JP7790466B2 - Method for removing organic dissolved substances in water/steam cycles - Google Patents
Method for removing organic dissolved substances in water/steam cyclesInfo
- Publication number
- JP7790466B2 JP7790466B2 JP2024066945A JP2024066945A JP7790466B2 JP 7790466 B2 JP7790466 B2 JP 7790466B2 JP 2024066945 A JP2024066945 A JP 2024066945A JP 2024066945 A JP2024066945 A JP 2024066945A JP 7790466 B2 JP7790466 B2 JP 7790466B2
- Authority
- JP
- Japan
- Prior art keywords
- water
- steam
- heat exchanger
- steam cycle
- boiler
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Active
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D63/00—Apparatus in general for separation processes using semi-permeable membranes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F22—STEAM GENERATION
- F22D—PREHEATING, OR ACCUMULATING PREHEATED, FEED-WATER FOR STEAM GENERATION; FEED-WATER SUPPLY FOR STEAM GENERATION; CONTROLLING WATER LEVEL FOR STEAM GENERATION; AUXILIARY DEVICES FOR PROMOTING WATER CIRCULATION WITHIN STEAM BOILERS
- F22D11/00—Feed-water supply not provided for in other main groups
Landscapes
- Engineering & Computer Science (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Thermal Sciences (AREA)
- Physics & Mathematics (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
- Treatment Of Water By Ion Exchange (AREA)
- Water Treatment By Sorption (AREA)
Description
本発明は水・蒸気サイクル中の有機系溶存物質の除去方法に関する。 The present invention relates to a method for removing organic dissolved substances from a water-steam cycle.
近年、工場で使用される蒸気の質に対する注目が高まっている。特に、飲料、食品分野では人体に対する化学物質の影響の低減、半導体工場では加湿蒸気の不純物の低減が必要となっている。 In recent years, there has been growing attention being paid to the quality of steam used in factories. In particular, in the beverage and food industries, there is a need to reduce the impact of chemicals on the human body, and in semiconductor factories, there is a need to reduce impurities in humidified steam.
カーボンニュートラルの観点から、効率的な熱交換ニーズも高く、近年は滴状凝縮を実現する有機薬剤(滴状凝縮促進剤)が利用されている。例えば、蒸気式の熱交換器の加熱効率向上を目的として、ポリアミン等の薬剤がボイラ給水又は蒸気に添加されることがある(特許文献1)。 From the perspective of carbon neutrality, there is a high need for efficient heat exchange, and in recent years, organic chemicals (droplet condensation promoters) that achieve dropwise condensation have been used. For example, chemicals such as polyamines are sometimes added to boiler feedwater or steam to improve the heating efficiency of steam heat exchangers (Patent Document 1).
これら薬剤の一部はドレン回収中に含まれ、補給水と共に再びボイラ給水となって系内を循環することになる。 Some of these chemicals are trapped in the recovered drain and, together with the makeup water, are recirculated within the system as boiler feed water.
火力発電プラントにおいては、復水処理装置として、復水脱塩装置のみの単独方式と、復水前置濾過装置と復水脱塩装置との組み合わせ方式が従来使用されている。この脱塩システムによれば、プラントの構成材料から発生し、復水中に微量存在する腐食生成物およびイオンの除去と、復水器の冷却水として使用される海水・淡水が万一漏洩した場合の海水成分の除去が行われる。 Conventionally, thermal power plants use two types of condensate treatment equipment: a standalone condensate demineralizer, and a combination of a condensate pre-filter and a condensate demineralizer. These demineralization systems remove trace amounts of corrosion products and ions generated by the plant's constituent materials and present in the condensate, as well as seawater components in the unlikely event of a leak of seawater or freshwater used as cooling water for the condenser.
ボイラから発生する蒸気の一部を熱交換器以外の蒸気使用箇所に直接供給する場合には、この蒸気中に含まれる有機薬剤を十分に除去することが必要となる。 If part of the steam generated by the boiler is directly supplied to a steam-using location other than a heat exchanger, it is necessary to thoroughly remove the organic chemicals contained in this steam.
本発明は、滴状凝縮促進剤等の添加による熱交換器の効率向上と、対象熱交換器を除いた水・蒸気サイクル系の有機系溶存物質の除去を両立させることができる、水・蒸気サイクル中の有機系溶存物質の除去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 method for removing organic dissolved substances in a water-steam cycle that can simultaneously improve the efficiency of the heat exchanger by adding a dropwise condensation promoter, etc., and remove organic dissolved substances from the water-steam cycle system excluding the target heat exchanger.
本発明の要旨は、次の通りである。 The gist of the present invention is as follows:
[1]熱交換器の上流で有機系薬品を添加する水・蒸気サイクル中の有機系溶存物質を除去する方法であって、
該熱交換器のドレン水の少なくとも一部を濾過装置に通して有機系溶存物質を除去する方法において、
該濾過装置として、イオン交換装置、活性炭濾過装置、RO膜装置及びNF膜装置の少なくとも一種よりなる機器が複数個並列に配置されており、
一部の該機器にドレン水を通し、薬品添加量またはセンサによる水質の測定値に基づいて濾過性能が低下したと判断された場合に通水を他の該機器に切替えることを特徴とする水・蒸気サイクル中の有機系溶存物質の除去方法。
[1] A method for removing organic dissolved substances in a water-steam cycle in which an organic chemical is added upstream of a heat exchanger, comprising:
In the method for removing organic dissolved substances by passing at least a portion of the drain water from the heat exchanger through a filtration device,
The filtration device is a plurality of devices each consisting of at least one of an ion exchange device, an activated carbon filtration device, an RO membrane device, and an NF membrane device, arranged in parallel;
A method for removing organic dissolved substances in a water-steam cycle, characterized in that drain water is passed through some of the equipment, and when it is determined that the filtration performance has decreased based on the amount of chemicals added or the water quality measured by a sensor, the water is switched to passing through other of the equipment.
[2]前記センサが、電気伝導率計、pH計、薬品濃度計、水晶振動子のいずれか1又は2以上であることを特徴とする[1]の水・蒸気サイクル中の有機系溶存物質の除去方法。 [2] The method for removing organic dissolved substances in a water-steam cycle according to [1], wherein the sensor is one or more of an electrical conductivity meter, a pH meter, a chemical concentration meter, and a quartz oscillator.
[3]前記センサの閾値またはトレンドのいずれかで、前記濾過装置を切り替えることを特徴とする[1]の水・蒸気サイクル中の有機系溶存物質の除去方法。 [3] The method for removing organic dissolved substances in a water-steam cycle according to [1], characterized in that the filtration device is switched based on either the threshold value or trend of the sensor.
[4]前記濾過装置内の濾材は、別設備での使用履歴があり、濾材を詰めたカートリッジまたは濾材のみを交換できることを特徴とする[1]の水・蒸気サイクル中の有機系溶存物質の除去方法。 [4] The method for removing organic dissolved substances in a water-steam cycle according to [1], characterized in that the filter material in the filtration device has a history of use in another facility, and the cartridge filled with the filter material or just the filter material can be replaced.
[5]前記機器の切換え作動信号を外部に発信し、運転管理者に該濾過装置の交換を促すことを特徴とする[1]の水・蒸気サイクル中の有機系溶存物質の除去方法。 [5] The method for removing organic dissolved substances in a water-steam cycle according to [1], characterized in that a switching activation signal for the equipment is transmitted to the outside, prompting the operation manager to replace the filtration device.
[6]前記濾過装置が、直前に薬品が添加される熱交換器の後段に設置されていることを特徴とする[1]の水・蒸気サイクル中の有機系溶存物質の除去方法。 [6] The method for removing organic dissolved substances in a water-steam cycle according to [1], characterized in that the filtration device is installed downstream of a heat exchanger to which chemicals are added immediately beforehand.
[7]熱交換器の上流で有機系薬品を添加する水・蒸気サイクル中の有機系溶存物質を除去する方法において、
該熱交換器のドレン水の少なくとも一部を電気脱イオン装置に通して有機系溶存物質を除去することを特徴とする水・蒸気サイクル中の有機系溶存物質の除去方法。
[7] A method for removing organic dissolved substances in a water-steam cycle in which an organic chemical is added upstream of a heat exchanger, comprising:
A method for removing organic dissolved substances in a water-steam cycle, comprising passing at least a portion of the drain water from the heat exchanger through an electrodeionization device to remove the organic dissolved substances.
[8]前記有機系薬品は滴状凝縮促進剤である[1]~[7]のいずれかの水・蒸気サイクル中の有機系溶存物質の除去方法。 [8] A method for removing organic dissolved substances in a water-steam cycle according to any one of [1] to [7], wherein the organic chemical is a dropwise condensation promoter.
本発明の水・蒸気サイクル中の有機系溶存物質の除去方法によると、滴状凝縮促進剤等の添加による熱交換器の効率向上と、滴状凝縮の対象熱交換器を除いた水・蒸気サイクル系の有機系溶存物質の除去を両立させることができる。 The method for removing organic dissolved substances in a water-steam cycle of the present invention can simultaneously improve the efficiency of heat exchangers by adding a dropwise condensation promoter, etc., and remove organic dissolved substances from the water-steam cycle system, excluding heat exchangers that are subject to dropwise condensation.
また、本発明の一態様では、樹脂再生などではなく、ディスポーザブルを基準とすることにより、再生装置も不要となるので装置サイズは小さく、設備導入のハードルが顕著に低減できる。 Furthermore, in one aspect of the present invention, by focusing on disposable materials rather than resin recycling, recycling equipment is not required, so the equipment size is small and the hurdles to installing the equipment are significantly reduced.
本発明の一態様では、特定の熱交換器の直前に意図的に添加した有機系薬品を、出口のドレンで濾過することで、水蒸気サイクル系全体に、有機系薬品を拡散させない。 In one aspect of the present invention, organic chemicals intentionally added immediately before a specific heat exchanger are filtered through the outlet drain, preventing the organic chemicals from diffusing throughout the entire steam cycle system.
本発明の水・蒸気サイクル中の有機系溶存物質の除去方法の一例を図1~4に示す。 An example of the method for removing organic dissolved substances in a water-steam cycle of the present invention is shown in Figures 1 to 4.
図1~3では、ボイラ1で発生した蒸気が配管2を通って熱交換器3に送蒸される。蒸気は熱交換器3において降温して凝縮してドレン水となる。このドレン水は、配管4から三方弁5によって配管6又は7に流れ、濾過装置(この実施の形態では滴状凝縮促進剤除去装置)A又はBに流れ、滴状凝縮促進剤の除去処理が行われる。滴状凝縮促進剤除去処理された処理水は、配管8又は9から配管10を通ってボイラ1に返送される。この途中で、補給水配管11から補給水が供給される。 In Figures 1 to 3, steam generated in boiler 1 is sent to heat exchanger 3 through pipe 2. The steam is cooled in heat exchanger 3 and condenses to become drain water. This drain water flows from pipe 4 to pipe 6 or 7 via three-way valve 5, and then flows to filtration device (droplet-shaped condensation promoter removal device in this embodiment) A or B, where the droplet-shaped condensation promoter is removed. The treated water from which the droplet-shaped condensation promoter has been removed is returned to boiler 1 through pipe 8 or 9 and pipe 10. Along the way, makeup water is supplied from makeup water pipe 11.
前記配管2において、有機系溶存物質として滴状凝縮促進剤が滴状凝縮促進剤添加装置20によって添加される。滴状凝縮促進剤添加装置20は、薬液を貯留する薬品タンク、薬注ポンプ及び薬品添加ライン等を備えている。 In the piping 2, a dropwise condensation promoter is added as an organic dissolved substance by a dropwise condensation promoter adding device 20. The dropwise condensation promoter adding device 20 is equipped with a chemical tank for storing the chemical solution, a chemical injection pump, a chemical addition line, etc.
三方弁5は、制御器21によって次のようにして制御される。 The three-way valve 5 is controlled by the controller 21 as follows:
図1では、滴状凝縮促進剤添加装置20に、薬品の添加量を検知する機構が設けられている。 In Figure 1, the dropwise condensation promoter addition device 20 is equipped with a mechanism for detecting the amount of chemical added.
運転開始当初は、まず一方の濾過装置Aに通水するように三方弁5が配管4,6を連通させる。薬品の添加量の積算量が、あらかじめ設定しておいた濾過装置Aの薬品吸着量の上限量に近づいたならば、三方弁5を切替え、濾過装置Bへ通水する。濾過装置Bに通水している間に濾過装置Aの濾材の交換を行う。濾過装置Bから濾過装置Aへの通水切替も同様にして行う。 When operation begins, three-way valve 5 first connects pipes 4 and 6 so that water flows through one of the filters, filter A. When the cumulative amount of chemical added approaches the preset upper limit for chemical absorption by filter A, three-way valve 5 switches and water flows through filter B. While water is flowing through filter B, the filter material in filter A is replaced. The same process is used to switch water flow from filter B to filter A.
薬品の添加量は、薬品タンク内の薬液の減少量から求めてもよく、薬品添加ラインに設けた流量計の検出値又は薬注ポンプの稼働時間から求めてもよい。 The amount of chemical to be added may be determined from the amount of chemical liquid remaining in the chemical tank, or from the detection value of a flow meter installed in the chemical addition line or the operating time of the chemical injection pump.
本発明の別の一態様を図2に示す。図2では、配管10に滴状凝縮促進剤濃度などの水質を検出する水質センサ22が設けられている。 Another embodiment of the present invention is shown in Figure 2. In Figure 2, a water quality sensor 22 is provided in the pipe 10 to detect water quality, such as the concentration of the dropwise condensation promoter.
この水質センサ22で、水質を連続的にモニタリングし、有機系薬品濃度に対応するセンサ値が閾値を超えた場合、またはセンサ値に所定のトレンド変動(時系列データの変動)があった場合には、三方弁5を切り替え、通水する濾過装置を切り替える。水質センサ22としては、薬品濃度計のほか、電気伝導率計、pH計、水晶振動子等の1又は2以上を用いることができる。 This water quality sensor 22 continuously monitors water quality, and when the sensor value corresponding to the organic chemical concentration exceeds a threshold value, or when there is a predetermined trend fluctuation (fluctuation in time-series data) in the sensor value, it switches the three-way valve 5 and switches the filtration device through which water passes. The water quality sensor 22 can be one or more of a chemical concentration meter, an electrical conductivity meter, a pH meter, a quartz oscillator, etc.
本発明のさらに別の一態様を図3に示す。図3では、配管4に添加薬品の濃度を検出する濃度センサ24が設けられると共に、配管10にドレン流量を検出する流量計25が設けられている。なお、流量計25は配管4に設けられてもよい。 Yet another embodiment of the present invention is shown in Figure 3. In Figure 3, a concentration sensor 24 that detects the concentration of the added chemical is provided in pipe 4, and a flow meter 25 that detects the drain flow rate is provided in pipe 10. Note that flow meter 25 may also be provided in pipe 4.
濃度センサ24とドレン流量計25の検出値が制御器21に入力され、負荷(濃度と流量の積の経時的積算値)が濾過装置の上限量に近づいたならば三方弁5を切り替える。なお、ドレン流量計25の代わりに、熱交換器前段の蒸気流量計を使用して、濾過装置A又はBを通過するドレン流量を把握してもよい。 The detected values of the concentration sensor 24 and drain flow meter 25 are input to the controller 21, and when the load (the cumulative value of the product of concentration and flow rate over time) approaches the upper limit of the filtration device, the three-way valve 5 is switched. Note that instead of the drain flow meter 25, a steam flow meter upstream of the heat exchanger may be used to monitor the drain flow rate passing through filtration device A or B.
図4は本発明のさらに別の一態様を示す。図4では、熱交換器3からのドレンが配管4を介して電気脱イオン装置30に送水され、脱イオン処理水が配管10を介してボイラ1に送水される。その他の構成は図1と同じである。 Figure 4 shows yet another embodiment of the present invention. In Figure 4, drain from heat exchanger 3 is sent to electrodeionization device 30 via pipe 4, and deionized water is sent to boiler 1 via pipe 10. The rest of the configuration is the same as in Figure 1.
図1~4では、ボイラで発生した蒸気を、単独の有機系薬品を添加する熱交換器3のみに送蒸しているが、本発明はこれに限定されるものではない。 In Figures 1 to 4, steam generated in the boiler is sent only to heat exchanger 3, which adds a single organic chemical, but the present invention is not limited to this.
また、図1~4では対象熱交換器を通過したドレンの全量を濾過装置(図中では滴状凝縮促進剤除去装置)又は電気脱イオン装置に通水しているが、一部でもよいし、他の系統の蒸気・ドレンと合わせて通水してもよい。濾過装置又は電気脱イオン装置が高温(例えば、60℃以上)のドレンを処理できない場合は、他の系統などの低温の水と合わせて水温を低下させてから通水してよい。 In addition, in Figures 1 to 4, the entire amount of drainage that has passed through the target heat exchanger is passed through a filtration device (shown as a dropwise condensation promoter removal device in the figures) or an electrodeionization device, but only a portion of it may be passed through, or it may be passed through together with steam and drainage from other systems. If the filtration device or electrodeionization device cannot process high-temperature drainage (e.g., 60°C or higher), it may be passed through after being combined with low-temperature water from other systems to lower the water temperature.
また、図1~3では、濾過設備は2系統を並列で設置しているが、3系統以上を並列設置し、随時切り替えるようにしてもよい。 In addition, while Figures 1 to 3 show two filtration systems installed in parallel, three or more systems may be installed in parallel and switched as needed.
なお、有機溶存物質の除去レベルは、完全な除去でもよいし、低減でもよく、例えば要求される濃度に応じて除去レベルを決定してよい。 The level of removal of organic dissolved substances may be complete removal or reduction, and the removal level may be determined, for example, depending on the required concentration.
図1~3で使用する濾過装置(滴状凝縮促進剤除去装置)としては、イオン交換樹脂塔、活性炭塔、RO膜装置、NF膜装置が挙げられる。 The filtration devices (droplet condensation promoter removal devices) used in Figures 1 to 3 include ion exchange resin towers, activated carbon towers, RO membrane devices, and NF membrane devices.
イオン交換樹脂は、添加する有機薬剤の種類に応じて、アニオン交換樹脂、カチオン交換樹脂、混床樹脂を選択することが経済的な観点で望ましい。 From an economical standpoint, it is desirable to select anion exchange resin, cation exchange resin, or mixed bed resin as the ion exchange resin depending on the type of organic chemical being added.
例えば、添加する薬品がポリアミン類(具体的には、OLDA(N-オレイル-1,3-プロパンジアミン))の場合には、カチオン交換樹脂を用いるのが好ましく、サルコシン類の場合にはアニオン交換樹脂を用いることが好ましい。 For example, if the chemical to be added is a polyamine (specifically, OLDA (N-oleyl-1,3-propanediamine)), it is preferable to use a cation exchange resin, and if it is a sarcosine, it is preferable to use an anion exchange resin.
また、イオン交換樹脂は、高温のドレン水でも劣化しにくいものが望ましい。 It is also desirable that the ion exchange resin is resistant to deterioration even in high-temperature drain water.
更に望ましくは、濾過装置は、純水レベルの高い設備で使用されていたハイスペックのイオン交換樹脂を用いたイオン交換樹脂塔、又は、RO膜装置が不純物の溶出防止の観点で望ましい。 More preferably, the filtration device is an ion exchange resin tower using high-spec ion exchange resins used in facilities with high levels of pure water purity, or an RO membrane device, from the perspective of preventing impurities from leaching out.
本発明では、濾過装置の前段に、ドレン水を冷却するためのドレン冷却部用熱交換器を設置してもよい。このようにすることで、ディスポーザブルで使用する濾材を収容した濾過装置の容器(ヴェッセル)を非金属製のものとし、操作性と経済性を向上させることができる。 In the present invention, a drain cooling heat exchanger for cooling drain water may be installed upstream of the filtration device. This allows the filtration device's container (vessel) containing disposable filter media to be made of a non-metallic material, improving operability and economy.
なお、濾過装置としてRO膜装置又はNF膜装置を用いる場合は、図1,2の態様に適用される。 When an RO membrane device or NF membrane device is used as the filtration device, the embodiments shown in Figures 1 and 2 are applicable.
[実施例1]
<実験条件>
図1の構成を有した水・蒸気サイクルにおいて、ボイラの定常運転時蒸気発生量10t/hr、常用圧力0.78MPaで運転した。蒸気使用用途は、蒸気直接吹込設備での使用量が1t/hrであり、残りの9t/hrは加熱用の熱交換器に使用される。また、配管2から蒸気を分流させて蒸気の一部を蒸気直接吹込み設備に供給する構成になっている。
[Example 1]
<Experimental conditions>
In the water-steam cycle having the configuration shown in Figure 1, the boiler was operated at a steady-state steam generation rate of 10 t/hr and a normal operating pressure of 0.78 MPa. Steam was used in the direct steam injection facility at 1 t/hr, with the remaining 9 t/hr used for heating heat exchangers. Steam was also diverted from pipe 2, with a portion of the steam being supplied to the direct steam injection facility.
熱交換器のドレン水は、濾過装置A又はBで濾過された後、補給水が補給されて、再度ボイラ給水となっている。濾過装置A,Bとしてはイオン交換塔を設置した。まず、除去装置Aに通水した。 The drain water from the heat exchanger is filtered by filtration device A or B, and then supplemented with makeup water to become boiler feed water again. Filtration devices A and B are equipped with ion exchange towers. First, the water is passed through removal device A.
滴状凝縮促進剤とて、N-オレイル-1,3-プロパンジアミンを主剤とする薬剤を蒸気量に対して20ppm添加した。 As a dropwise condensation promoter, a chemical based on N-oleyl-1,3-propanediamine was added at 20 ppm relative to the steam volume.
また、薬品タンクに液面計を設け、この液面計検出値からタンクからの薬注量を求め、外部に出力信号を発信する仕組みが設けられている。 In addition, a level gauge is installed in the chemical tank, and a mechanism is in place to determine the amount of chemical dispensed from the tank from the detected value of this level gauge and send an output signal to the outside.
イオン交換樹脂が破過する値(閾値)を、理論値から算出した値の80%の値として設定し、この閾値を超えると三方弁切替信号を発信するように構成した。 The value (threshold) at which the ion exchange resin breaks through is set to 80% of the value calculated from the theoretical value, and the system is configured to send a three-way valve switching signal when this threshold is exceeded.
濾過装置A,Bには、別プラントで超純水製造に用いられていたハイグレードのイオン交換樹脂を再利用して充填した。 Filtration devices A and B are filled with recycled high-grade ion exchange resin that was previously used to produce ultrapure water at another plant.
<結果・考察>
蒸気量に対して20ppmの薬剤を連続添加することで、熱交換器3では期待通りの伝熱効率の向上が得られた。また、配管10でドレン水を採取して分析したところ、薬品由来の有機物濃度はゼロであり、まったく検出されなかった。更に、蒸気直接吹込み設備の蒸気を分析しても有機物濃度は同様にゼロであった。
<Results/Discussion>
By continuously adding 20 ppm of chemicals to the amount of steam, the expected improvement in heat transfer efficiency was achieved in the heat exchanger 3. Furthermore, when drain water was sampled and analyzed in the pipe 10, the concentration of organic matter derived from the chemicals was zero, meaning that no organic matter was detected at all. Furthermore, when the steam from the direct steam injection equipment was analyzed, the organic matter concentration was also zero.
濾過装置Aに通水開始して、2か月経過後、薬品の積算使用量に基づいて、三方弁が切り替わり、濾過装置Bへの通水に切り替わると同時に、濾過装置Aの樹脂を交換する指示信号が外部に発信された。 Two months after water began flowing through filtration device A, the three-way valve switched based on the cumulative amount of chemical used, and water was switched to flow through filtration device B. At the same time, a signal was sent to the outside to replace the resin in filtration device A.
[比較例1]
<実験条件>
図1において、三方弁5、配管6,7,8,9及び濾過装置A,Bを省略し、配管4,10を直結した構成とした。これ以外は、実施例1と全く同じ条件で試験を行った。
[Comparative Example 1]
<Experimental conditions>
1, the three-way valve 5, the pipes 6, 7, 8, 9, and the filtration devices A and B were omitted, and the pipes 4 and 10 were directly connected. Except for this, the test was carried out under the same conditions as in Example 1.
<結果・考察>
蒸気直接吹込み設備で検出された薬品成分濃度は、0.14mg/Lとなり、蒸気中にTOC成分を含まない蒸気質の規格を満足できなかった。なお、薬品成分の分析は、蒸気を冷却する仮設の熱交換器(図示略)を用いて凝縮してから測定した。
<Results/Discussion>
The chemical component concentration detected by the direct steam injection equipment was 0.14 mg/L, which did not satisfy the standard for steam quality that does not contain TOC components. The chemical component analysis was performed after condensing the steam using a temporary heat exchanger (not shown) that cools the steam.
以上のことから、熱交換器3の前段で添加された有機系薬品を、ドレンから濾過除去することにより、水蒸気サイクル系全体に、有機系薬品を拡散させないことが確認できた。 From the above, it was confirmed that by filtering and removing the organic chemicals added upstream of heat exchanger 3 through the drain, the organic chemicals do not diffuse throughout the entire steam cycle system.
本発明を特定の態様を用いて詳細に説明したが、発明の効果が奏される範囲内で様々な変更が可能であることは当業者に明らかである。 Although the present invention has been described in detail using specific embodiments, it will be apparent to those skilled in the art that various modifications are possible within the scope of the invention.
1 ボイラ
3 熱交換器
5 三方弁
21 制御器
30 電気脱イオン装置
1 Boiler 3 Heat exchanger 5 Three-way valve 21 Controller 30 Electrodeionization device
Claims (7)
該熱交換器のドレン水を濾過装置に通して滴状凝縮促進剤を除去することにより前記蒸気直接吹込設備へ供給される蒸気に滴状凝縮促進剤を含有させないようにする水・蒸気サイクル中の滴状凝縮促進剤の除去方法であって、
該濾過装置として、イオン交換装置、活性炭濾過装置、RO膜装置及びNF膜装置の少なくとも一種よりなる機器が複数個並列に配置されており、
一部の該機器にドレン水を通し、薬品添加量またはセンサによる水質の測定値に基づいて濾過性能が低下したと判断された場合に通水を他の該機器に切替えることを特徴とする水・蒸気サイクル中の滴状凝縮促進剤の除去方法。 In a water-steam cycle in which a portion of steam from a boiler is supplied to a steam direct injection facility, the remainder of the steam from the boiler is supplied to a heat exchanger after adding a drop-like condensation promoter, and drain water from the heat exchanger is returned to the boiler ,
A method for removing a dropwise condensation promoter in a water-steam cycle, which comprises passing drain water from the heat exchanger through a filtration device to remove the dropwise condensation promoter, thereby preventing the dropwise condensation promoter from being contained in the steam supplied to the steam direct injection facility, comprising :
The filtration device is a plurality of devices each consisting of at least one of an ion exchange device, an activated carbon filtration device, an RO membrane device, and an NF membrane device, arranged in parallel;
A method for removing droplets of condensation promoters in a water-steam cycle, characterized in that drain water is passed through some of the equipment, and when it is determined that the filtration performance has decreased based on the amount of chemicals added or the water quality measured by a sensor, the water is switched to passing through other of the equipment .
該熱交換器のドレン水を電気脱イオン装置に通して滴状凝縮促進剤を除去することにより前記蒸気直接吹込設備へ供給される蒸気に滴状凝縮促進剤を含有させないようにすることを特徴とする水・蒸気サイクル中の滴状凝縮促進剤の除去方法。 In a water-steam cycle in which a portion of steam from a boiler is supplied to a steam direct injection facility, the remainder of the steam from the boiler is supplied to a heat exchanger after adding a drop-like condensation promoter, and drain water from the heat exchanger is returned to the boiler ,
A method for removing dropwise condensation promoters in a water-steam cycle, characterized in that the drain water from the heat exchanger is passed through an electrodeionization device to remove the dropwise condensation promoters, thereby preventing the dropwise condensation promoters from being contained in the steam supplied to the steam direct injection facility .
Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2024066945A JP7790466B2 (en) | 2024-04-17 | 2024-04-17 | Method for removing organic dissolved substances in water/steam cycles |
| PCT/JP2025/014017 WO2025220542A1 (en) | 2024-04-17 | 2025-04-08 | Method for removing organic dissolved substance in water/vapor cycle |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2024066945A JP7790466B2 (en) | 2024-04-17 | 2024-04-17 | Method for removing organic dissolved substances in water/steam cycles |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JP2025163555A JP2025163555A (en) | 2025-10-29 |
| JP7790466B2 true JP7790466B2 (en) | 2025-12-23 |
Family
ID=97403475
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2024066945A Active JP7790466B2 (en) | 2024-04-17 | 2024-04-17 | Method for removing organic dissolved substances in water/steam cycles |
Country Status (2)
| Country | Link |
|---|---|
| JP (1) | JP7790466B2 (en) |
| WO (1) | WO2025220542A1 (en) |
Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2005163628A (en) | 2003-12-02 | 2005-06-23 | Toshiba Corp | Reheat steam turbine plant and operation method thereof |
| JP2008178826A (en) | 2007-01-25 | 2008-08-07 | Toshiba Corp | Water treatment equipment |
| JP2011012921A (en) | 2009-07-03 | 2011-01-20 | Kurita Water Ind Ltd | Method of improving heat transfer efficiency of steam dryer |
| JP2017064639A (en) | 2015-09-30 | 2017-04-06 | 栗田工業株式会社 | Steam power plant wastewater recovery method and equipment |
| JP2019219270A (en) | 2018-06-20 | 2019-12-26 | 日立Geニュークリア・エナジー株式会社 | Condensate desalination system |
| JP2021104481A (en) | 2019-12-26 | 2021-07-26 | 三菱パワー株式会社 | Water treatment apparatus, power generation plant and water treatment method |
-
2024
- 2024-04-17 JP JP2024066945A patent/JP7790466B2/en active Active
-
2025
- 2025-04-08 WO PCT/JP2025/014017 patent/WO2025220542A1/en active Pending
Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2005163628A (en) | 2003-12-02 | 2005-06-23 | Toshiba Corp | Reheat steam turbine plant and operation method thereof |
| JP2008178826A (en) | 2007-01-25 | 2008-08-07 | Toshiba Corp | Water treatment equipment |
| JP2011012921A (en) | 2009-07-03 | 2011-01-20 | Kurita Water Ind Ltd | Method of improving heat transfer efficiency of steam dryer |
| JP2017064639A (en) | 2015-09-30 | 2017-04-06 | 栗田工業株式会社 | Steam power plant wastewater recovery method and equipment |
| JP2019219270A (en) | 2018-06-20 | 2019-12-26 | 日立Geニュークリア・エナジー株式会社 | Condensate desalination system |
| JP2021104481A (en) | 2019-12-26 | 2021-07-26 | 三菱パワー株式会社 | Water treatment apparatus, power generation plant and water treatment method |
Also Published As
| Publication number | Publication date |
|---|---|
| JP2025163555A (en) | 2025-10-29 |
| WO2025220542A1 (en) | 2025-10-23 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US7531096B2 (en) | System and method of reducing organic contaminants in feed water | |
| WO1988006914A1 (en) | Apparatus for concentrating waste liquid, apparatus for processing waste liquid and method of concentrating waste liquid | |
| US4213830A (en) | Method for the transfer of heat | |
| ES2935276T3 (en) | Scale removal system and procedures | |
| US20050056594A1 (en) | Method and system for the manufacture of pharmaceutical water | |
| JPS63501350A (en) | Water supply level control device for demineralizer | |
| JPH1147560A (en) | Secondary system line water treatment plant for pressurized water type atomic power plant | |
| Seigworth et al. | Case study: Integrating membrane processes with evaporation to achieve economical zero liquid discharge at the Doswell Combined Cycle Facility | |
| JP7790466B2 (en) | Method for removing organic dissolved substances in water/steam cycles | |
| JPH1164575A (en) | Secondary system line water treatment device for pressurized-water nuclear power plant | |
| CN212833221U (en) | Nuclear power plant steam generator sewage purification system | |
| US10618032B2 (en) | Low temperature wet air oxidation | |
| CN107857395B (en) | Condensate fine treatment regeneration wastewater ammonia recovery system | |
| JP7596807B2 (en) | Water Treatment Systems | |
| JP2009162514A (en) | System for purifying system water in secondary system of nuclear power plant with pressurized water reactor | |
| TW202608828A (en) | Methods for removing organic dissolved substances in water-vapor cycles | |
| JP2013245833A (en) | Power generating plant | |
| JPH0899086A (en) | Boiler water supply treatment device | |
| JP4931107B2 (en) | Electrodeionization device and secondary line water treatment device for pressurized water nuclear power plant using the same | |
| JPH1085739A (en) | Condensate desalination equipment | |
| JPS5929093A (en) | How to remove scale | |
| JP5350337B2 (en) | Radioactive waste treatment method and apparatus | |
| Wade et al. | Desalination: The state of the art | |
| JP3001842B2 (en) | Radioactive waste treatment method and apparatus | |
| Scherm | Treatment of Organic Chemical Manufacturing Wastewater for Reuse |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20250408 |
|
| A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20250624 |
|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20250804 |
|
| TRDD | Decision of grant or rejection written | ||
| A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20251111 |
|
| A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20251124 |
|
| R150 | Certificate of patent or registration of utility model |
Ref document number: 7790466 Country of ref document: JP Free format text: JAPANESE INTERMEDIATE CODE: R150 |