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JP7754142B2 - Wastewater treatment method - Google Patents
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JP7754142B2 - Wastewater treatment method - Google Patents

Wastewater treatment method

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Publication number
JP7754142B2
JP7754142B2 JP2023120083A JP2023120083A JP7754142B2 JP 7754142 B2 JP7754142 B2 JP 7754142B2 JP 2023120083 A JP2023120083 A JP 2023120083A JP 2023120083 A JP2023120083 A JP 2023120083A JP 7754142 B2 JP7754142 B2 JP 7754142B2
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wastewater
adjustment tank
load
wastewater treatment
tank
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JP2025017159A (en
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瑞季 鈴木
康一 大木
哲 竹林
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Kurita Water Industries Ltd
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Priority to JP2023120083A priority Critical patent/JP7754142B2/en
Priority to PCT/JP2024/024253 priority patent/WO2025022974A1/en
Priority to CN202480045104.6A priority patent/CN121443559A/en
Priority to KR1020257035872A priority patent/KR20260042063A/en
Priority to TW113126131A priority patent/TW202513478A/en
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage

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  • Life Sciences & Earth Sciences (AREA)
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  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Activated Sludge Processes (AREA)
  • Sink And Installation For Waste Water (AREA)
  • Sewage (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

本発明は、排水処理流入部の排水負荷を推定し、推定した排水負荷を元に排水処理が破綻しないように高負荷排水を別の貯槽へ振り分け、排水負荷が低いタイミングで高負荷排水を送水することで排水処理を安定化させる排水処理方法に関する。 The present invention relates to a wastewater treatment method that estimates the wastewater load at the wastewater treatment inlet, allocates high-load wastewater to a separate storage tank based on the estimated wastewater load to prevent the wastewater treatment from failing, and delivers high-load wastewater at times when the wastewater load is low, thereby stabilizing the wastewater treatment.

飲料、食品などの製造工場から排出される排水は、製造品目や製造量、製造ラインの洗浄経過時間などにより、濃度や排水量が大きく変動する場合が多い。排水の負荷により適した排水処理の運転条件が異なる場合が多く、排水の負荷変動が大きい場合には処理状況に影響を及ぼす場合がある。 The concentration and volume of wastewater discharged from beverage, food, and other manufacturing plants often fluctuate greatly depending on the product, production volume, and the elapsed time since the production line was cleaned. The optimal operating conditions for wastewater treatment often vary depending on the wastewater load, and large fluctuations in wastewater load can affect the treatment status.

特に有機性排水は排水処理として好気処理や嫌気処理といった生物処理を行うことが一般的であるが、排水負荷が大きいと生物の処理能力を超えて生物処理が破綻し、処理水質が悪化する等の問題が発生する恐れがある。 Organic wastewater in particular is typically treated using biological processes such as aerobic and anaerobic treatment, but if the wastewater load is large, the biological treatment may fail due to the organisms exceeding their processing capacity, resulting in problems such as a deterioration in the quality of the treated water.

また、フェントン反応による処理や吸着などの物理化学処理による処理においても、添加する薬剤や吸着剤の必要量が変化するため、処理設備に流入する排水の負荷の変動を把握することは重要である。 Furthermore, even in treatments using physical and chemical processes such as the Fenton reaction or adsorption, the amount of chemicals or adsorbents required to be added changes, so it is important to understand the fluctuations in the load of wastewater flowing into the treatment facility.

従来は、運転員が定期的に排水を採取・分析することで、排水処理流入部の排水負荷を把握し、高負荷排水が流入した際には、別の槽へ緊急避難する、希釈をする、排水処理への流入量を減らすなどの対策を手動で行っていた。しかし、この方法では、常に人の手で行うため連続的な測定ができず、高負荷排水の流入を見逃したり、対策が遅れたりすることで、排水処理が破綻し、処理水質が悪化することがあった。従って、流入する排水の負荷を連続的に把握し、排水処理が破綻しないよういち早く対策を取ることは非常に重要である。 Conventionally, operators would regularly collect and analyze wastewater samples to determine the wastewater load at the inlet of the wastewater treatment plant. When high-load wastewater flowed in, they would manually take measures such as emergency evacuation to another tank, dilution, or reducing the amount of wastewater entering the treatment plant. However, because this method requires constant manual work, continuous measurement is not possible, and the inflow of high-load wastewater could be overlooked or measures delayed, leading to a breakdown in the wastewater treatment system and a deterioration in the quality of the treated water. Therefore, it is extremely important to continuously monitor the load of inflowing wastewater and take prompt measures to prevent the wastewater treatment system from breaking down.

特許文献1には、濃度に応じて処理工程を振り分けることで、排水処理の安定化を図る排水処理装置が開示されている。具体的には、測定した排水の電気伝導度を元に排水を高濃度排水と低濃度排水に振り分ける。しかし、本手法で測定している電気伝導度では、導電性の低い汚濁物質を十分に評価することが難しい。加えて、高濃度排水と低濃度排水は両者の比較により高濃度か低濃度かを区別しており、数値により限定はされていない。このような方法では、排水の水質によって高濃度か低濃度かの判断が異なることとなる。例えば、高濃度の排水が長時間続いた場合には、後段の排水処理に影響を及ぼすような濃度の排水が低濃度排水として区別されてしまう懸念がある。 Patent Document 1 discloses a wastewater treatment device that stabilizes wastewater treatment by allocating treatment processes according to concentration. Specifically, wastewater is divided into high-concentration and low-concentration wastewater based on the measured electrical conductivity of the wastewater. However, the electrical conductivity measured by this method makes it difficult to adequately evaluate pollutants with low conductivity. In addition, high-concentration and low-concentration wastewater are distinguished by comparing the two, and are not limited by numerical values. With this method, the determination of whether the wastewater is high or low in concentration varies depending on the water quality of the wastewater. For example, if high-concentration wastewater continues for a long period of time, there is a concern that wastewater with a concentration that would affect subsequent wastewater treatment may be classified as low-concentration wastewater.

特開2002-282889号公報Japanese Patent Application Laid-Open No. 2002-282889

本発明は、排水処理を安定して行うことができる排水処理方法を提供することを課題とする。 The objective of the present invention is to provide a wastewater treatment method that can stably treat wastewater.

[1] 排水を調整槽に流入し、前記調整槽から排水処理設備へ送水する排水処理方法であって、
排水負荷に関する水質項目または運転管理項目を連続的または定期的に測定し、測定値に基づいて予め設定した演算式にて前記排水処理設備への排水流入部(排水処理流入部)の排水負荷を推定し、
推定した前記排水負荷が所定の閾値未満の場合、前記排水を前記調整槽に供給し、
推定した前記排水負荷が前記閾値以上の場合、前記排水を前記調整槽の上流側の排水分岐位置にて分岐して高負荷調整槽に貯留する、排水処理方法。
[1] A wastewater treatment method in which wastewater flows into an adjustment tank and is sent from the adjustment tank to wastewater treatment equipment,
Water quality items or operational management items related to wastewater loads are measured continuously or periodically, and the wastewater load at the wastewater inlet (wastewater treatment inlet) to the wastewater treatment facility is estimated using a predetermined calculation formula based on the measured values;
If the estimated wastewater load is less than a predetermined threshold, the wastewater is supplied to the adjustment tank;
When the estimated wastewater load is equal to or greater than the threshold value, the wastewater is branched at a wastewater branch position upstream of the adjustment tank and stored in a high-load adjustment tank.

[2] 前記排水負荷に関する水質項目または運転管理項目は、前記排水の汚濁負荷又は汚濁負荷と相関する項目、及び前記排水処理設備へ流入する排水流量を含む、[1]の排水処理方法。 [2] The wastewater treatment method of [1], wherein the water quality items or operational management items related to the wastewater load include the pollution load of the wastewater or items correlated with the pollution load, and the wastewater flow rate flowing into the wastewater treatment facility.

[3] 前記高負荷調整槽から送水して前記排水分岐位置より下流側に合流させたときの前記排水負荷が所定の閾値以下になる場合は、前記高負荷調整槽から送水を行う、[1]又は[2]の排水処理方法。 [3] A wastewater treatment method according to [1] or [2], in which if the wastewater load when water is sent from the high-load adjustment tank and joined downstream of the wastewater branch position is below a predetermined threshold, water is sent from the high-load adjustment tank.

[4] 前記高負荷調整槽から送水して、前記調整槽の下流側に合流させる、[3]の排水処理方法。 [4] A wastewater treatment method according to [3], in which water is pumped from the high-load adjustment tank and merges downstream of the adjustment tank.

[5] 前記高負荷調整槽から前記調整槽へ送水する、[3]の排水処理方法。 [5] The wastewater treatment method of [3], in which water is pumped from the high-load adjustment tank to the adjustment tank.

本発明によれば、排水処理を安定して行うことができる。 According to the present invention, wastewater treatment can be carried out stably.

参考技術に係る排水処理システムの概略構成図である。FIG. 1 is a schematic configuration diagram of a wastewater treatment system according to a reference technology. 参考技術に係る排水処理システムの概略構成図である。FIG. 1 is a schematic configuration diagram of a wastewater treatment system according to a reference technology. 参考技術に係る排水処理システムの概略構成図である。FIG. 1 is a schematic configuration diagram of a wastewater treatment system according to a reference technology. 本発明の実施形態に係る排水処理システムの概略構成図である。1 is a schematic configuration diagram of a wastewater treatment system according to an embodiment of the present invention. 同実施形態に係る排水処理システムの概略構成図である。FIG. 2 is a schematic configuration diagram of the wastewater treatment system according to the embodiment. 参考技術に係る排水処理システムの概略構成図である。FIG. 1 is a schematic configuration diagram of a wastewater treatment system according to a reference technology. 本発明の実施形態に係る排水処理システムの概略構成図である。1 is a schematic configuration diagram of a wastewater treatment system according to an embodiment of the present invention. 同実施形態に係る排水処理システムの概略構成図である。FIG. 2 is a schematic configuration diagram of the wastewater treatment system according to the embodiment. 同実施形態に係る排水処理システムの概略構成図である。FIG. 2 is a schematic configuration diagram of the wastewater treatment system according to the embodiment. 同実施形態に係る排水処理システムの概略構成図である。FIG. 2 is a schematic configuration diagram of the wastewater treatment system according to the embodiment. 参考技術に係る排水処理システムの概略構成図である。FIG. 1 is a schematic configuration diagram of a wastewater treatment system according to a reference technology. 参考技術に係る排水処理システムの概略構成図である。FIG. 1 is a schematic configuration diagram of a wastewater treatment system according to a reference technology. 本発明の実施形態に係る排水処理システムの概略構成図である。1 is a schematic configuration diagram of a wastewater treatment system according to an embodiment of the present invention. 同実施形態に係る排水処理システムの概略構成図である。FIG. 2 is a schematic configuration diagram of the wastewater treatment system according to the embodiment.

本発明の実施形態に係る排水処理システムは、排水を調整槽で受け、調整槽から排水処理設備へ排水を送水するものであって、調整槽より上流側の汚濁負荷と、調整槽へ流入する排水の流量と、排水処理設備へ流入する排水の流量とをそれぞれ測定し、これらを用いて、排水処理設備の流入部(以下、「排水処理流入部」とも記載する。)の排水負荷を推定する。また、推定した排水負荷を元に、排水処理が破綻しないように高負荷排水を別の貯槽へ振り分け、排水負荷が低いタイミングで高負荷排水を送水することで排水処理を安定化させる。 A wastewater treatment system according to an embodiment of the present invention receives wastewater in an equalization tank and delivers it from the equalization tank to a wastewater treatment facility. It measures the pollution load upstream of the equalization tank, the flow rate of wastewater flowing into the equalization tank, and the flow rate of wastewater flowing into the wastewater treatment facility, and uses these to estimate the wastewater load at the inlet of the wastewater treatment facility (hereinafter also referred to as the "wastewater treatment inlet"). Furthermore, based on the estimated wastewater load, high-load wastewater is allocated to a separate storage tank to prevent the wastewater treatment from failing, and high-load wastewater is delivered when the wastewater load is low, thereby stabilizing the wastewater treatment.

調整槽は1槽以上設けられており、後述のように、複数の調整槽1が並列に配置されていてもよいし、直列に配置されていてもよい。調整槽の容積などの仕様は特に限定されない。また、排水処理設備の処理方式や系統数は特に限定されない。処理方式としては、例えば好気性、嫌気性を含めたいわゆる生物処理、フェントン処理や活性炭処理など物理化学処理が挙げられる。 One or more equalization tanks are provided, and as described below, multiple equalization tanks 1 may be arranged in parallel or in series. Specifications such as the volume of the equalization tank are not particularly limited. Furthermore, the treatment method and number of systems in the wastewater treatment facility are not particularly limited. Treatment methods include, for example, so-called biological treatment, including aerobic and anaerobic treatment, and physicochemical treatments such as Fenton treatment and activated carbon treatment.

次に、排水処理流入部の排水負荷の推定方法を図面に基づいて説明する。 Next, we will explain how to estimate the wastewater load at the wastewater treatment inlet using the drawings.

図1に示すように、排水処理システムが、調整槽1と、調整槽1の後段(下流側)に設置された排水処理設備3とを備える場合は、調整槽1の前段(上流側)に設けられた汚濁負荷測定部4により、排水の汚濁負荷を測定する。また、第1流量測定部5を用いて、調整槽1へ流入する排水の流量を測定し、第2流量測定部10を用いて、排水処理設備3へ流入する排水の流量を測定する。 As shown in Figure 1, when a wastewater treatment system includes an equalization tank 1 and wastewater treatment equipment 3 installed downstream of the equalization tank 1, the pollutant load of the wastewater is measured using a pollution load measuring unit 4 installed upstream of the equalization tank 1. In addition, a first flow rate measuring unit 5 is used to measure the flow rate of wastewater flowing into the equalization tank 1, and a second flow rate measuring unit 10 is used to measure the flow rate of wastewater flowing into the wastewater treatment equipment 3.

調整槽1は、水質や水量の変動が調整され緩和されることを目的として、HRT(水理学的滞留時間)30分以上を有する。 The adjustment tank 1 has an HRT (hydraulic retention time) of 30 minutes or more in order to regulate and mitigate fluctuations in water quality and quantity.

本実施形態では、汚濁負荷としてTOC濃度を測定する例について説明するが、測定項目はTOC濃度に限定されず、COD濃度やSS濃度など他の汚濁負荷を示す指標であってもよい。また、汚濁負荷測定部4が測定するものは、汚濁負荷に相関する項目であってもよく、例えば、電気伝導度やブリックス糖度が挙げられる。 In this embodiment, an example will be described in which TOC concentration is measured as the pollution load, but the measurement item is not limited to TOC concentration, and other indicators of pollution load, such as COD concentration or SS concentration, may also be used. Furthermore, the pollution load measurement unit 4 may measure items that are correlated with pollution load, such as electrical conductivity or Brix sugar content.

第1流量測定部5は流量計を用いることができる。調整槽1がバッチ通水の場合、第1流量測定部5は、調整槽1における単位時間当たりの水位増加量から、調整槽1へ流入する排水の流量を算出しても良い。もしくは調整槽1が連続通水の場合は、調整槽1の貯留量変化と調整槽からの排出流量の和から、調整槽1へ流入する排水の流量を算出しても良い。 The first flow rate measuring unit 5 can be a flow meter. If the adjustment tank 1 is a batch-flow tank, the first flow rate measuring unit 5 may calculate the flow rate of wastewater flowing into the adjustment tank 1 from the increase in water level per unit time in the adjustment tank 1. Alternatively, if the adjustment tank 1 is a continuous flow tank, the flow rate of wastewater flowing into the adjustment tank 1 may be calculated from the sum of the change in the storage volume of the adjustment tank 1 and the discharge flow rate from the adjustment tank.

第2流量測定部10は流量計を用いることができる。調整槽1がバッチ通水の場合、第2流量測定部10は、調整槽1における単位時間当たりの水位減少量から、排水処理設備3へ流入する排水の流量を算出しても良い。 The second flow rate measuring unit 10 can be a flow meter. If the adjustment tank 1 is a batch water supply tank, the second flow rate measuring unit 10 may calculate the flow rate of wastewater flowing into the wastewater treatment equipment 3 from the amount of decrease in water level per unit time in the adjustment tank 1.

汚濁負荷測定部4、第1流量測定部5及び第2流量測定部10により、排水負荷に関する水質項目または運転管理項目である、汚濁負荷又はそれと相関する項目、調整槽1へ流入する排水の流量、及び排水処理系統へ流入する排水流量が、連続的に、又は比較的短い時間間隔で定期的に測定される。 The pollution load measuring unit 4, first flow rate measuring unit 5, and second flow rate measuring unit 10 continuously or periodically measure the pollution load or related items, which are water quality items or operational management items related to wastewater load, the flow rate of wastewater flowing into the balancing tank 1, and the flow rate of wastewater flowing into the wastewater treatment system, either continuously or at relatively short time intervals.

演算部6は、汚濁負荷測定部4が測定したTOC濃度、及び第1流量測定部5が測定した流量を用いて、排水処理流入部(調整槽1の出口)におけるTOC濃度を推定する。また、演算部6は、推定したTOC濃度、及び第2流量測定部10が測定した流量を用いて、排水処理流入部の排水負荷(kg-TOC/day)を推定する。 The calculation unit 6 estimates the TOC concentration at the wastewater treatment inlet (outlet of the equalization tank 1) using the TOC concentration measured by the pollution load measurement unit 4 and the flow rate measured by the first flow rate measurement unit 5. The calculation unit 6 also estimates the wastewater treatment inlet load (kg-TOC/day) using the estimated TOC concentration and the flow rate measured by the second flow rate measurement unit 10.

汚濁負荷測定部4が測定したTOC濃度、及び第1流量測定部5が測定した流量を用いて、排水処理流入部におけるTOC濃度を推定する方法は、各種提案されている滞留水槽の濃度計算モデルで行えるが、例えば調整槽1が連続通水かバッチ通水かによって、以下のような異なる推定方法を用いることができる。 The TOC concentration at the wastewater treatment inlet can be estimated using the TOC concentration measured by the pollution load measurement unit 4 and the flow rate measured by the first flow rate measurement unit 5 using various proposed concentration calculation models for retention tanks. However, depending on whether the equalization tank 1 is a continuous or batch flow tank, for example, different estimation methods can be used, such as those described below.

<連続通水の時>
推定方法(1)-1
調整槽1より上流側で測定したTOC濃度を、調整槽1での滞留時間に近い時間で移動平均化することで、排水処理流入部のTOC濃度(mg/L)を推定する。例えば、調整槽1での滞留時間が50分である場合、現在から50分前までのTOC濃度測定結果の平均を、(調整槽1から排出される)排水処理流入部のTOC濃度とみなすことができる。
<When water is flowing continuously>
Estimation method (1)-1
The TOC concentration (mg/L) at the inlet of the wastewater treatment plant is estimated by taking a moving average of the TOC concentration measured upstream of the adjustment tank 1 over a time period close to the residence time in the adjustment tank 1. For example, if the residence time in the adjustment tank 1 is 50 minutes, the average of the TOC concentration measurement results from the present to 50 minutes ago can be considered to be the TOC concentration at the inlet of the wastewater treatment plant (discharged from the adjustment tank 1).

推定方法(2)-1
調整槽1より上流側で測定したTOC濃度と流量から、完全混合槽モデルを用いて調整槽1に流入した排水濃度の変化を推定し、排水処理流入部のTOC濃度(mg/L)を推定する。
Estimation method (2)-1
From the TOC concentration and flow rate measured upstream of the adjustment tank 1, the change in the concentration of wastewater flowing into the adjustment tank 1 is estimated using a complete mixing tank model, and the TOC concentration (mg/L) at the wastewater treatment inlet is estimated.

<バッチ通水の時>
推定方法(3)-1
調整槽1に流入した全TOC重量(g)を調整槽1に流入した全水量(m)で除することで、排水処理流入部のTOC濃度(mg/L)を推定する。調整槽1へ流入した全TOC重量や全水量を正確に把握するためには、調整槽入口バルブ開閉信号やポンプ発停信号を入手し、入口バルブ「開」から「閉」まで、又はポンプが稼働している時間のTOC濃度及び水量を積算し、負荷を算出することが望ましい。バルブ開閉信号やポンプ発停信号の入手が難しい場合は、調整槽1の水位変化から調整槽1に排水が流入しているタイミングを把握しても良い。
<When passing water through a batch>
Estimation method (3)-1
The TOC concentration (mg/L) at the wastewater treatment inlet is estimated by dividing the total TOC weight (g) that flowed into the adjustment tank 1 by the total water volume (m 3 ) that flowed into the adjustment tank 1. In order to accurately determine the total TOC weight and total water volume that flowed into the adjustment tank 1, it is desirable to obtain an adjustment tank inlet valve open/close signal or a pump start/stop signal, and calculate the load by integrating the TOC concentration and water volume from the inlet valve "open" to "close" or while the pump is operating. If it is difficult to obtain a valve open/close signal or a pump start/stop signal, the timing at which wastewater is flowing into the adjustment tank 1 can be determined from changes in the water level in the adjustment tank 1.

演算部6は、上記の推定方法(1)-1、(2)-1、(3)-1のいずれかで推定した排水処理流入部のTOC濃度と、第2流量測定部10が測定した排水処理流入部の流量から、排水負荷(kg-TOC/day)を以下の式1にて推定する。 The calculation unit 6 estimates the wastewater load (kg-TOC/day) using the following formula 1 from the TOC concentration at the wastewater treatment inlet estimated using one of the above estimation methods (1)-1, (2)-1, or (3)-1, and the flow rate at the wastewater treatment inlet measured by the second flow rate measurement unit 10.

式1: 排水負荷(kg-TOC/day)=排水処理流入部のTOC濃度(mg/L)×排水処理流入部の流量(m/h)×24h/1000 Equation 1: Wastewater load (kg-TOC/day)=TOC concentration at inlet of wastewater treatment (mg/L)×flow rate at inlet of wastewater treatment (m 3 /h)×24h/1000

図2のように、調整槽1と排水処理設備3との間に、調整槽2が調整槽1と直列に並んで設けられている場合には、まず調整槽1出口のTOC濃度(推定値A)を推定する。調整槽2は1槽以上設けられており、後述のように、複数の調整槽2が並列に配置されていてもよい。調整槽2の容積などの仕様は特に限定されない。図1と同様に、調整槽1が連続通水かバッチ通水かで推定方法が異なり、連続通水の場合は上記の推定方法(1)-1又は(2)-1、バッチ通水の場合は推定方法(3)-1にて調整槽1出口のTOC濃度(推定値A)を推定する。 As shown in Figure 2, when an adjustment tank 2 is installed in series with the adjustment tank 1 between the adjustment tank 1 and the wastewater treatment equipment 3, the TOC concentration (estimated value A) at the outlet of the adjustment tank 1 is first estimated. One or more adjustment tanks 2 may be installed, and as described below, multiple adjustment tanks 2 may be arranged in parallel. Specifications such as the volume of the adjustment tank 2 are not particularly limited. As with Figure 1, the estimation method differs depending on whether the adjustment tank 1 is a continuous or batch-flow system. In the case of continuous flow, the TOC concentration (estimated value A) at the outlet of the adjustment tank 1 is estimated using the above estimation method (1)-1 or (2)-1, and in the case of batch-flow, estimation method (3)-1.

次に、上記のようにして求めた調整槽1出口のTOC濃度(推定値A)と、第3流量測定部8が測定した調整槽2に流入する排水の流量から、排水処理流入部(調整槽2の出口)のTOC濃度(推定値B)を推定する。ここでも、調整槽2が連続通水かバッチ通水かで推定方法が異なり、連続通水の場合は以下の推定方法(1)-2又は(2)-2、バッチ通水の場合は推定方法(3)-2を用いて、排水処理流入部のTOC濃度(推定値B)を推定する。 Next, the TOC concentration (estimated value B) at the wastewater treatment inlet (outlet of adjustment tank 2) is estimated from the TOC concentration (estimated value A) at the outlet of adjustment tank 1 determined as described above and the flow rate of wastewater flowing into adjustment tank 2 measured by third flow measurement unit 8. Here again, the estimation method differs depending on whether adjustment tank 2 is a continuous or batch flow system. In the case of continuous flow, the TOC concentration (estimated value B) at the wastewater treatment inlet is estimated using estimation method (1)-2 or (2)-2 below, and in the case of batch flow, estimation method (3)-2.

推定方法(1)-2
TOC濃度(推定値A)を調整槽2での滞留時間に近い時間で移動平均化することで排水処理流入部のTOC濃度(mg/L)を推定する。
Estimation method (1)-2
The TOC concentration (estimated value A) is averaged over a period of time close to the residence time in the adjusting tank 2 to estimate the TOC concentration (mg/L) at the inlet of the wastewater treatment plant.

推定方法(2)-2
TOC濃度(推定値A)と調整槽2に流入する流量から、完全混合槽モデルを用いて調整槽2に流入した排水濃度の変化を推定し、排水処理流入部のTOC濃度(mg/L)を推定する。
Estimation method (2)-2
From the TOC concentration (estimated value A) and the flow rate flowing into the adjustment tank 2, the change in the concentration of wastewater flowing into the adjustment tank 2 is estimated using a complete mixing tank model, and the TOC concentration (mg/L) at the wastewater treatment inlet is estimated.

推定方法(3)-2
調整槽2に流入した全TOC重量(g)を調整槽2に流入した全水量(m)で除することで、排水処理流入部のTOC濃度(mg/L)を推定する。
Estimation method (3)-2
The total TOC weight (g) flowing into the adjustment tank 2 is divided by the total amount of water (m 3 ) flowing into the adjustment tank 2 to estimate the TOC concentration (mg/L) at the inlet of the wastewater treatment.

調整槽2へ流入する排水の流量を測定する第3流量測定部8は、流量計でもよいし、調整槽2がバッチ通水の場合は調整槽2における単位時間当たりの水位増加量から算出するものでも良い。もしくは調整槽2が連続通水の場合は、調整槽2の貯留量変化と調整槽からの排出流量の和から、調整槽2へ流入する排水の流量を算出しても良い。 The third flow rate measuring unit 8, which measures the flow rate of wastewater flowing into the equalization tank 2, may be a flow meter, or, if the equalization tank 2 is a batch-flow tank, it may be calculated from the increase in water level per unit time in the equalization tank 2. Alternatively, if the equalization tank 2 is a continuous-flow tank, the flow rate of wastewater flowing into the equalization tank 2 may be calculated from the sum of the change in storage volume in the equalization tank 2 and the discharge flow rate from the equalization tank.

このようにして求めた排水処理流入部のTOC濃度(推定値B)と、第2流量測定部10が測定した排水処理流入部の流量から、排水負荷(kg-TOC/day)を上記の式1にて推定する。 The wastewater load (kg-TOC/day) is estimated using the above formula 1 from the TOC concentration (estimated value B) at the wastewater treatment inlet determined in this way and the flow rate at the wastewater treatment inlet measured by the second flow rate measurement unit 10.

次に、図3に示すように、調整槽1と排水処理設備3との間に、調整槽2A、2Bが並列に設けられ、調整槽2Bから調整槽1へ排水が返送されている場合について考える。調整槽1から流出した排水は、調整槽2A又は2Bに流入する。調整槽2Aから流出した排水は、排水処理設備3に流入する。調整槽2Bから流出した排水は、調整槽1へ返送される。 Next, as shown in Figure 3, consider the case where equalization tanks 2A and 2B are installed in parallel between equalization tank 1 and wastewater treatment equipment 3, and wastewater is returned from equalization tank 2B to equalization tank 1. Wastewater flowing out of equalization tank 1 flows into equalization tank 2A or 2B. Wastewater flowing out of equalization tank 2A flows into wastewater treatment equipment 3. Wastewater flowing out of equalization tank 2B is returned to equalization tank 1.

第4流量測定部13は、調整槽2Bへ流入する排水の流量を測定するものであり、流量計で測定しても良いし、調整槽2Bにおける単位時間当たりの水位増加量から算出しても良い。第5流量測定部15は、調整槽2Bから調整槽1へ返送される排水の流量を測定するものであり、流量計で測定しても良いし、調整槽2Bにおける単位時間当たりの水位減少量から算出しても良い。 The fourth flow rate measurement unit 13 measures the flow rate of wastewater flowing into the adjustment tank 2B, and may be measured using a flow meter or calculated from the increase in water level per unit time in the adjustment tank 2B. The fifth flow rate measurement unit 15 measures the flow rate of wastewater returned from the adjustment tank 2B to the adjustment tank 1, and may be measured using a flow meter or calculated from the decrease in water level per unit time in the adjustment tank 2B.

この場合、調整槽1へ排水を返送する調整槽2Bはバッチ通水であることが条件であり、調整槽1および調整槽2Aは連続通水、バッチ通水いずれでも良い。調整槽2Aは、1槽以上設けられており、複数の調整槽2Aが並列に配置されていてもよい。 In this case, the condition is that the adjustment tank 2B, which returns wastewater to the adjustment tank 1, is a batch water supply tank, and the adjustment tank 1 and adjustment tank 2A may be either continuous water supply tanks or batch water supply tanks. One or more adjustment tanks 2A may be provided, and multiple adjustment tanks 2A may be arranged in parallel.

まず、調整槽1の上流側で測定したTOC濃度及び第4流量測定部13が測定した流量から、以下の推定方法(3)―3により、調整槽2B内の排水のTOC濃度(推定値C)を推定する。 First, the TOC concentration (estimated value C) of the wastewater in the equalization tank 2B is estimated using the following estimation method (3)-3 from the TOC concentration measured upstream of the equalization tank 1 and the flow rate measured by the fourth flow rate measurement unit 13.

推定方法(3)-3
調整槽2Bに流入した全TOC重量(g)を調整槽2Bに流入した全水量(m)で除することで、調整槽2BのTOC濃度(mg/L)を推定する。
Estimation method (3)-3
The TOC concentration (mg/L) in the adjustment tank 2B is estimated by dividing the total TOC weight (g) flowing into the adjustment tank 2B by the total amount of water (m 3 ) flowing into the adjustment tank 2B.

次に、上記のようにして求めた調整槽2BのTOC濃度(推定値C)と、第5流量測定部15が測定した流量と、調整槽1の上流側で測定したTOC濃度および流量から、調整槽1出口のTOC濃度(推定値D)を推定する。調整槽1が連続通水の場合は推定方法(2)-3、調整槽1がバッチ通水の場合は推定方法(3)-4により推定する。 Next, the TOC concentration at the outlet of the adjustment tank 1 (estimated value D) is estimated from the TOC concentration in the adjustment tank 2B obtained as described above (estimated value C), the flow rate measured by the fifth flow rate measurement unit 15, and the TOC concentration and flow rate measured upstream of the adjustment tank 1. If the adjustment tank 1 is continuously flowing, estimation method (2)-3 is used; if the adjustment tank 1 is batch-flowing, estimation method (3)-4 is used.

推定方法(2)-3
調整槽1の上流側で測定したTOC濃度及び流量と、調整槽2BのTOC濃度(推定値C)と、調整槽2Bから調整槽1に流入する流量とから、完全混合槽モデルを用いて調整槽1に流入した排水濃度の変化を推定し、調整槽1出口のTOC濃度(mg/L)を推定する。
Estimation method (2)-3
Using the TOC concentration and flow rate measured upstream of the adjustment tank 1, the TOC concentration (estimated value C) in the adjustment tank 2B, and the flow rate flowing from the adjustment tank 2B into the adjustment tank 1, the change in the concentration of the wastewater flowing into the adjustment tank 1 is estimated using a complete mixing tank model, and the TOC concentration (mg/L) at the outlet of the adjustment tank 1 is estimated.

推定方法(3)-4
調整槽1に流入した全TOC重量(g)を、調整槽1に流入した全水量(m)で除することで、調整槽1出口のTOC濃度(mg/L)を推定する。全TOC重量及び全水量は、調整槽1の上流側で測定したTOC重量及び水量に、調整槽2Bから返送されたTOC重量及び水量をそれぞれ加算することで算出する。
Estimation method (3)-4
The TOC concentration (mg/L) at the outlet of adjustment tank 1 is estimated by dividing the total TOC weight (g) that flowed into adjustment tank 1 by the total water volume (m 3 ) that flowed into adjustment tank 1. The total TOC weight and total water volume are calculated by adding the TOC weight and water volume measured upstream of adjustment tank 1 to the TOC weight and water volume returned from adjustment tank 2B, respectively.

次に、上記のようにして求めた調整槽1出口のTOC濃度(推定値D)と、調整槽2Aに流入する流量から、排水処理流入部(調整槽2Aの出口)のTOC濃度(推定値E)を推定する。調整槽2Aが連続通水の場合は推定方法(1)-3又は(2)-4、バッチ通水の場合は推定方法(3)-5にて排水処理流入部のTOC濃度(推定値E)を推定する。 Next, the TOC concentration (estimated value E) at the wastewater treatment inlet (outlet of adjustment tank 2A) is estimated from the TOC concentration (estimated value D) at the outlet of adjustment tank 1 obtained as described above and the flow rate into adjustment tank 2A. If adjustment tank 2A is continuously flowing, the TOC concentration (estimated value E) at the wastewater treatment inlet is estimated using estimation method (1)-3 or (2)-4; if it is batch flow, estimation method (3)-5.

推定方法(1)-3
TOC濃度(推定値D)を調整槽2Aでの滞留時間に近い時間で移動平均化することで排水処理流入部のTOC濃度(mg/L)を推定する。
Estimation method (1)-3
The TOC concentration (estimated value D) is averaged over a period close to the residence time in the adjustment tank 2A to estimate the TOC concentration (mg/L) at the inlet of the wastewater treatment system.

推定方法(2)-4
TOC濃度(推定値D)と調整槽2Aに流入する流量から、完全混合槽モデルを用いて調整槽2Aに流入した排水濃度の変化を推定し、排水処理流入部のTOC濃度(mg/L)を推定する。
Estimation method (2)-4
From the TOC concentration (estimated value D) and the flow rate flowing into the adjustment tank 2A, the change in the concentration of the wastewater flowing into the adjustment tank 2A is estimated using a complete mixing tank model, and the TOC concentration (mg/L) at the wastewater treatment inlet is estimated.

推定方法(3)-5
調整槽2Aに流入した全TOC重量(g)を調整槽2Aに流入した全水量(m)で除することで排水処理流入部のTOC濃度(mg/L)を推定する。
Estimation method (3)-5
The TOC concentration (mg/L) at the wastewater treatment inlet is estimated by dividing the total TOC weight (g) flowing into the adjustment tank 2A by the total amount of water (m 3 ) flowing into the adjustment tank 2A.

このようにして求めた排水処理流入部のTOC濃度(推定値E)と、第2流量測定部10が測定した排水処理流入部の流量から、排水負荷(kg-TOC/day)を上記の式1にて推定する。 The wastewater load (kg-TOC/day) is estimated using the above formula 1 from the TOC concentration (estimated value E) at the wastewater treatment inlet determined in this way and the flow rate at the wastewater treatment inlet measured by the second flow rate measurement unit 10.

本実施形態によれば、調整槽1の上流側の汚濁負荷(又は汚濁負荷と相関する項目)と、調整槽へ流入する排水の流量と、排水処理設備へ流入する排水の流量とをそれぞれ測定し、これらを用いて、排水処理流入部の排水負荷を推定する。この推定値から、排水処理への流入量を制御したり、高負荷排水を高負荷調整槽(図4~図14参照)へ振り分けたりすることで、排水処理を安定化させることができる。 In this embodiment, the pollution load (or items correlated with the pollution load) upstream of the adjustment tank 1, the flow rate of wastewater flowing into the adjustment tank, and the flow rate of wastewater flowing into the wastewater treatment facility are measured, and these are used to estimate the wastewater load at the wastewater treatment inlet. Based on these estimated values, the amount of inflow to the wastewater treatment facility can be controlled, or high-load wastewater can be allocated to a high-load adjustment tank (see Figures 4 to 14), thereby stabilizing wastewater treatment.

推定した排水負荷に閾値を設け、排水負荷が閾値以上の場合には高負荷調整槽へ振り分け、閾値未満の場合には通常の調整槽へ振り分ける。閾値は後段の排水処理設備の設計基準値以下とするなど、排水処理が破綻しないような条件で設定する。現在の排水負荷に加え、数時間前に通過した排水の排水負荷を閾値の判定に加えてもよい。例えば、現在の排水負荷が設定した閾値A以上となり、かつ数時間前の排水負荷が設定した閾値B以上となった場合に高負荷調整槽へ振り分けるようにしてもよい。現場の状況に合わせて、閾値を予め設定することが望ましい。 A threshold is set for the estimated wastewater load, and if the wastewater load is above the threshold, it is distributed to a high-load adjustment tank, and if it is below the threshold, it is distributed to a normal adjustment tank. The threshold is set under conditions that will prevent wastewater treatment from failing, such as being below the design standard value of the downstream wastewater treatment equipment. In addition to the current wastewater load, the wastewater load of wastewater that passed through several hours ago can also be used to determine the threshold. For example, if the current wastewater load is above set threshold A and the wastewater load from several hours ago was above set threshold B, it may be distributed to the high-load adjustment tank. It is desirable to set thresholds in advance to suit the situation on site.

高負荷調整槽から送水して排水に混合する際は、排水処理流入部の排水負荷に高負荷調整槽から送水する排水負荷が加わった時に、設定した閾値未満になる場合は高負荷調整槽から送水する。逆に加算した負荷が閾値以上になる場合は、送水せず高負荷調整槽に貯留したままとする。 When water is sent from the high-load adjustment tank to be mixed with wastewater, if the wastewater load at the wastewater treatment inlet is added to the wastewater load sent from the high-load adjustment tank and the combined load is below the set threshold, water will be sent from the high-load adjustment tank. Conversely, if the combined load exceeds the threshold, the water will not be sent and will remain stored in the high-load adjustment tank.

高負荷調整槽への振り分け方法および高負荷調整槽からの送水方法の具体例を以下に説明する。 Specific examples of how water is distributed to the high-load adjustment tank and how it is sent from the high-load adjustment tank are explained below.

図4は、図1に示す排水処理システムに高負荷調整槽12を設けた構成を示す。図4に示す構成では、高負荷調整槽12は、調整槽1と並列に配置される。移送ポンプ11により送水される排水は、調整槽1の上流側で分岐し、バルブ17A、17Bの開閉を制御することで、調整槽1と高負荷調整槽12のどちらに流入させるか切り替えることができる。 Figure 4 shows a configuration in which a high-load adjustment tank 12 is installed in the wastewater treatment system shown in Figure 1. In the configuration shown in Figure 4, the high-load adjustment tank 12 is arranged in parallel with the adjustment tank 1. The wastewater delivered by the transfer pump 11 branches upstream of the adjustment tank 1, and by controlling the opening and closing of valves 17A and 17B, it is possible to switch whether the wastewater flows into the adjustment tank 1 or the high-load adjustment tank 12.

演算部6は、汚濁負荷測定部4が測定したTOC濃度、及び第1流量測定部5が測定した流量を取得し、上記の推定方法(1)-1、(2)-1、(3)-1のいずれかにより排水処理流入部のTOC濃度を推定する。また、演算部6は、推定したTOC濃度、及び第2流量測定部10が測定した流量を用いて、排水処理流入部の排水負荷を推定し、排水処理設備3へ流入しても問題ないか否かを判断する。 The calculation unit 6 acquires the TOC concentration measured by the pollution load measurement unit 4 and the flow rate measured by the first flow rate measurement unit 5, and estimates the TOC concentration at the wastewater treatment inlet using one of the estimation methods (1)-1, (2)-1, or (3)-1 described above. The calculation unit 6 also uses the estimated TOC concentration and the flow rate measured by the second flow rate measurement unit 10 to estimate the wastewater load at the wastewater treatment inlet, and determines whether it is safe for the wastewater to flow into the wastewater treatment facility 3.

通常時、排水は調整槽1へ流入する。演算部6は、推定した排水負荷が所定の閾値以上であり、排水処理が破綻し得ると判断した場合、バルブ17Aを閉、バルブ17Bを開とし、排水を高負荷調整槽12へ振り分ける。排水の流入先を高負荷調整槽12へ切り替えた後も、移送ポンプ20により調整槽1から排水処理設備3へ排水が送水され、演算部6は排水処理流入部のTOC濃度の推定及び排水負荷の推定を継続して行う。 Under normal circumstances, wastewater flows into adjustment tank 1. If the calculation unit 6 determines that the estimated wastewater load is above a predetermined threshold and that the wastewater treatment may fail, it closes valve 17A and opens valve 17B, and distributes the wastewater to high-load adjustment tank 12. Even after the wastewater inflow destination is switched to high-load adjustment tank 12, the transfer pump 20 continues to transport the wastewater from adjustment tank 1 to wastewater treatment equipment 3, and the calculation unit 6 continues to estimate the TOC concentration at the wastewater treatment inlet and the wastewater load.

その後、推定される排水負荷が閾値未満になると、排水の流入先を高負荷調整槽12から調整槽1へ切り替える。また、演算部6は、移送ポンプ19を制御し、排水処理が破綻しないように、高負荷調整槽12から排水処理設備3へ高負荷排水を送水するタイミングを調整する。演算部6は、調整槽1の下流側で調整槽1からの排水に高負荷調整槽12からの排水を混合(合流)させた場合の排水負荷が所定の閾値未満となる場合、高負荷調整槽12から送水させる。混合後の排水負荷が閾値以上の場合、高負荷調整槽12から送水せず、貯留したままとする。 After that, when the estimated wastewater load falls below the threshold, the wastewater inflow destination is switched from the high-load adjustment tank 12 to the adjustment tank 1. The calculation unit 6 also controls the transfer pump 19 to adjust the timing of sending high-load wastewater from the high-load adjustment tank 12 to the wastewater treatment equipment 3 so as not to cause the wastewater treatment to fail. If the wastewater load when the wastewater from the high-load adjustment tank 12 is mixed (confluent) with the wastewater from the adjustment tank 1 downstream of the adjustment tank 1 falls below a predetermined threshold, the calculation unit 6 sends water from the high-load adjustment tank 12. If the wastewater load after mixing is equal to or greater than the threshold, the water is not sent from the high-load adjustment tank 12 and remains stored.

演算部6が、バルブ17A、17Bの開閉のタイミングをモニタの画面などに表示し、作業員が表示に従って手動でバルブ17A、17Bの開閉制御を行ってもよい。同様に、演算部6が、移送ポンプ19,20の送水タイミングがわかるようにモニタの画面などに表示し、作業員が表示に従って手動でポンプを動かしてもよい。また、移送ポンプ19,20の代わりに合流点の下流側に移送ポンプを設置して、調整槽1および高負荷調整槽からの排水が合流する手前に切り替えバルブを設けることで、1台の移送ポンプで運転できるようにしても良い。 The calculation unit 6 may display the opening and closing timing of valves 17A and 17B on a monitor screen or the like, and an operator may manually control the opening and closing of valves 17A and 17B in accordance with the display. Similarly, the calculation unit 6 may display the water supply timing of transfer pumps 19 and 20 on a monitor screen or the like so that the operator can see the timing, and an operator may manually operate the pumps in accordance with the display. Alternatively, instead of transfer pumps 19 and 20, a transfer pump may be installed downstream of the confluence, and a switching valve may be provided just before the confluence of wastewater from adjustment tank 1 and the high-load adjustment tank, allowing operation with a single transfer pump.

図4に示す構成では、高負荷調整槽12内の排水を排水処理設備3へ送水する構成について説明したが、図5に示すように、高負荷調整槽12内の排水を調整槽1へ送水してもよい。 In the configuration shown in Figure 4, the wastewater in the high-load adjustment tank 12 is sent to the wastewater treatment equipment 3, but as shown in Figure 5, the wastewater in the high-load adjustment tank 12 may also be sent to the adjustment tank 1.

図6に示す構成では、排水の汚濁負荷は考慮せずに排水を調整槽1および調整槽1´に任意に送水する。調整槽2へ排水を送水する時はバルブ7Aを開、バルブ7Bを閉とし、調整槽2´へ排水を送水する時はバルブ7Aを閉、バルブ7Bを開とする。また、調整槽2および2´のうち、排水を送水していない調整槽から排水処理設備3へ排水を送水する。演算部6は排水負荷が高く、排水処理が破綻し得ると判断した場合は、移送ポンプ19´および20´を制御し、排水処理が破綻しない排水負荷(TOC濃度×流量)となるように、調整槽1および調整槽1’から送水される排水の流量を調整する。演算部6が、移送ポンプ19´,20´の送水量がわかるようにモニタの画面などに表示し、作業員が表示に従って手動でポンプを動かしてもよい。また移送ポンプ19´,20´の代わりに合流点の下流側に移送ポンプを設置して、調整槽1および高負荷調整槽12からの排水が合流する手前に切り替えバルブを設けることで、1台の移送ポンプで運転できるようにしても良い。 In the configuration shown in Figure 6, wastewater is sent to adjustment tank 1 and adjustment tank 1' at will without considering the wastewater pollution load. When sending wastewater to adjustment tank 2, valve 7A is opened and valve 7B is closed. When sending wastewater to adjustment tank 2', valve 7A is closed and valve 7B is opened. In addition, of adjustment tanks 2 and 2', wastewater is sent to wastewater treatment equipment 3 from the adjustment tank that is not sending wastewater. If the calculation unit 6 determines that the wastewater load is high and the wastewater treatment may fail, it controls transfer pumps 19' and 20' to adjust the flow rate of wastewater sent from adjustment tank 1 and adjustment tank 1' so that the wastewater load (TOC concentration x flow rate) is such that the wastewater treatment will not fail. The calculation unit 6 displays the water supply rates of transfer pumps 19' and 20' on a monitor screen or the like, so that operators can operate the pumps manually according to the display. Alternatively, instead of transfer pumps 19' and 20', a transfer pump can be installed downstream of the confluence, and a switching valve can be installed just before the wastewater from adjustment tank 1 and high-load adjustment tank 12 join, allowing operation with a single transfer pump.

図7は、図2に示す排水処理システムの調整槽2と並列に高負荷調整槽12を設けた構成を示す。バルブ7A、7Bの開閉を制御することで、調整槽1から送水される排水を、調整槽2と高負荷調整槽12のどちらに流入させるか切り替えることができる。 Figure 7 shows a configuration in which a high-load adjustment tank 12 is installed in parallel with the adjustment tank 2 of the wastewater treatment system shown in Figure 2. By controlling the opening and closing of valves 7A and 7B, it is possible to switch whether the wastewater delivered from adjustment tank 1 flows into adjustment tank 2 or high-load adjustment tank 12.

演算部6は、汚濁負荷測定部4が測定したTOC濃度、及び第1流量測定部5が測定した流量を取得し、上記の推定方法(1)-1、(2)-1、(3)-1のいずれかにより調整槽1出口のTOC濃度を推定する。 The calculation unit 6 acquires the TOC concentration measured by the pollution load measurement unit 4 and the flow rate measured by the first flow rate measurement unit 5, and estimates the TOC concentration at the outlet of the equalization tank 1 using one of the above estimation methods (1)-1, (2)-1, or (3)-1.

演算部6は、推定した調整槽1出口のTOC濃度と、第3流量測定部8が測定した調整槽2に流入する排水の流量を用いて、上記の推定方法(1)-2、(2)-2、(3)-2のいずれかにより、排水処理流入部のTOC濃度を推定する。また、演算部6は、推定した排水処理流入部のTOC濃度と、第2流量測定部10が測定した排水処理流入部の流量から、上記の式1により、排水処理流入部の排水負荷を推定する。 The calculation unit 6 estimates the TOC concentration at the wastewater treatment inlet using one of the estimation methods (1)-2, (2)-2, or (3)-2 above, using the estimated TOC concentration at the outlet of the equalization tank 1 and the flow rate of wastewater flowing into the equalization tank 2 measured by the third flow rate measurement unit 8. The calculation unit 6 also estimates the wastewater load at the wastewater treatment inlet using Equation 1 above, based on the estimated TOC concentration at the wastewater treatment inlet and the flow rate at the wastewater treatment inlet measured by the second flow rate measurement unit 10.

通常時、調整槽1からの排水は調整槽2へ流入する。演算部6は、推定した排水負荷が所定の閾値以上であり、排水処理が破綻し得ると判断した場合は、バルブ7Aを閉、バルブ7Bを開とし、調整槽1から送水された排水を高負荷調整槽12へ流入させる。排水の流入先を高負荷調整槽12へ切り替えた後も、移送ポンプ20により調整槽2から排水処理設備3へ排水が送水され、演算部6は、調整槽1出口のTOC濃度の推定、排水処理流入部のTOC濃度の推定及び排水負荷の推定を継続して行う。 Under normal circumstances, wastewater from adjustment tank 1 flows into adjustment tank 2. If the calculation unit 6 determines that the estimated wastewater load is above a predetermined threshold and that the wastewater treatment may fail, it closes valve 7A and opens valve 7B, allowing the wastewater delivered from adjustment tank 1 to flow into high-load adjustment tank 12. Even after the wastewater inflow destination is switched to high-load adjustment tank 12, the transfer pump 20 continues to deliver the wastewater from adjustment tank 2 to wastewater treatment equipment 3, and the calculation unit 6 continues to estimate the TOC concentration at the outlet of adjustment tank 1, the TOC concentration at the wastewater treatment inlet, and the wastewater load.

その後、推定される排水負荷が閾値未満になると、排水の流入先を高負荷調整槽12から調整槽2へ切り替える。また、演算部6は、移送ポンプ19を制御し、排水処理が破綻しないように、高負荷調整槽12から排水処理設備3へ高負荷排水を送水するタイミングを調整する。演算部6は、調整槽2からの排水に高負荷調整槽12からの排水を混合させた場合の排水負荷が所定の閾値未満の場合、高負荷調整槽12から送水させる。混合後の排水負荷が閾値以上の場合、高負荷調整槽12から送水せず、貯留したままとする。 After that, when the estimated wastewater load falls below the threshold, the wastewater inflow destination is switched from the high-load adjustment tank 12 to the adjustment tank 2. The calculation unit 6 also controls the transfer pump 19 to adjust the timing of sending high-load wastewater from the high-load adjustment tank 12 to the wastewater treatment equipment 3 so as not to cause the wastewater treatment to fail. If the wastewater load when the wastewater from the adjustment tank 2 is mixed with the wastewater from the high-load adjustment tank 12 is below a predetermined threshold, the calculation unit 6 sends water from the high-load adjustment tank 12. If the wastewater load after mixing is equal to or greater than the threshold, the water is not sent from the high-load adjustment tank 12 and remains stored.

図7の構成では、バルブ7A、7Bの開閉を制御して、調整槽1から送水される排水の流入先を切り替えていたが、図8に示すように、調整槽1から調整槽2へ送水する移送ポンプ18Aと、調整槽1から高負荷調整槽12へ送水する移送ポンプ18Bとを設け、移送ポンプ18A、18Bの発停を制御して、排水を調整槽2と高負荷調整槽12のどちらに流入させるか切り替えてもよい。演算部6が、移送ポンプ18A、18Bの発停のタイミングがわかるようにモニタの画面などに表示し、作業員が表示に従って手動でポンプを動かしてもよい。 In the configuration shown in Figure 7, the opening and closing of valves 7A and 7B was controlled to switch the destination of the wastewater delivered from adjustment tank 1. However, as shown in Figure 8, a transfer pump 18A that delivers water from adjustment tank 1 to adjustment tank 2 and a transfer pump 18B that delivers water from adjustment tank 1 to high-load adjustment tank 12 may be provided, and the on/off of transfer pumps 18A and 18B may be controlled to switch whether the wastewater is delivered to adjustment tank 2 or high-load adjustment tank 12. The calculation unit 6 may display the start/stop timing of transfer pumps 18A and 18B on a monitor screen or the like so that the operator can see the timing, and the operator may manually operate the pumps according to the display.

図7に示す構成では、排水負荷が低くなったタイミングで、高負荷調整槽12内の排水を排水処理設備3へ送水する構成について説明したが、図9に示すように、高負荷調整槽12内の排水を調整槽2へ送水してもよい。 In the configuration shown in Figure 7, the wastewater in the high-load adjustment tank 12 is sent to the wastewater treatment equipment 3 when the wastewater load decreases, but as shown in Figure 9, the wastewater in the high-load adjustment tank 12 may also be sent to the adjustment tank 2.

図9の構成では、バルブ7A、7Bの開閉を制御して、調整槽1から送水される排水の流入先を切り替えていたが、図10に示すように、調整槽1から調整槽2へ送水する移送ポンプ18Aと、調整槽1から高負荷調整槽12へ送水する移送ポンプ18Bとを設け、移送ポンプ18A、18Bの発停を制御して、調整槽1からの排水を調整槽2と高負荷調整槽12のどちらに流入させるか切り替えてもよい。 In the configuration shown in Figure 9, the opening and closing of valves 7A and 7B was controlled to switch the destination of the wastewater delivered from adjustment tank 1. However, as shown in Figure 10, a transfer pump 18A that delivers water from adjustment tank 1 to adjustment tank 2 and a transfer pump 18B that delivers water from adjustment tank 1 to high-load adjustment tank 12 may be provided, and the start and stop of transfer pumps 18A and 18B may be controlled to switch whether the wastewater from adjustment tank 1 flows into adjustment tank 2 or high-load adjustment tank 12.

図7~10に示す構成では、調整槽1の下流側において分岐し、排水負荷が所定値以上になると推定される排水を調整槽2と並列に配置した高負荷調整槽12に振り分ける。調整槽1の上流側で分岐して高負荷調整槽12に振り分けた場合、排水水質の変動が激しく高負荷調整槽12への振り分けが頻繁に行われることになるため、バルブ開閉や移送ポンプ発停の操作に関して、特に手動で操作する場合には運転対応に負荷がかかる可能性がある。従って、振り分け操作を簡略化することを目的とし、高負荷調整槽12への振り分けは調整槽1の下流側にて行うことが好ましい。 In the configurations shown in Figures 7 to 10, wastewater branching occurs downstream of the adjustment tank 1, and is distributed to the high-load adjustment tank 12, which is placed in parallel with the adjustment tank 2, when the wastewater load is estimated to exceed a predetermined value. If the wastewater branching occurs upstream of the adjustment tank 1 and is distributed to the high-load adjustment tank 12, the quality of the wastewater will fluctuate greatly and distribution to the high-load adjustment tank 12 will be frequent. This can place a burden on the operation of opening and closing valves and starting and stopping the transfer pump, especially when performed manually. Therefore, in order to simplify the distribution operation, it is preferable to distribute the wastewater to the high-load adjustment tank 12 downstream of the adjustment tank 1.

なお、図7~10における調整槽1のHRTは30分~60分であることが好ましい。HRT60分以下では調整槽1において水質が平準化される機能が低く、調整槽1の上流側・下流側のどちらで高負荷調整槽12に分岐させても、振り分ける頻度や効果に差が生じにくいと考えられる。従ってこの場合、調整槽1の下流側にて分岐して調整槽2および高負荷調整槽を並列配置で設けることで、水質の平準化や高負荷排水の振り分けを行うことが望ましい。 Note that the HRT of the adjustment tank 1 in Figures 7 to 10 is preferably between 30 and 60 minutes. At an HRT of 60 minutes or less, the ability of the adjustment tank 1 to level out water quality is low, and it is thought that there will be little difference in the frequency or effectiveness of distribution regardless of whether the water is branched to the high-load adjustment tank 12 upstream or downstream of the adjustment tank 1. Therefore, in this case, it is desirable to branch off downstream of the adjustment tank 1 and install the adjustment tank 2 and high-load adjustment tank in parallel to level out water quality and distribute high-load wastewater.

また、調整槽2のHRTは60分~30時間程度であることが好ましい。HRT60分以上であれば、水質は十分に平準化されると考えられるが、平準化されたにも拘わらず排水負荷が所定値を超えると推定される場合に、予め高負荷調整槽12へ振り分けることで排水処理を安定化することができる。一方、HRTが30時間を超えるような場合には排水負荷が所定値を超える可能性は低く、高負荷調整槽12へ排水を振り分ける必要がないと考えられる。 Furthermore, it is preferable that the HRT of the adjustment tank 2 is approximately 60 minutes to 30 hours. If the HRT is 60 minutes or more, it is believed that the water quality will be sufficiently equalized, but if it is estimated that the wastewater load will exceed a predetermined value despite equalization, the wastewater treatment can be stabilized by allocating the wastewater to the high-load adjustment tank 12 in advance. On the other hand, if the HRT is more than 30 hours, it is unlikely that the wastewater load will exceed the predetermined value, and it is believed that there is no need to allocate the wastewater to the high-load adjustment tank 12.

図11に示す構成では、排水の汚濁負荷は考慮せずに排水を調整槽2および調整槽2´に任意に送水する。調整槽2へ排水を送水する時はバルブ7Aを開、バルブ7Bを閉とし、調整槽2´へ排水を送水する時はバルブ7Aを閉、バルブ7Bを開とする。また、調整槽2および調整槽2´のうち、排水を送水していない調整槽から排水処理設備3へ排水を送水する。もしくは図12に示すように、調整槽1から調整槽2へ送水する移送ポンプ18Aと、調整槽2から調整槽2´へ送水する移送ポンプ18Bとを設け、ポンプの発停を切り分けても良い。演算部6は排水負荷が高く、排水処理が破綻し得ると判断した場合は、移送ポンプ19´、20´を制御し、排水処理が破綻しない排水負荷(TOC濃度×流量)となるように、調整槽2および調整槽2’から送水される排水の流量を調整する。 In the configuration shown in Figure 11, wastewater is sent to adjustment tank 2 and adjustment tank 2' at will without considering the wastewater pollution load. When sending wastewater to adjustment tank 2, valve 7A is opened and valve 7B is closed. When sending wastewater to adjustment tank 2', valve 7A is closed and valve 7B is opened. Furthermore, of adjustment tanks 2 and 2', wastewater is sent to the wastewater treatment equipment 3 from the adjustment tank that is not sending wastewater. Alternatively, as shown in Figure 12, transfer pump 18A that sends water from adjustment tank 1 to adjustment tank 2 and transfer pump 18B that sends water from adjustment tank 2 to adjustment tank 2' may be provided, and the pumps may be started and stopped separately. If calculation unit 6 determines that the wastewater load is high and that wastewater treatment may fail, it controls transfer pumps 19' and 20' to adjust the flow rate of wastewater sent from adjustment tank 2 and adjustment tank 2' so that the wastewater load (TOC concentration x flow rate) is such that wastewater treatment will not fail.

図13は、図3に示す排水処理システムの調整槽2A、2Bをそれぞれ調整槽2、高負荷調整槽12とした構成を示す。バルブ7A、7Bの開閉を制御することで、調整槽1から送水される排水を、調整槽2と高負荷調整槽12のどちらに流入させるか切り替えることができる。 Figure 13 shows a configuration in which the adjustment tanks 2A and 2B of the wastewater treatment system shown in Figure 3 have been replaced with adjustment tank 2 and high-load adjustment tank 12, respectively. By controlling the opening and closing of valves 7A and 7B, it is possible to switch whether wastewater delivered from adjustment tank 1 flows into adjustment tank 2 or high-load adjustment tank 12.

演算部6は、汚濁負荷測定部4が測定したTOC濃度、及び第4流量測定部13が測定した高負荷調整槽12へ流入する排水の流量を取得し、上記の推定方法(3)-3により高負荷調整槽12のTOC濃度を推定する。 The calculation unit 6 acquires the TOC concentration measured by the pollution load measurement unit 4 and the flow rate of wastewater flowing into the high-load adjustment tank 12 measured by the fourth flow rate measurement unit 13, and estimates the TOC concentration in the high-load adjustment tank 12 using the estimation method (3)-3 described above.

演算部6は、推定した高負荷調整槽12のTOC濃度、第5流量測定部15が測定した流量と、汚濁負荷測定部4が測定したTOC濃度と、第1流量測定部5が測定した流量を用いて、上記の推定方法(2)-3又は(3)-4により、調整槽1出口のTOC濃度を推定する。 The calculation unit 6 uses the estimated TOC concentration in the high-load adjustment tank 12, the flow rate measured by the fifth flow rate measurement unit 15, the TOC concentration measured by the pollution load measurement unit 4, and the flow rate measured by the first flow rate measurement unit 5 to estimate the TOC concentration at the outlet of the adjustment tank 1 using the estimation method (2)-3 or (3)-4 described above.

次に、演算部6は、推定した調整槽1出口のTOC濃度と、第3流量測定部8が測定した調整槽2に流入する排水の流量とを用いて、上記の推定方法(1)-3、(2)-4、(3)-5のいずれかにより、排水処理流入部(調整槽2出口)のTOC濃度を推定する。 Next, the calculation unit 6 uses the estimated TOC concentration at the outlet of the equalization tank 1 and the flow rate of the wastewater flowing into the equalization tank 2 measured by the third flow rate measurement unit 8 to estimate the TOC concentration at the wastewater treatment inlet (outlet of the equalization tank 2) using one of the above estimation methods (1)-3, (2)-4, or (3)-5.

そして、演算部6は、推定した排水処理流入部のTOC濃度と、第2流量測定部10が測定した排水処理流入部の流量から、排水負荷を上記の式1により推定する。 Then, the calculation unit 6 estimates the wastewater load using the above formula 1 from the estimated TOC concentration at the wastewater treatment inlet and the flow rate at the wastewater treatment inlet measured by the second flow rate measurement unit 10.

通常時、調整槽1からの排水は調整槽2へ流入する。演算部6は、推定した排水負荷が所定の閾値以上であり、排水処理が破綻し得ると判断した場合は、バルブ7Aを閉、バルブ7Bを開とし、調整槽1から送水された排水を高負荷調整槽12へ流入させる。排水の流入先を高負荷調整槽12へ切り替えた後も、移送ポンプ20により調整槽2から排水処理設備3へ排水が送水され、演算部6は、排水負荷の推定を継続して行う。 Under normal conditions, wastewater from adjustment tank 1 flows into adjustment tank 2. If calculation unit 6 determines that the estimated wastewater load is above a predetermined threshold and that wastewater treatment may fail, it closes valve 7A and opens valve 7B, allowing the wastewater delivered from adjustment tank 1 to flow into high-load adjustment tank 12. Even after the wastewater inflow destination is switched to high-load adjustment tank 12, transfer pump 20 continues to deliver wastewater from adjustment tank 2 to wastewater treatment equipment 3, and calculation unit 6 continues to estimate the wastewater load.

その後、推定される排水負荷が閾値未満になると、排水の流入先を高負荷調整槽12から調整槽2へ切り替える。また、演算部6は、移送ポンプ19を制御し、排水処理が破綻しないように、高負荷調整槽12から調整槽1へ高負荷排水を送水するタイミングを調整する。演算部6は、高負荷調整槽12からの排水を調整槽1へ返送した場合の排水負荷が所定の閾値未満の場合、高負荷調整槽12から調整槽1へ送水させる。返送により排水負荷が閾値以上となる場合、高負荷調整槽12から送水せず、貯留したままとする。 After that, when the estimated wastewater load falls below the threshold, the wastewater inflow destination is switched from the high-load adjustment tank 12 to the adjustment tank 2. The calculation unit 6 also controls the transfer pump 19 to adjust the timing of sending high-load wastewater from the high-load adjustment tank 12 to the adjustment tank 1 so as not to cause the wastewater treatment to fail. If the wastewater load when the wastewater from the high-load adjustment tank 12 is returned to the adjustment tank 1 is below a predetermined threshold, the calculation unit 6 sends water from the high-load adjustment tank 12 to the adjustment tank 1. If the wastewater load becomes equal to or exceeds the threshold due to the return, the water is not sent from the high-load adjustment tank 12 and remains stored.

図13の構成では、バルブ7A、7Bの開閉を制御して、調整槽1から送水される排水の流入先を切り替えていたが、図14に示すように、調整槽1から調整槽2へ送水する移送ポンプ18Aと、調整槽1から高負荷調整槽12へ送水する移送ポンプ18Bとを設け、移送ポンプ18A、18Bの発停を制御して、調整槽1からの排水を調整槽2と高負荷調整槽12のどちらに流入させるか切り替えてもよい。 In the configuration shown in Figure 13, the opening and closing of valves 7A and 7B was controlled to switch the destination of the wastewater sent from adjustment tank 1. However, as shown in Figure 14, a transfer pump 18A is provided to send water from adjustment tank 1 to adjustment tank 2, and a transfer pump 18B is provided to send water from adjustment tank 1 to high-load adjustment tank 12. By controlling the start and stop of transfer pumps 18A and 18B, it is possible to switch whether the wastewater from adjustment tank 1 flows into adjustment tank 2 or high-load adjustment tank 12.

上記のように構成された本実施形態によれば、予め設定した閾値以上の高負荷排水を高負荷調整槽へ振り分けることで、後段の排水処理の排水負荷が設定値を超過しないようにできる。高負荷調整槽に振り分けた排水については、設定した閾値を超えないように原水に混合することで、後段の排水処理の排水負荷が設定値を超過しないようにしつつ処理することができる。これにより排水処理の安定化が期待できる。 In this embodiment configured as described above, high-load wastewater above a preset threshold is diverted to the high-load adjustment tank, preventing the wastewater load in the subsequent wastewater treatment stage from exceeding the set value. By mixing the wastewater diverted to the high-load adjustment tank with raw water so that it does not exceed the set threshold, it can be treated while preventing the wastewater load in the subsequent wastewater treatment stage from exceeding the set value. This is expected to stabilize wastewater treatment.

上記実施形態では、排水処理流入部の汚濁負荷の推定、排水処理流入部の排水負荷の推定等の演算を演算部6が行う構成について説明したが、演算部6は1台のコンピュータで構成されていてもよいし、複数台のコンピュータで分散処理するものであってもよい。 In the above embodiment, a configuration was described in which the calculation unit 6 performs calculations such as estimating the pollution load at the inlet of the wastewater treatment plant and estimating the wastewater load at the inlet of the wastewater treatment plant. However, the calculation unit 6 may be configured as a single computer, or may perform distributed processing across multiple computers.

なお、本発明は上記実施形態そのままに限定されるものではなく、実施段階ではその要旨を逸脱しない範囲で構成要素を変形して具体化できる。また、上記実施形態に開示されている複数の構成要素の適宜な組み合わせにより、種々の発明を形成できる。例えば、実施形態に示される全構成要素から幾つかの構成要素を削除してもよい。さらに、異なる実施形態にわたる構成要素を適宜組み合わせてもよい。 The present invention is not limited to the above-described embodiments, and can be embodied by modifying the components within the scope of the spirit of the invention when implemented. Furthermore, various inventions can be created by appropriately combining multiple components disclosed in the above-described embodiments. For example, some components may be omitted from all of the components shown in the embodiments. Furthermore, components from different embodiments may be appropriately combined.

1,2,2´ 調整槽
3 排水処理設備
4 汚濁負荷測定部
5 第1流量測定部
6 演算部
8 第3流量測定部
10 第2流量測定部
11,19,19´,20,20´ 移送ポンプ
12 高負荷調整槽
13 第4流量測定部
15 第5流量測定部
1, 2, 2' Adjustment tank 3 Wastewater treatment equipment 4 Pollutant load measurement unit 5 First flow rate measurement unit 6 Calculation unit 8 Third flow rate measurement unit 10 Second flow rate measurement unit 11, 19, 19', 20, 20' Transfer pump 12 High load adjustment tank 13 Fourth flow rate measurement unit 15 Fifth flow rate measurement unit

Claims (5)

排水を調整槽に流入し、前記調整槽から排水処理設備へ送水する排水処理方法であって、
排水負荷に関する水質項目、前記調整槽へ流入する排水の流量、および前記排水処理設備へ流入する排水の流量を連続的または定期的に測定し、測定値に基づいて予め設定した演算式にて前記排水処理設備への排水流入部(排水処理流入部)の排水負荷を推定し、
推定した前記排水負荷が所定の閾値未満の場合、前記排水を前記調整槽に供給し、
推定した前記排水負荷が前記閾値以上の場合、前記排水を前記調整槽の上流側の排水分岐位置にて分岐して高負荷調整槽に貯留する、排水処理方法。
A wastewater treatment method in which wastewater flows into an adjustment tank and is sent from the adjustment tank to wastewater treatment equipment,
The water quality items related to the wastewater load, the flow rate of the wastewater flowing into the adjustment tank, and the flow rate of the wastewater flowing into the wastewater treatment facility are continuously or periodically measured, and the wastewater load at the wastewater inlet (wastewater treatment inlet) to the wastewater treatment facility is estimated using a predetermined calculation formula based on the measured values;
If the estimated wastewater load is less than a predetermined threshold, the wastewater is supplied to the adjustment tank;
When the estimated wastewater load is equal to or greater than the threshold value, the wastewater is branched at a wastewater branch position upstream of the adjustment tank and stored in a high-load adjustment tank.
前記排水負荷に関する水質項目は、前記排水の汚濁負荷又は汚濁負荷と相関する項目を含み、前記汚濁負荷はTOC濃度、COD濃度及びSS濃度のいずれかを含む、請求項1に記載の排水処理方法。 The wastewater treatment method according to claim 1 , wherein the water quality items related to the wastewater load include a pollution load of the wastewater or an item correlated with the pollution load, and the pollution load includes any one of a TOC concentration, a COD concentration, and an SS concentration . 前記高負荷調整槽から送水して前記排水分岐位置より下流側に合流させたときの前記排水負荷が所定の閾値以下になる場合は、前記高負荷調整槽から送水を行う、請求項1に記載の排水処理方法。 The wastewater treatment method of claim 1, wherein water is fed from the high-load adjustment tank if the wastewater load when fed from the high-load adjustment tank and joined downstream of the wastewater branch position is equal to or less than a predetermined threshold. 前記高負荷調整槽から送水して、前記調整槽の下流側に合流させる、請求項3に記載の排水処理方法。 The wastewater treatment method described in claim 3, wherein water is conveyed from the high-load adjustment tank and merged downstream of the adjustment tank. 前記高負荷調整槽から前記調整槽へ送水する、請求項3に記載の排水処理方法。 The wastewater treatment method described in claim 3, wherein water is pumped from the high-load adjustment tank to the adjustment tank.
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