流する。ここで、本発明の下水処理方法では、栄養塩類を回収されてから放流される下水処理水の割合を変更することで、放流水中に含まれている栄養塩類の量を能動的に制御することができる。
なお、下水処理水から栄養塩類を回収して得られる処理水中の窒素濃度は、下水処理システムに関して上述したのと同様とすることができる。
In addition, in the discharge step, the treated sewage water is discharged as it is, or after recovering nutrients, such that the amount ratio determined in the distribution step is achieved. Here, in the sewage treatment method of the present invention, the amount of nutrient salts contained in the effluent is actively controlled by changing the ratio of sewage treated water that is discharged after nutrient salts have been recovered. I can do it.
Note that the nitrogen concentration in treated water obtained by recovering nutrients from treated sewage water can be the same as that described above regarding the sewage treatment system.

分配工程における、そのまま放流される下水処理水と、栄養塩類を回収されてから放流される下水処理水の割合の決定は、時季に応じて行ってもよいし、放流先で要求される栄養塩類の量に基づいて行ってもよい。 In the distribution process, the ratio of treated sewage water that is discharged as is and treated sewage water that is discharged after recovering nutrients may be determined depending on the season, or may be determined based on the nutrient salts required at the destination. It may also be done based on the amount of

具体的には、例えば、分配工程では、放流先において栄養塩類が不足しがちな冬季(1~3月)にはそのまま放流される下水処理水の量を増やし、夏季(7~9月)には栄養塩類を回収されてから放流される下水処理水の量を増やすように上記割合を決定してもよい。このようにすれば、季節別運転管理を適切に行うことができる。 Specifically, for example, in the distribution process, the amount of treated sewage water that is directly discharged is increased during the winter (January to March), when nutrients tend to be insufficient at the discharge destination, and during the summer (July to September), the amount of treated sewage water is increased. The above ratio may be determined so as to increase the amount of treated sewage water that is discharged after nutrient salts have been recovered. In this way, seasonal operation management can be appropriately performed.

また、分配工程では、放流先で要求される栄養塩類の量が多い場合にはそのまま放流される下水処理水の量を増やし、放流先で要求される栄養塩類の量が少ない場合には栄養塩類を回収されてから放流される下水処理水の量を増やすように上記割合を決定してもよい。このようにすれば、放流先で要求される栄養塩類の量に応じて放流水の水質の能動的管理を適切に行うことができる。
なお、放流先で要求される栄養塩類の量は、例えば、放流先の水域の栄養塩類の濃度を測定し、放流先の水域の栄養塩類の濃度の目標値と測定値との差を算出することにより決定することができる。
In addition, in the distribution process, if the amount of nutrient salts required at the destination is large, the amount of treated sewage water is increased, and if the amount of nutrient salts required at the destination is small, the amount of nutrient salts is increased. The above ratio may be determined so as to increase the amount of treated sewage water that is collected and then discharged. In this way, the quality of the discharged water can be appropriately managed in accordance with the amount of nutrients required at the discharge destination.
The amount of nutrients required at the destination is determined by, for example, measuring the concentration of nutrients in the destination water area and calculating the difference between the target value and the measured value of the nutrient concentration in the destination area. It can be determined by

更に、例えば放流先の水域に放出可能な栄養塩類の総量が下水道法等の法令・条例により規定されている場合などには、分配工程では、放流先への栄養塩類の年間排出量が所定値以下になるように、上記割合を決定してもよい。具体的には、分配工程では、例えば、予め年間運転計画を立案した上で、放流水中の栄養塩類の濃度および放流水の流量を測定して放流先への栄養塩類の供給量の積算値を算出しておき、冬季の供給量を十分確保すべく当該積算値が法令や条例の規制値を超えないように、あらかじめ夏季に供給量を抑制することができる。 Furthermore, in cases where the total amount of nutrient salts that can be released into the water area at the destination is stipulated by laws and ordinances such as the Sewerage Act, in the distribution process, the annual amount of nutrient salts discharged to the destination should be set at a predetermined value. The above ratio may be determined to be as follows. Specifically, in the distribution process, for example, an annual operation plan is drawn up in advance, and the concentration of nutrients in the effluent and the flow rate of the effluent are measured to calculate the cumulative amount of nutrient salts supplied to the destination. By calculating the amount, it is possible to suppress the supply amount in advance in the summer so that the integrated value does not exceed the regulated value of laws and ordinances in order to ensure a sufficient supply amount in the winter.

なお、本発明の下水処理方法は、上述した工程に加え、更に、放流工程で用いる水生植物の量を調節する水生植物量調節工程を有していてもよい。
ここで、水生植物量調節工程における水生植物の量の調節は、例えば、放流工程において水生植物を用いて下水処理水から栄養塩類を回収して得られる処理水中の栄養塩類の量が目標値に近づくように行うことができる。具体的には、水生植物を用いて栄養塩類を回収される下水処理水の量および/または下水処理水中の栄養塩類の濃度が増加した場合には、放流工程で用いる水生植物の量を増加させることができる。また、水生植物を用いて栄養塩類を回収される下水処理水の量および/または下水処理水中の栄養塩類の濃度が減少した場合には、発電工程において回収する水生植物の量を増加させることにより、処理水の水質を維持しつつ発電工程における発電量を増加させることができる。
なお、処理水中の栄養塩類の量の目標値は、特に限定されることなく、放流先の水域で要求される栄養塩類の量や、法令や条例に規定されている規制値などに基づいて適宜に設定することができる。
In addition to the steps described above, the sewage treatment method of the present invention may further include an aquatic plant amount adjustment step of adjusting the amount of aquatic plants used in the discharge step.
Here, adjustment of the amount of aquatic plants in the aquatic plant amount adjustment step is performed by, for example, recovering nutrients from treated sewage water using aquatic plants in the discharge step so that the amount of nutrient salts in the treated water reaches a target value. It can be done to get closer. Specifically, if the amount of treated sewage water from which nutrient salts are recovered using aquatic plants and/or the concentration of nutrient salts in the treated sewage water increases, the amount of aquatic plants used in the discharge process is increased. be able to. In addition, if the amount of sewage treated water from which nutrient salts are recovered using aquatic plants and/or the concentration of nutrient salts in sewage treated water decreases, increasing the amount of aquatic plants recovered in the power generation process , it is possible to increase the amount of power generated in the power generation process while maintaining the quality of treated water.
The target value for the amount of nutrient salts in the treated water is not particularly limited, and may be determined as appropriate based on the amount of nutrient salts required in the water area to which it is discharged, and the regulatory values stipulated in laws and ordinances. Can be set to .

そして、発電工程では、回収した水生植物を原料として用いて発電をすることが可能であれば特に限定されることなく、例えば、余剰の水生植物を回収する回収ステップと、回収した水生植物を嫌気性消化して消化ガスを得る消化ステップと、消化ガスを用いて発電を行う発電ステップとを実施して発電することができる。余剰の水生植物を原料として用いて発電を行えば、放流水中に含まれている栄養塩類の量の能動的な管理を行いつつ、電気エネルギーを創出することができる。
なお、発電工程では、水生植物に加えて、下水処理工程で生じる余剰汚泥等も原料として用いて発電を行ってもよい。
In the power generation process, there is no particular limitation as long as it is possible to generate electricity using the collected aquatic plants as raw materials. Electric power can be generated by performing a digestion step to obtain digestive gas by performing natural digestion and a power generation step to generate power using the digestive gas. By using surplus aquatic plants as raw materials to generate electricity, it is possible to generate electrical energy while actively managing the amount of nutrients contained in the effluent.
In addition, in the power generation process, in addition to aquatic plants, surplus sludge generated in the sewage treatment process may also be used as a raw material to generate power.

以上、一例を用いて本発明の下水処理システムおよび下水処理方法について説明したが、本発明の下水処理システムおよび下水処理方法は上述した例に限定されるものではない。具体的には、本発明の下水処理システムおよび下水処理方法では、水生植物を原料として用いて発電を行った際の発電量を予測し得るようにしてもよい。より具体的には、例えば、放流先の水域の栄養塩類の要求量に基づいて下水処理水から回収する栄養塩類の量を決定し、回収される栄養塩類の量から水生植物の増殖量を算出し、当該増殖量から消化ガスの発生量および当該消化ガスを用いた際の発電量を算出することにより、発電可能な電力量を予測し得るようにしてもよい。発電量の予測が可能であれば、エネルギー供給拠点としてより効率的にエネルギーを供給することができる。 Although the sewage treatment system and sewage treatment method of the present invention have been described above using one example, the sewage treatment system and sewage treatment method of the present invention are not limited to the above-mentioned example. Specifically, in the sewage treatment system and sewage treatment method of the present invention, it may be possible to predict the amount of power generated when power is generated using aquatic plants as raw materials. More specifically, for example, the amount of nutrients to be recovered from treated sewage water is determined based on the amount of nutrients required by the water area to which it is discharged, and the amount of aquatic plant growth is calculated from the amount of recovered nutrients. However, the amount of power that can be generated may be predicted by calculating the amount of digestion gas generated and the amount of power generated when using the digestion gas from the amount of proliferation. If it is possible to predict the amount of power generated, it will be possible to supply energy more efficiently as an energy supply base.

本発明の下水処理システムおよび下水処理方法によれば、放流水の水質の能動的管理を容易に行うことができると共に、エネルギーの創出も可能になる。 According to the sewage treatment system and sewage treatment method of the present invention, it is possible to easily actively manage the quality of effluent water, and it is also possible to generate energy.

10 下水処理設備
21 放流路
22 第一流量調節弁
23 バイパス流路
24 第二流量調節弁
30 栄養塩類回収設備
31 水生植物供給機構
32 発電設備
40 制御装置
10 Sewage treatment equipment 21 Discharge channel 22 First flow rate control valve 23 Bypass channel 24 Second flow rate control valve 30 Nutrient recovery facility 31 Aquatic plant supply mechanism 32 Power generation facility 40 Control device

Claims (8)

下水を処理し、栄養塩類を含む下水処理水を排出する下水処理設備と、
前記下水処理設備から流出した前記下水処理水を放流先へと放流する第一放流路と、
水生植物を用いて前記下水処理水中の栄養塩類を回収する栄養塩類回収設備を有し、前記下水処理水から栄養塩類を回収してなる処理水を前記放流先へと放流する第二放流路と、
前記下水処理設備から前記第一放流路へと流入する下水処理水量および前記下水処理設備から前記第二放流路へと流入する下水処理水量を調節する流量調節機構と、
前記栄養塩類回収設備から前記水生植物を回収し、回収した水生植物を原料として用いて発電を行う発電設備と、
を備え
前記栄養塩類回収設備が、前記処理水中の栄養塩類の量が目標値に近づくように前記水生植物の量を調節する制御装置を備える、下水処理システム。
A sewage treatment facility that processes sewage and discharges treated sewage water containing nutrients;
a first discharge path for discharging the treated sewage water flowing out from the sewage treatment facility to a destination;
a second discharge channel comprising a nutrient salt recovery facility for recovering nutrients in the treated sewage water using aquatic plants, and discharging the treated water obtained by recovering the nutrients from the treated sewage water to the discharge destination; ,
a flow rate adjustment mechanism that adjusts the amount of treated sewage water flowing from the sewage treatment equipment into the first discharge channel and the amount of treated sewage water flowing from the sewage treatment facility into the second discharge channel;
a power generation facility that collects the aquatic plants from the nutrient salt recovery facility and generates power using the collected aquatic plants as raw materials;
Equipped with
A sewage treatment system , wherein the nutrient salt recovery equipment includes a control device that adjusts the amount of the aquatic plants so that the amount of nutrient salts in the treated water approaches a target value .
前記流量調節機構が、前記第一放流路へと流入する下水処理水量および前記第二放流路へと流入する下水処理水量を時季に応じて制御する制御装置を備える、請求項1に記載の下水処理システム。 The sewage system according to claim 1, wherein the flow rate adjustment mechanism includes a control device that controls the amount of treated sewage water flowing into the first discharge channel and the amount of treated sewage water flowing into the second discharge channel according to the season. processing system. 前記流量調節機構が、前記第一放流路へと流入する下水処理水量および前記第二放流路へと流入する下水処理水量を、前記放流先で要求される栄養塩類の量に基づいて制御する制御装置を備える、請求項1に記載の下水処理システム。 The flow rate adjustment mechanism controls the amount of treated sewage water flowing into the first discharge channel and the amount of treated sewage water flowing into the second discharge channel based on the amount of nutrients required at the discharge destination. A sewage treatment system according to claim 1, comprising an apparatus. 前記流量調節機構が、前記放流先への栄養塩類の年間排出量が所定値以下になるように前記第一放流路へと流入する下水処理水量および前記第二放流路へと流入する下水処理水量を制御する制御装置を備える、請求項1~3の何れかに記載の下水処理システム。 The flow rate adjustment mechanism controls the amount of treated sewage water flowing into the first discharge channel and the amount of treated sewage water flowing into the second discharge channel so that the annual discharge amount of nutrients to the discharge destination is equal to or less than a predetermined value. The sewage treatment system according to any one of claims 1 to 3, comprising a control device for controlling the sewage treatment system. 下水を処理し、栄養塩類を含む下水処理水を得る下水処理工程と、
前記下水処理工程で得られた前記下水処理水について、そのまま、および/または、水生植物を用いて栄養塩類を回収した後に放流先へと放流する放流工程と、
前記放流工程において、そのまま放流する下水処理水の量と、栄養塩類を回収した後に放流する下水処理水の量とを決定する分配工程と、
前記水生植物を回収し、回収した水生植物を原料として用いて発電を行う発電工程と、
を含み、
前記放流工程において前記水生植物を用いて前記下水処理水から栄養塩類を回収して得られる処理水中の栄養塩類の量が目標値に近づくように前記放流工程で用いる前記水生植物の量を調節する水生植物量調節工程を更に含む、下水処理方法。
a sewage treatment process for treating sewage to obtain treated sewage water containing nutrients;
A discharge step of discharging the treated sewage water obtained in the sewage treatment step to a destination as it is and/or after recovering nutrients using aquatic plants;
In the discharge step, a distribution step of determining the amount of treated sewage water to be discharged as is and the amount of treated sewage water to be discharged after recovering nutrients;
a power generation step of collecting the aquatic plants and generating electricity using the collected aquatic plants as raw materials;
including;
In the discharge step, the amount of the aquatic plants used in the discharge step is adjusted so that the amount of nutrients in the treated water obtained by recovering nutrients from the treated sewage water using the aquatic plants approaches a target value. A sewage treatment method further comprising a step of adjusting the amount of aquatic plants .
前記分配工程では、そのまま放流する下水処理水の量と、栄養塩類を回収した後に放流する下水処理水の量とを、時季に応じて決定する、請求項に記載の下水処理方法。 The sewage treatment method according to claim 5 , wherein in the distribution step, the amount of treated sewage water to be discharged as is and the amount of treated sewage water to be discharged after recovering nutrients are determined depending on the season. 前記分配工程では、そのまま放流する下水処理水の量と、栄養塩類を回収した後に放流する下水処理水の量とを、前記放流先で要求される栄養塩類の量に基づいて決定する、請求項に記載の下水処理方法。 In the distribution step, the amount of treated sewage water to be discharged as is and the amount of treated sewage water to be discharged after recovering the nutrient salts are determined based on the amount of nutrient salts required at the discharge destination. The sewage treatment method described in 5 . 前記分配工程では、そのまま放流する下水処理水の量と、栄養塩類を回収した後に放流する下水処理水の量とを、前記放流先への栄養塩類の年間排出量が所定値以下になるように決定する、請求項5~7の何れかに記載の下水処理方法。 In the distribution step, the amount of treated sewage water to be discharged as is and the amount of treated sewage water to be discharged after recovering nutrients are adjusted such that the annual amount of nutrients discharged to the discharge destination is below a predetermined value. The sewage treatment method according to any one of claims 5 to 7 , wherein the sewage treatment method is determined.
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きれいで豊かな海の確保に向けた下水道の取り組みについて,中央環境審議会水環境部会瀬戸内海環境保全小委員会(第10回),資料8,国土交通省

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