[go: up one dir, main page]

TWI548595B - Water treatment method - Google Patents

Water treatment method Download PDF

Info

Publication number
TWI548595B
TWI548595B TW101133035A TW101133035A TWI548595B TW I548595 B TWI548595 B TW I548595B TW 101133035 A TW101133035 A TW 101133035A TW 101133035 A TW101133035 A TW 101133035A TW I548595 B TWI548595 B TW I548595B
Authority
TW
Taiwan
Prior art keywords
water
salt
acid
treatment method
electric double
Prior art date
Application number
TW101133035A
Other languages
Chinese (zh)
Other versions
TW201313619A (en
Inventor
志村幸祐
山田學
Original Assignee
栗田工業股份有限公司
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by 栗田工業股份有限公司 filed Critical 栗田工業股份有限公司
Publication of TW201313619A publication Critical patent/TW201313619A/en
Application granted granted Critical
Publication of TWI548595B publication Critical patent/TWI548595B/en

Links

Classifications

    • 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
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F22STEAM GENERATION
    • F22DPREHEATING, 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
    • F22D11/00Feed-water supply not provided for in other main groups
    • F22D11/006Arrangements of feedwater cleaning with a boiler
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/16Regeneration of sorbents, filters

Landscapes

  • Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Hydrology & Water Resources (AREA)
  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
  • Treatment Of Water By Ion Exchange (AREA)
  • Electric Double-Layer Capacitors Or The Like (AREA)

Description

水處理方法 Water treatment method

本發明是有關於一種用以製造鍋爐(boiler)等的蒸氣產生設備的供水的水處理方法。詳細而言,本發明是有關於一種如下的水處理方法:無須使用強鹼或強酸,而且,無須使用大量的氯化鈉,可進行與先前的軟水供水相比大幅降低了由吹除(blow)引起的熱與水的損失的運轉。本發明是有關於一種如下的水處理方法:可防止由鈣或鎂引起的傳熱面的銹化,並且亦可一併防止自蒸氣凝結水帶入的鐵的銹化,藉此,可將傳熱面保持清潔。 The present invention relates to a water treatment method for supplying water to a steam generating device such as a boiler. In particular, the present invention relates to a water treatment method which does not require the use of a strong base or a strong acid, and which does not require the use of a large amount of sodium chloride, which can be drastically reduced compared to the previous soft water supply (blow) The operation of the loss of heat and water. The present invention relates to a water treatment method capable of preventing rusting of a heat transfer surface caused by calcium or magnesium, and also preventing rusting of iron brought in by steam condensate, thereby The heat transfer surface remains clean.

當在鍋爐等的蒸氣產生設備中運轉壓力低時,一般而言,利用填充了鈉型陽離子交換樹脂的軟化器來對都市供水等的自來水或地下水等進行處理,藉此將水中的鈣與鎂置換為鈉的軟化水作為補給水而使用。這是為了防止如下情況:鈣或鎂等的硬度成分被帶入至鍋爐內而於傳熱面銹化從而妨礙到傳熱,藉此會產生能量損失,或者傳熱面過熱而受損。 When the operating pressure is low in a steam generating facility such as a boiler, generally, a taper filled with a sodium-type cation exchange resin is used to treat tap water or groundwater such as a city water supply, thereby using calcium and magnesium in the water. The softened water substituted with sodium is used as make-up water. This is to prevent the hardness component such as calcium or magnesium from being introduced into the boiler and rusting on the heat transfer surface to hinder heat transfer, thereby causing energy loss or overheating of the heat transfer surface.

當使用軟化水作為補給水而運轉蒸氣產生設備時,存在軟化器的陽離子交換樹脂的再生中使用大量的氯化鈉的問題。在由軟化器而獲得的軟化水中大量地包含溶解鹽類,因而伴隨蒸氣的產生的濃縮所造成的鍋爐水中的鹽類濃度上升,鍋爐水連同蒸氣容易產生伴隨的汽水共沸(carry over)。因此,必須吹除相對大量的鍋爐水而將濃 縮倍率維持在規定的範圍內。藉由吹除鍋爐水,補給水會增多,並且伴隨吹除水而損失的熱量增多。 When the steam generating apparatus is operated using demineralized water as the makeup water, there is a problem that a large amount of sodium chloride is used in the regeneration of the cation exchange resin of the softener. The demineralized water obtained by the softener contains a large amount of dissolved salts, so that the concentration of the salt in the boiler water is increased by the concentration of the vapor, and the boiler water and the vapor are likely to cause accompanying soda azealing. Therefore, it is necessary to blow off a relatively large amount of boiler water and it will be thick The magnification is maintained within the specified range. By blowing off the boiler water, the make-up water will increase, and the amount of heat lost with the blowing of water will increase.

為了削減藉由吹除而損失掉的熱,眾所周知有下述i~iii的方法,即,對低壓鍋爐的補給水進行處理,藉此除去補給水中的溶解物質,從而削減吹除水量。各方法中分別存在以下的問題。 In order to reduce the heat lost by blowing, it is known that the following i-iii method is used to treat the supply water of the low-pressure boiler, thereby removing the dissolved matter in the make-up water, thereby reducing the amount of blown water. The following problems exist in each method.

i)使用強鹽基性陰離子交換樹脂與強酸性陽離子交換樹脂而除去溶解離子的方法(非專利文獻1)。 i) A method of removing dissolved ions using a strong salt-based anion exchange resin and a strongly acidic cation exchange resin (Non-Patent Document 1).

該方法中必須頻繁地利用強酸與強鹼再生離子交換樹脂。 In this method, it is necessary to frequently regenerate the ion exchange resin with a strong acid and a strong base.

ii)在利用軟化器進行處理後,利用逆浸透膜(reverse osmosis membrane)裝置除去供水的溶解鹽類的方法(非專利文獻2)。 Ii) A method of removing dissolved salts of water supply by a reverse osmosis membrane apparatus after treatment with a softener (Non-Patent Document 2).

該方法中,與藉由先前的軟化器而軟化的方法同樣地,在填充於軟化器的陽離子交換樹脂的再生中使用大量的氯化鈉,並且在逆浸透膜處理中排出相對多的濃縮水,因而供逆浸透膜處理的軟化水的使用量進一步增加,藉此氯化鈉的使用量進一步增加。即便減去吹除的削減量,水的使用量與僅利用軟化器進行處理的情況相比亦增多。 In this method, as in the method of softening by a previous softener, a large amount of sodium chloride is used in the regeneration of the cation exchange resin filled in the softener, and a relatively large amount of concentrated water is discharged in the reverse osmosis membrane treatment. Therefore, the amount of demineralized water used for the reverse osmosis membrane treatment is further increased, whereby the amount of sodium chloride used is further increased. Even if the reduction amount of the blow-off is subtracted, the amount of water used is increased as compared with the case where only the softener is used for the treatment.

iii)在利用逆浸透膜裝置進行處理後,利用組合了離子交換膜及直流電源的電性脫鹽裝置進行處理的方法(非專利文獻3)。 Iii) A method of performing treatment by an electrical desalination apparatus in which an ion exchange membrane and a DC power source are combined after being treated by a reverse osmosis membrane device (Non-Patent Document 3).

該方法中,所獲得的處理水成為溶解物質極少的水,但裝置規模非常大,價格亦高。 In this method, the treated water obtained is a water having a very small amount of dissolved matter, but the apparatus is very large in scale and high in price.

將自鍋爐發生的蒸氣的凝結水加以回收並作為供水而再利用,會形成熱與水的回收,並且在補給軟化水的情況下,藉由自供水而帶入至鍋爐中的溶解物質的減少,且藉由吹除水的削減亦實現更進一步的節能。自回收凝結水的配管溶出的鐵被帶入至鍋爐中,藉此鍋爐內的傳熱面附著氧化鐵銹,會使傳熱效率降低,亦成為發生附著有銹的下部的腐蝕困擾(trouble)的原因。因此,在所回收的凝結水的鐵濃度高的情況下,亦存在無法作為供水再利用而排出的情況。 The condensed water from the steam generated in the boiler is recovered and reused as a water supply, and heat and water are recovered, and in the case of replenishing the softened water, the dissolved matter brought into the boiler by the self-water supply is reduced. Further energy savings are achieved by the reduction of blown water. The iron eluted from the piping for recovering the condensed water is brought into the boiler, whereby the heat transfer surface in the boiler adheres to the oxidized rust, which lowers the heat transfer efficiency and becomes a corrosion problem in which the lower portion to which the rust adheres is generated. the reason. Therefore, when the iron concentration of the collected condensed water is high, there is a case where it cannot be discharged as a water supply.

本發明中所使用的通液型電雙層電容器(Electric double-layer condenser)脫鹽裝置應用於純水的製造等中,亦眾所周知利用通液型電雙層電容器脫鹽裝置與離子交換裝置依次進行處理的脫鹽方法(專利文獻1)。 The electric double-layer condenser desalination device used in the present invention is applied to the production of pure water, etc., and it is also known to use a liquid-through type electric double-layer capacitor desalination device and an ion exchange device to sequentially perform processing. Desalination method (Patent Document 1).

先前技術文獻 Prior technical literature 專利文獻 Patent literature

專利文獻1:日本專利特開2002-210468號公報 Patent Document 1: Japanese Patent Laid-Open Publication No. 2002-210468

非專利文獻 Non-patent literature

非專利文獻1:鍋爐的水管理<知識與應用>社団法人日本鍋爐協會發行初版P.146~176 Non-Patent Document 1: Water Management of Boilers <Knowledge and Application> The first edition of P.146~176 issued by the Japan Boiler Association

非專利文獻2:鍋爐的水管理<知識與應用>社団法人日本鍋爐協會發行初版P.183 Non-Patent Document 2: Water Management of Boilers <Knowledge and Application> Social Welfare Corporation Japan Boiler Association Released P.183

非專利文獻3:鍋爐的水管理<知識與應用>社団法人日本鍋爐協會發行初版P.191~193 Non-Patent Document 3: Water Management of Boilers <Knowledge and Application> The first edition of P.191~193 issued by the Japan Boiler Association

本發明的第1目的在於提供如下的水處理方法,該水處理方法改善了先前技術的需要大量的氯化鈉或強酸、強鹼的問題,或供水處理中排出大量的濃縮水的問題,且可進行低壓鍋爐的吹除削減運轉。 A first object of the present invention is to provide a water treatment method which improves the problems of the prior art which require a large amount of sodium chloride or a strong acid or a strong alkali, or a large amount of concentrated water in a water supply treatment, and The low pressure boiler can be blown and reduced.

本發明的第2目的在於提供如下的水處理方法,該水處理方法不會產生由銹附著引起的能量損失或腐蝕困擾等,藉由與節能、節水有關的作為蒸氣凝結水的供水的回收、再利用而實現熱與水的回收再利用,且藉由吹除削減而實現節能運轉。 A second object of the present invention is to provide a water treatment method which does not cause energy loss or corrosion trouble caused by rust adhesion, and is recovered from water supply as steam condensate related to energy saving and water saving. Reuse and reuse of heat and water, and energy-saving operation by blowing reduction.

本發明者等人為了解決上述課題而反覆進行了積極研究,結果發現,藉由應用通液型電雙層電容器脫鹽裝置,進而藉由使用分子內具有羧基的水溶性聚合物作為防銹劑,而可解決上述課題。 The inventors of the present invention have conducted active research in order to solve the above problems, and as a result, it has been found that a water-soluble polymer having a carboxyl group in a molecule is used as a rust preventive agent by applying a liquid-pass type electric double layer capacitor desalination device. The above problems can be solved.

本發明基於上述見解而達成,且以如下為主旨。 The present invention has been achieved based on the above findings and is intended to be as follows.

[1]一種水處理方法,其特徵在於:將原水依序通過通液型電雙層電容器脫鹽裝置及軟化器而獲得的處理水,供給至蒸氣產生器。 [1] A water treatment method in which raw water obtained by sequentially passing a raw water through a liquid-through type electric double-layer capacitor desalination apparatus and a softener is supplied to a steam generator.

[2]一種水處理方法,其特徵在於:在將蒸氣凝結水作為供水而回收、再利用的蒸氣產生設備中,將不使用軟化器而將原水通過通液型電雙層電容器脫鹽裝置所獲得的處理水、與上述蒸氣凝結水的回收水作為供水而供給至蒸氣產生器,並且在該供水中添加分子內具有羧基的水溶性聚合物。 [2] A water treatment method in which a raw material is passed through a through-liquid type electric double layer capacitor desalination apparatus without using a softener in a steam generation apparatus that recovers and reuses steam condensed water as a water supply. The treated water and the recovered water of the vapor condensed water are supplied to the steam generator as a water supply, and a water-soluble polymer having a carboxyl group in the molecule is added to the water supply.

[3]在[2]的水處理方法中,相對於向上述蒸氣產生器 的供水中的鈣量,添加1重量倍~5重量倍的上述具有羧基的水溶性聚合物。 [3] In the water treatment method of [2], with respect to the above steam generator The amount of calcium in the water supply is 1 to 5 times by weight of the above water-soluble polymer having a carboxyl group.

[4]在[2]或[3]的水處理方法中,上述具有羧基的水溶性聚合物為丙烯酸鈉的均聚物。 [4] The water treatment method according to [2] or [3], wherein the water-soluble polymer having a carboxyl group is a homopolymer of sodium acrylate.

根據本發明的水處理方法,無須如使用強鹽基性陰離子交換樹脂與強酸性陽離子交換樹脂的情況般使用強鹼、強酸,而且無須如僅利用軟化器進行處理的情況般使用大量的氯化鈉,從而與先前的僅利用軟化器進行處理的軟化水或將該軟化水進而利用逆浸透膜裝置進行處理而供水的情況相比,可進行大幅降低了由吹除引起的熱與水的損失的運轉。藉由防止由鈣或鎂引起的傳熱面的銹化,並且亦一併防止自蒸氣凝結水帶入的鐵的銹化,而可進行能夠將傳熱面維持清潔的水處理。 According to the water treatment method of the present invention, it is not necessary to use a strong base or a strong acid as in the case of using a strong salt-based anion exchange resin and a strongly acidic cation exchange resin, and it is not necessary to use a large amount of chlorination as in the case of treatment using only a softener. Sodium can be used to significantly reduce the loss of heat and water caused by blowing, as compared with the case of the prior softened water treated only with a softener or by treating the softened water with a reverse osmosis membrane device for water supply. The operation. By preventing rusting of the heat transfer surface caused by calcium or magnesium, and also preventing rusting of iron brought in by the steam condensate, water treatment capable of maintaining the heat transfer surface clean can be performed.

尤其在將蒸氣凝結水回收、再利用的情況下,在僅利用通液型電雙層電容器脫鹽裝置進行處理的處理水中,可添加分子內具有羧基的水溶性聚合物並供給至蒸氣產生器,該情況下,可不需要軟化器,且可不需要用以裝置的簡化與軟化器的再生的氯化鈉。該方法中,可使連同蒸氣凝結水而一併被帶入的鐵的銹化,與通液型電雙層電容器脫鹽裝置中所含的鈣共存,並且添加分子內具有羧基的水溶性聚合物,藉此使鐵與鈣一併不會銹化地吹除而排出。 In particular, when the steam condensed water is recovered and reused, a water-soluble polymer having a carboxyl group in the molecule can be added to the steam generator in the treated water treated only by the through-liquid type electric double-layer capacitor desalination apparatus. In this case, a softener may not be required, and sodium chloride for simplification of the apparatus and regeneration of the softener may not be required. In this method, rusting of iron brought together with steam condensed water, coexistence with calcium contained in a through-liquid type electric double layer capacitor desalination apparatus, and addition of a water-soluble polymer having a carboxyl group in the molecule Thereby, iron and calcium are not rusted and discharged.

以下對本發明的實施的形態進行詳細說明。 The form of implementation of the present invention will be described in detail below.

本發明的第1態樣的水處理方法的特徵在於:將原水依序通過通液型電雙層電容器脫鹽裝置及軟化器而獲得的處理水,供給至蒸氣產生器。 A water treatment method according to a first aspect of the present invention is characterized in that the raw water is sequentially supplied to the steam generator by the treated water obtained by sequentially passing through the liquid-through type electric double-layer capacitor desalination apparatus and the softener.

根據第1態樣,將原水利用通液型電雙層電容器脫鹽裝置加以處理而除去原水中的鈉離子、鈣離子、鎂離子等的陽離子,及氯化物離子、硫酸離子、硝酸離子等的陰離子,從而可大幅地減少原水中的離子。因此,可降低後段的軟化器的離子負載,並可大幅地削減軟化器的再生中所使用的氯化鈉量。根據第1態樣,可大幅地降低帶入至鍋爐水中的鹽類的濃度,亦可大幅地降低由該些溶解鹽類引起的導電率的上升,從而可大幅削減吹除水。根據第1態樣,亦不需要如使用離子交換樹脂情況般的強鹼或強酸。軟化器藉由陽離子交換樹脂而將鈣離子、鎂離子等置換為鈉離子。陽離子交換樹脂的再生中使用濃厚的氯化鈉水溶液。 According to the first aspect, the raw water is treated by a through-liquid type electric double layer capacitor desalination device to remove cations such as sodium ions, calcium ions, and magnesium ions in the raw water, and anions such as chloride ions, sulfate ions, and nitrate ions. Therefore, the ions in the raw water can be greatly reduced. Therefore, the ion load of the softener in the subsequent stage can be reduced, and the amount of sodium chloride used in the regeneration of the softener can be greatly reduced. According to the first aspect, the concentration of the salt introduced into the boiler water can be greatly reduced, and the increase in the electrical conductivity caused by the dissolved salts can be greatly reduced, and the blown water can be drastically reduced. According to the first aspect, a strong base or a strong acid as in the case of using an ion exchange resin is not required. The softener replaces calcium ions, magnesium ions, and the like into sodium ions by a cation exchange resin. A thick aqueous solution of sodium chloride is used for the regeneration of the cation exchange resin.

本發明的第2態樣的水處理方法的特徵在於:在將蒸氣凝結水作為供水而回收、再利用的蒸氣產生設備中,將不使用軟化器而將原水通過通液型電雙層電容器脫鹽裝置所獲得的處理水、與上述蒸氣凝結水的回收水作為供水而供給至蒸氣產生器,並且在該供水中添加分子內具有羧基的水溶性聚合物。 A water treatment method according to a second aspect of the present invention is characterized in that, in a steam generating apparatus that recovers and reuses steam condensed water as a water supply, the raw water is desalted by a liquid-through type electric double layer capacitor without using a softener. The treated water obtained by the apparatus and the recovered water of the vapor condensed water are supplied to the steam generator as a water supply, and a water-soluble polymer having a carboxyl group in the molecule is added to the water supply.

根據第2態樣,因不需要軟化器,故亦不需要用於軟化器的再生的氯化鈉。根據第2態樣,被帶入至鍋爐的鹽類濃度與僅利用軟化器處理原水的情況相比得到大幅降 低,因而可削減吹除。根據第2態樣,排出的熱或水、水處理化學品成分得以削減,供水量減少,因而添加的水處理化學品的量亦得以削減。 According to the second aspect, since the softener is not required, sodium chloride for regeneration of the softener is not required. According to the second aspect, the concentration of the salt brought into the boiler is greatly reduced as compared with the case where only the softener is used to treat the raw water. Low, so you can cut off. According to the second aspect, the amount of heat or water and water treatment chemicals discharged is reduced, and the amount of water supplied is reduced, so that the amount of added water treatment chemicals is also reduced.

根據第2態樣,利用通液型電雙層電容器脫鹽裝置的處理水中所含的鈣、與供水中所添加的分子內具有羧基的水溶性聚合物,可防止與蒸氣凝結水一併被帶入的鐵的銹化,並可向吹除水中排出。因此,較佳為供水中存在鈣,由此,未利用軟化器對通液型電雙層電容器脫鹽裝置的處理水進行處理便進行供水。 According to the second aspect, the calcium contained in the treated water of the through-liquid type electric double-layer capacitor desalination apparatus and the water-soluble polymer having a carboxyl group added to the molecule added to the water supply can be prevented from being taken together with the vapor condensed water. The iron that has entered is rusted and can be discharged into the blown water. Therefore, it is preferable that calcium is present in the water supply, and thus the water to be treated is treated without using the softener to treat the treated water of the liquid-through type electric double layer capacitor desalination apparatus.

通液型電雙層電容器脫鹽裝置具有如下構成:之間夾著通液路徑的具有2個高比表面積的導電體層,且於該些導電體層的外側配置集電極。藉由對集電極施加電壓,使原水中的離子電性地吸附於導電體層,而可獲得溶解鹽類的濃度減少的處理水。作為上述高比表面積的導電體,例如較佳為活性碳。 The liquid-passing type electric double-layer capacitor desalination apparatus has a structure in which two conductor layers having a high specific surface area are interposed between each other, and a collector is disposed outside the conductor layers. By applying a voltage to the collector, ions in the raw water are electrically adsorbed to the conductor layer, and treated water having a reduced concentration of dissolved salts can be obtained. As the above-mentioned high specific surface area conductor, for example, activated carbon is preferable.

在通液型電雙層電容器脫鹽裝置中,經由以下所示的處理步驟而將流入水中的離子性物質除去。以流入水中所含的離子性物質為氯化鈉,上述高比表面積的導電體為活性碳的情況為例,使用圖1、圖2對該處理機構進行說明。 In the through-liquid type electric double layer capacitor desalination apparatus, the ionic substance flowing into the water is removed through the processing steps shown below. The treatment mechanism will be described with reference to FIGS. 1 and 2, in the case where the ionic substance contained in the inflow water is sodium chloride and the conductor having the high specific surface area is activated carbon.

如圖1所示,於施加電壓時,流入水中的鈉離子電性吸附於與陰極側的集電極1接觸的活性碳層2,氯化物離子電性地吸附於與陽極側的集電極3接觸的活性碳層4。因此,自出口獲得的處理水的氯化鈉濃度大幅降低。若長時間持續通水,則對活性碳層2、活性碳層4的離子的吸 附接近飽和,因而自出口獲得的處理水的氯化鈉濃度增高。因此,若在達到吸附飽和前使陽極側與陰極側短路或者逆轉,則如圖2所示,吸附於活性碳層2、活性碳層4的鈉離子及氯化物離子脫離,包含比流入水中的氯化鈉濃度更高濃度的氯化鈉的流出水自出口被排出。若延緩此時的流速,則便可以較少的流水量排出吸附於活性碳層2、活性碳層4的氯化鈉。 As shown in FIG. 1, when a voltage is applied, sodium ions flowing into the water are electrically adsorbed to the activated carbon layer 2 in contact with the collector 1 on the cathode side, and the chloride ions are electrically adsorbed to the collector 3 on the anode side. Activated carbon layer 4. Therefore, the sodium chloride concentration of the treated water obtained from the outlet is greatly lowered. If the water is continuously passed for a long time, the ions of the activated carbon layer 2 and the activated carbon layer 4 are sucked. The saturation is close to the saturation, so that the concentration of sodium chloride in the treated water obtained from the outlet is increased. Therefore, if the anode side and the cathode side are short-circuited or reversed before the adsorption saturation is reached, as shown in FIG. 2, the sodium ions and chloride ions adsorbed on the activated carbon layer 2 and the activated carbon layer 4 are separated, including the inflow water. Sodium chloride concentration The effluent water of a higher concentration of sodium chloride is discharged from the outlet. If the flow rate at this time is delayed, the sodium chloride adsorbed to the activated carbon layer 2 and the activated carbon layer 4 can be discharged with a small amount of flowing water.

本發明中,使用上述通液型電雙層電容器脫鹽裝置製造鍋爐供水。 In the present invention, the boiler water supply is manufactured using the above-described liquid-through type electric double layer capacitor desalination apparatus.

通液型電雙層電容器脫鹽裝置如上述般,因在電極部中重複進行脫鹽步驟與排出步驟,故排出步驟中無法獲得脫鹽處理水。在必須連續地獲得處理水的情況下,只要以設置多個通液型電雙層電容器而可確保必要的處理水量的方式對動作時期加以控制即可。 In the liquid-passing type electric double-layer capacitor desalination apparatus, as described above, since the desalination step and the discharge step are repeated in the electrode portion, the desalination treatment water cannot be obtained in the discharge step. When it is necessary to continuously obtain the treated water, it is only necessary to control the operating period so that a plurality of liquid-through type electric double layer capacitors are provided to secure the necessary amount of treated water.

作為本發明中進行處理的原水,可列舉井水、自來水、河川水、工業用水、再生水(reclaimed water)、污水等的各種水。 Examples of the raw water to be treated in the present invention include various types of water such as well water, tap water, river water, industrial water, reclaimed water, and sewage.

以下,參照圖3,對本發明的第1態樣進行具體說明。 Hereinafter, a first aspect of the present invention will be specifically described with reference to Fig. 3 .

圖3是表示本發明的第1態樣的實施形態的系統圖。原水首先被導入至通液型電雙層電容器脫鹽裝置11而得到處理,藉此除去鈉離子、鈣離子、鎂離子等的陽離子,及氯化物離子、硫酸離子、硝酸離子等的陰離子。藉由通液型電雙層電容器脫鹽裝置11,可將原水中的離子除去至少數十%以上,繼而可將軟化器12的離子負載降低至數分 之一至數十分之一。因此,軟化器12的再生中所使用的氯化鈉的量亦可降低至數分之一至數十分之一,並且軟水器12的處理水經由供水箱13而供給至鍋爐14,藉此可大幅降低帶入至鍋爐水中的鹽類的濃度,亦可大幅地降低由該些溶解鹽類引起的導電率的上升。因此,可大幅削減吹除水,藉由吹除而排出的水與熱得以削減,並且對用以產生規定的蒸氣的鍋爐的供水量亦減少。結果,獲得如下優點:可使通液型電雙層電容器脫鹽裝置11或軟化器12為處理水量小者,軟化器的再生中使用的氯化鈉的量得以進一步削減。而且,藉由對鍋爐14的供水量減少,供水中添加規定濃度的水處理化學品的使用量亦得以削減。進而,藉由吹除的削減,鍋爐水的濃縮上升,因而對於藉由在鍋爐水中維持規定濃度而防止鍋爐內的腐蝕或銹的水處理化學品而言,添加濃度與先前相比可進一步降低。而且,藉由在供水中添加分子內具有羧基的水溶性聚合物,而防止供水中極微量地含有的硬度成分的鍋爐內的銹化,亦可進行抑制了傳熱損失或銹下部的腐蝕的發生等的水處理。 Fig. 3 is a system diagram showing an embodiment of a first aspect of the present invention. The raw water is first introduced into the liquid-through type electric double layer capacitor desalination apparatus 11 and treated to remove cations such as sodium ions, calcium ions, and magnesium ions, and anions such as chloride ions, sulfate ions, and nitrate ions. By using the liquid-through type electric double-layer capacitor desalination device 11, the ions in the raw water can be removed by at least several tens of%, and then the ion load of the softener 12 can be reduced to several points. One to one tenth. Therefore, the amount of sodium chloride used in the regeneration of the softener 12 can also be reduced to a fraction of a tenth to a few tenths, and the treated water of the water softener 12 is supplied to the boiler 14 via the water supply tank 13, whereby Significantly reducing the concentration of salts brought into the boiler water can also greatly reduce the increase in conductivity caused by the dissolved salts. Therefore, the blowing water can be drastically reduced, the water and heat discharged by the blowing can be reduced, and the amount of water supplied to the boiler for generating the predetermined steam is also reduced. As a result, there is obtained an advantage that the liquid-through type electric double layer capacitor desalination apparatus 11 or the softener 12 can be made smaller in the amount of treated water, and the amount of sodium chloride used in the regeneration of the softener can be further reduced. Further, by reducing the amount of water supplied to the boiler 14, the amount of water treatment chemicals added to the water supply to a predetermined concentration is also reduced. Further, since the concentration of the boiler water is increased by the reduction of the blow-off, the concentration of the water treatment chemicals which can prevent corrosion or rust in the boiler by maintaining a predetermined concentration in the boiler water can be further lowered as compared with the prior art. . In addition, by adding a water-soluble polymer having a carboxyl group in the molecule to the water supply, it is possible to prevent rusting in the boiler in a hardness component which is extremely contained in the water supply, and to suppress heat transfer loss or corrosion of the rust portion. Occurrence of water treatment.

第1態樣中,較佳為通液型電雙層電容器脫鹽裝置的水回收率設為80%~95%左右,溶解鹽類的除去率設為70%~90%左右。若通液型電雙層電容器脫鹽裝置的水回收率過低則原水使用量增加,若過高則未能充分除去溶解鹽類。若通液型電雙層電容器脫鹽裝置的溶解鹽類的除去率過低,則後段的軟化器的離子負載增大,軟化器的再生頻度增高。若通液型電雙層電容器脫鹽裝置的溶解鹽類的 除去率過高,則藉由使用電力的增加而經濟性降低。 In the first aspect, the water recovery rate of the liquid-through type electric double layer capacitor desalination apparatus is preferably about 80% to 95%, and the removal rate of dissolved salts is about 70% to 90%. If the water recovery rate of the through-liquid type electric double layer capacitor desalination apparatus is too low, the amount of raw water used is increased, and if it is too high, the dissolved salt is not sufficiently removed. If the removal rate of dissolved salts of the through-liquid type electric double layer capacitor desalination apparatus is too low, the ion load of the softener in the latter stage increases, and the frequency of regeneration of the softener increases. Dissolved salt of a liquid-through type electric double layer capacitor desalination device When the removal rate is too high, the economy is lowered by the increase in the use of electric power.

圖4是表示本發明的第2態樣的實施形態的系統圖。將原水通過通液型電雙層電容器脫鹽裝置21而溶解離子降低至數分之一至數十分之一的處理水,不經由軟水器而直接供給至供水箱22。該供水箱22中亦被供給了經回收的蒸氣凝結水(凝汽水)。在該供水箱22的水中,與通液型電雙層電容器脫鹽裝置21的處理水流量成比例地,添加分子內具有羧基的水溶性聚合物而供給至鍋爐。本實施形態中因未使用軟化器而設備變得簡單,並且不需要軟化器的再生用的氯化鈉。而且,被帶入至鍋爐的鹽類濃度與僅利用軟化器處理原水的情況相比得以大幅降低,因而可削減吹除,所排出的熱或水、水處理化學品成分得以削減,供水量減少,藉此添加的水處理化學品的量亦得以削減。而且,作為供水而回收的蒸氣凝結水中所含的來自熱交換器或配管的溶出鐵,藉由通液型電雙層電容器脫鹽裝置21的處理水中所含的硬度成分與所添加的分子內具有羧基的水溶性聚合物的效果,而有效地利用吹除被排出,且可有效地抑制因被帶入至鍋爐內而引起的傳熱面的銹附著。 Fig. 4 is a system diagram showing an embodiment of a second aspect of the present invention. The raw water is passed through the liquid-through type electric double-layer capacitor desalination apparatus 21 to reduce the dissolved ions to one-tenth to one-tenth of the treated water, and is directly supplied to the water supply tank 22 without passing through the water softener. The recovered steam condensate (condensed water) is also supplied to the water supply tank 22. In the water of the water supply tank 22, a water-soluble polymer having a carboxyl group in the molecule is added to the boiler in proportion to the flow rate of the treated water of the liquid-through type electric double-layer capacitor desalination device 21. In the present embodiment, the device is simplified because the softener is not used, and sodium chloride for regeneration of the softener is not required. Moreover, the concentration of the salt brought into the boiler is greatly reduced as compared with the case where the raw water is treated only by the softener, so that the blowing can be reduced, the heat or the water, the water treatment chemical component can be reduced, and the water supply can be reduced. The amount of water treatment chemicals added is also reduced. Further, the molten iron from the heat exchanger or the pipe contained in the vapor condensed water recovered as the water supply has the hardness component contained in the treated water of the liquid-through type electric double layer capacitor desalination device 21 and the added intramolecular The effect of the water-soluble polymer of a carboxyl group is effectively discharged by blowing, and rust adhesion of the heat transfer surface due to being brought into the boiler can be effectively suppressed.

第2態樣中,較佳為通液型電雙層電容器脫鹽裝置的水回收率設為80%~95%左右,溶解鹽類的除去率設為70%~90%左右。若通液型電雙層電容器脫鹽裝置的水回收率過低則原水使用量增加,若過高則未能將溶解鹽類充分除去。若通液型電雙層電容器脫鹽裝置的溶解鹽類的除去率過低則必須使吹除水量增多,但若通液型電雙層電容 器脫鹽裝置的溶解鹽類的除去率過高,則無法藉由通液型電雙層電容器脫鹽裝置的處理水中的鈣而充分獲得上述鐵的銹化防止效果。 In the second aspect, the water recovery rate of the liquid-through type electric double layer capacitor desalination apparatus is preferably about 80% to 95%, and the removal rate of dissolved salts is about 70% to 90%. If the water recovery rate of the through-type electric double-layer capacitor desalination apparatus is too low, the amount of raw water used is increased, and if it is too high, the dissolved salt cannot be sufficiently removed. If the removal rate of the dissolved salt in the through-type electric double-layer capacitor desalination device is too low, the amount of blown water must be increased, but if the flow-through type electric double-layer capacitor When the removal rate of the dissolved salt in the desalination apparatus is too high, the effect of preventing the rust of the iron described above cannot be sufficiently obtained by the calcium in the treated water of the liquid-through type electric double layer capacitor desalination apparatus.

因此,較佳為藉由適當調整通液型電雙層電容器脫鹽裝置的溶解鹽類的除去率,以鍋爐供水中的鈣濃度為0.1 mg~10 mg-CaCO3/L左右的方式使鈣殘留。 Therefore, it is preferable to adjust the removal rate of dissolved salts of the through-liquid type electric double layer capacitor desalination apparatus by appropriately adjusting the calcium concentration in the boiler water supply to about 0.1 mg to 10 mg-CaCO 3 /L. .

作為本發明中使用的分子內具有羧基的水溶性聚合物,可列舉丙烯酸及/或其鹽、馬來酸及/或其鹽、伊康酸及/或其鹽、甲基丙烯酸及/或其鹽等的羧酸及/或其鹽的均聚物,共聚物,或三聚物;2-羥基-3-烯丙氧基丙磺酸及/或其鹽與上述羧酸及/或其鹽的共聚物;2-丙烯醯胺-2-甲基丙磺酸及/或其鹽與上述羧酸及/或其鹽的共聚物;雙(聚-2-羧乙基)膦酸及/或其鹽;羧甲基纖維素等。另外,作為上述羧酸、磺酸、膦酸的鹽,可列舉鈉鹽、鉀鹽等的鹼金屬鹽。 The water-soluble polymer having a carboxyl group in the molecule used in the present invention may, for example, be acrylic acid and/or a salt thereof, maleic acid and/or a salt thereof, itaconic acid and/or a salt thereof, methacrylic acid and/or a homopolymer, a copolymer, or a terpolymer of a carboxylic acid and/or a salt thereof, such as a salt; 2-hydroxy-3-allyloxypropanesulfonic acid and/or a salt thereof, and the above carboxylic acid and/or a salt thereof a copolymer; a copolymer of 2-propenylamine-2-methylpropanesulfonic acid and/or a salt thereof with the above carboxylic acid and/or a salt thereof; bis(poly-2-carboxyethyl)phosphonic acid and/or Its salt; carboxymethyl cellulose and the like. In addition, examples of the salt of the carboxylic acid, the sulfonic acid, and the phosphonic acid include alkali metal salts such as a sodium salt and a potassium salt.

作為分子內具有羧基的水溶性聚合物,其中丙烯酸鈉的均聚物較佳。 As the water-soluble polymer having a carboxyl group in the molecule, a homopolymer of sodium acrylate is preferred.

分子內具有羧基的水溶性聚合物的重量平均分子量較佳為1000~100000,尤佳為1500~50000。若該分子量過大則有藉由與鈣的鍵結而生成凝膠化物,從而使過濾器(strainer)等阻塞之虞。若該分子量過小則有時無法發揮充分效果。 The weight average molecular weight of the water-soluble polymer having a carboxyl group in the molecule is preferably from 1,000 to 100,000, particularly preferably from 1,500 to 50,000. If the molecular weight is too large, a gelation is formed by bonding with calcium, and a strainer or the like is blocked. If the molecular weight is too small, a sufficient effect may not be exhibited.

分子內具有羧基的水溶性聚合物的添加量宜調整為相對於鍋爐供水中的鈣濃度為0.5倍~10倍的濃度,更理想 的是1倍~5倍的濃度。若水溶性聚合物的添加濃度比上述上限多,則自蒸氣凝結水的回收線而帶入的鐵的分散效果降低,銹的附著量增加。若水溶性聚合物的添加濃度比上述下限少,則通液型電雙層電容器脫鹽裝置的處理水中所含的硬度成分對鍋爐內的銹附著的防止效果不充分。 The amount of the water-soluble polymer having a carboxyl group in the molecule should be adjusted to be 0.5 to 10 times the concentration of the calcium in the boiler water supply, and more preferably It is 1 to 5 times the concentration. When the concentration of the water-soluble polymer added is more than the above upper limit, the effect of dispersing iron brought in from the recovery line of the vapor-condensed water is lowered, and the amount of adhesion of rust is increased. When the concentration of the water-soluble polymer to be added is less than the above lower limit, the effect of the hardness component contained in the treated water of the liquid-through type electric double layer capacitor desalination apparatus on the rust adhesion in the boiler is insufficient.

本發明中除上述水溶性聚合物之外,亦可併用一般用作水處理化學品的鹼劑(NaOH、KOH、K2CO3、Na2CO3等)或脫氧劑(肼、單寧、單寧酸及/或其鹽、異抗壞血酸及/或其鹽、抗壞血酸及/或其鹽、葡萄糖等),腐蝕抑制劑(葡萄糖酸及/或其鹽、葡庚糖酸及/或其鹽、丁二酸及/或其鹽、檸檬酸及/或其鹽、酒石酸及/或其鹽等),磷酸及/或其鹽、聚合磷酸及/或其鹽、膦酸及/或其鹽等。 In the present invention, in addition to the above water-soluble polymer, an alkali agent (NaOH, KOH, K 2 CO 3 , Na 2 CO 3 , etc.) or a deoxidizer (tantalum, tannin, etc.) generally used as a water treatment chemical may be used in combination. Tannic acid and/or its salt, isoascorbic acid and/or its salt, ascorbic acid and/or its salt, glucose, etc., corrosion inhibitor (gluconic acid and/or its salt, glucoheptonic acid and/or its salt, Succinic acid and/or a salt thereof, citric acid and/or a salt thereof, tartaric acid and/or a salt thereof, phosphoric acid and/or a salt thereof, a polymerized phosphoric acid and/or a salt thereof, a phosphonic acid and/or a salt thereof.

[實例] [Example]

以下列舉實例及比較例對本發明進行更具體說明。 The invention will be more specifically described below by way of examples and comparative examples.

另外,以下的實例及比較例中處理的原水為下述水質的日本栃木縣野木町的自來水。 In addition, the raw water to be treated in the following examples and comparative examples is the tap water of Noki-cho, Tochigi Prefecture, Japan, which has the following water quality.

<原水水質> <Original water quality>

導電率:25mS/m Conductivity: 25mS/m

M鹼度:23mg-CaCO3/L M alkalinity: 23mg-CaCO 3 /L

二氧化矽:18mg/L Ceria: 18mg/L

Ca硬度:30mg-CaCO3/L Ca hardness: 30mg-CaCO 3 /L

Mg硬度:15mg-CaCO3/L Mg Hardness: 15mg-CaCO 3 / L

[比較例1] [Comparative Example 1]

將野木町水通過陽離子交換樹脂量18L的軟化器所 得的處理水供給至供水箱中,並在其中一邊添加30 mg/L的作為水處理化學品的脫氧劑的異抗壞血酸鈉、及27 mg/L的作為鹼劑的NaOH,該NaOH的鍋爐水中的P鹼度為二氧化矽的1.7倍濃度,一邊以0.450 m3/h而供給至實驗用鍋爐中,在壓力0.7 MPa下以鍋爐水的導電率為300 mS/m的方式一邊吹除一邊運轉10天。 The treatment water obtained by the Nojima water was passed through a softener of a cation exchange resin amount of 18 L to a water supply tank, and 30 mg/L of sodium erythorbate as a deoxidizing agent for water treatment chemicals was added thereto, and 27 mg/ NaOH as an alkali agent of L, the P alkalinity of the NaOH boiler water is 1.7 times the concentration of cerium oxide, and is supplied to the experimental boiler at 0.450 m 3 /h, and the boiler water is at a pressure of 0.7 MPa. The electric conductivity was 300 mS/m, and it was operated for 10 days while being blown off.

此時的吹除率平均為13.5%,蒸發量為0.39 ton/h。而且,試驗期間內進行6次軟化器的再生,再生中所使用的氯化鈉為13.8 kg。 At this time, the purge rate averaged 13.5% and the evaporation amount was 0.39 ton/h. Further, the softener was regenerated six times during the test period, and the sodium chloride used for the regeneration was 13.8 kg.

[比較例2] [Comparative Example 2]

比較例1中,在將野木町水利用軟化器加以處理後,通過逆浸透膜裝置而在水回收率80%下運轉(此時的溶解鹽類的除去率平均為98%),將逆浸透膜裝置的處理水供至供水箱,並在其中一邊添加30 mg/L的作為水處理化學品的脫氧劑的異抗壞血酸鈉、及19 mg/L的作為鹼劑的NaOH,該NaOH的鍋爐水的pH值為11.5且在吹除率3.0%下算出的導電率為300 mS/m,一邊供給至實驗用鍋爐中,在壓力0.7 MPa下運轉10天。 In Comparative Example 1, after the Noki-machi water was treated with a softener, the water was recovered by a reverse osmosis membrane apparatus at a water recovery rate of 80% (the average removal rate of dissolved salts at this time was 98%), and the reverse was saturated. The treated water of the membrane device is supplied to the water supply tank, and 30 mg/L of sodium erythorbate as a deoxidizing agent for water treatment chemicals and 19 mg/L of NaOH as an alkali agent are added to one side of the membrane, and the NaOH boiler water The conductivity was 11.5 and the conductivity calculated at a blow rate of 3.0% was 300 mS/m, and was supplied to an experimental boiler and operated at a pressure of 0.7 MPa for 10 days.

此時的蒸發量為0.39 t/h。對鍋爐的供水量為0.401 m3/h,原水流量平均為0.501 m3/h,試驗期間內進行7次軟化器的再生,再生中所使用的氯化鈉為16.1 kg。 The evaporation amount at this time was 0.39 t/h. The water supply to the boiler was 0.401 m 3 /h, and the raw water flow rate was 0.501 m 3 /h on average. During the test period, the softener was regenerated 7 times, and the sodium chloride used in the regeneration was 16.1 kg.

[實例1] [Example 1]

將野木町水通過通液型電雙層電容器脫鹽裝置,在水回收率90%下運轉(此時的溶解鹽類的除去率平均為 80%),將通液型電雙層電容器脫鹽裝置的處理水與比較例1同樣地通過軟化器所得的處理水供至供水箱,並在其中一邊添加30 mg/L的作為水處理化學品的脫氧劑的異抗壞血酸鈉、及17 mg/L的作為鹼劑的NaOH,該NaOH的鍋爐水中的P鹼度為二氧化矽的1.7倍濃度,一邊供給至實驗用鍋爐中,以在壓力0.7 MPa下鍋爐水的導電率為300 mS/m的方式吹除並運轉10天。 The wild wood water is passed through a liquid-liquid double-layer capacitor desalination device and operated at a water recovery rate of 90% (the average removal rate of dissolved salts at this time is 80%), the treated water of the liquid-through type electric double-layer capacitor desalination apparatus was supplied to the water supply tank by the treated water obtained by the softener in the same manner as in Comparative Example 1, and 30 mg/L was added as a water treatment chemical on one side. The deoxidizer sodium erythorbate and 17 mg/L NaOH as an alkali agent, the P alkalinity of the NaOH boiler water is 1.7 times the concentration of cerium oxide, and is supplied to the experimental boiler at a pressure of 0.7. The boiler water has a conductivity of 300 mS/m at MPa and is blown off and operated for 10 days.

此時的吹除率平均為3.0%,蒸發量為0.39 t/h。對鍋爐的供水量為0.401 m3/h,原水流量平均為0.446 m3/h,試驗期間內進行1次軟化器的再生,再生中所使用的氯化鈉為2.3 kg。 The blow rate at this time was 3.0% on average, and the evaporation amount was 0.39 t/h. The water supply to the boiler was 0.401 m 3 /h, and the raw water flow rate was 0.446 m 3 /h on average. During the test period, the softener was regenerated once, and the sodium chloride used in the regeneration was 2.3 kg.

根據上述比較例1、比較例2及實例1的結果可知為如下。 The results of Comparative Example 1, Comparative Example 2, and Example 1 described above are as follows.

亦即,在利用通液型電雙層電容器脫鹽裝置與軟化器進行處理的實例1中,與僅利用軟化器處理的比較例1相比,水的使用量削減了約1 m3,氯化鈉的使用量削減了11.5(=13.8-2.3)kg,燃料的A柴油的使用量亦削減了2.5%。而且,實例1中,與利用軟化器與逆浸透膜裝置進行處理的比較例2相比,水的使用量削減了132(=(0.501-0.446)×24×10)m3,氯化鈉的使用量削減了13.8(=16.1-2.3)kg。燃料使用量同等。 That is, in the example 1 which was treated by the through-liquid type electric double layer capacitor desalination apparatus and the softener, the amount of water used was reduced by about 1 m 3 and chlorinated as compared with the comparative example 1 which was treated only by the softener. The use of sodium was reduced by 11.5 (=13.8-2.3) kg, and the use of fuel A diesel was also reduced by 2.5%. Further, in Example 1, the amount of water used was reduced by 132 (= (0.501 - 0.446) × 24 × 10) m 3 compared with Comparative Example 2 which was treated by the softener and the reverse osmosis membrane device, and sodium chloride was used. The usage was reduced by 13.8 (=16.1-2.3) kg. The amount of fuel used is the same.

[實例2~實例7] [Example 2 to Example 7]

將野木町水通過通液型電雙層電容器脫鹽裝置,在水回收率90%下運轉(此時的溶解鹽類的除去率平均為 80%),將通液型電雙層電容器脫鹽裝置的處理水利用軟化器通水而將水中的Ca離子及Mg離子置換為Na離子後供給至容量10 L的供水箱中。而且,在該供水箱中,模擬出蒸氣凝結水對供水箱的回收水,將在加熱至90℃的純水中設想回收線的鐵的溶出而以鐵濃度為2 mg/L的方式添加氯化鐵所得的水以4 L/h進行供給。在來自該供水箱的供水中,一邊添加10 mg/L的作為水處理化學品的腐蝕抑制劑的丁二酸,且以表1所示的添加濃度添加表1所示的水溶性聚合物,並添加13 mg/L的作為鹼劑的NaOH,該NaOH的鍋爐水中的P鹼度為二氧化矽的1.7倍濃度,一邊供給至容量5 L的不銹鋼製測試鍋爐中,在壓力0.7 MPa、蒸發量8 L/h、吹除率5%下運轉。 The wild wood water is passed through a liquid-liquid double-layer capacitor desalination device and operated at a water recovery rate of 90% (the average removal rate of dissolved salts at this time is 80%), the treated water of the liquid-through type electric double-layer capacitor desalination device was passed through a softener to pass water, and Ca ions and Mg ions in the water were replaced with Na ions, and then supplied to a water supply tank having a capacity of 10 L. Further, in the water supply tank, the recovered water of the steam condensate to the water supply tank is simulated, and the elution of iron in the recovery line is assumed in pure water heated to 90 ° C, and chlorine is added in such a manner that the iron concentration is 2 mg/L. The water obtained by the iron is supplied at 4 L/h. In the water supply from the water supply tank, 10 mg/L of succinic acid as a corrosion inhibitor of water treatment chemicals was added, and the water-soluble polymer shown in Table 1 was added at the added concentration shown in Table 1, And adding 13 mg/L of NaOH as an alkali agent, the P alkalinity of the NaOH boiler water is 1.7 times the concentration of cerium oxide, and is supplied to a stainless steel test boiler having a capacity of 5 L, at a pressure of 0.7 MPa, and evaporated. The amount is 8 L/h and the blowing rate is 5%.

在連續運轉1週後停止而取出傳熱管(不銹鋼製,表面積200 cm2×3根),結果確認到大量的紅褐色銹的附著,因而在移除後進行附著量測定。將結果表示於表1中。 After one continuous operation, the heat transfer tube (stainless steel, surface area: 200 cm 2 × 3) was taken out, and it was confirmed that a large amount of reddish brown rust adhered. Therefore, the amount of adhesion was measured after removal. The results are shown in Table 1.

[實例8~實例19] [Example 8 to Example 19]

實例2中,去掉軟化器,將作為水溶性聚合物的表1所示的水溶性聚合物以表1所示的添加濃度而添加,除此之外在同樣的條件下運轉,同樣地對連續運轉1週後的傳熱管的附著量進行測定。將結果表示於表1中。 In Example 2, the softener was removed, and the water-soluble polymer shown in Table 1 as a water-soluble polymer was added at the added concentration shown in Table 1, except that it was operated under the same conditions, and was similarly continuous. The amount of adhesion of the heat transfer tubes after one week of operation was measured. The results are shown in Table 1.

實例1~實例17中,通液型電雙層電容器脫鹽裝置的處理水中的鈣濃度為6 mg-CaCO3/L,而在將該通液型電雙層電容器脫鹽裝置的處理水進而利用軟化器進行處理後、與上述凝結水的回收水的模擬水一併作為鍋爐供水的實例 2~實例7中,鍋爐供水的鈣濃度小於0.1 mg-CaCO3/L。而且,在將通液型電雙層電容器脫鹽裝置的處理水不利用軟化器進行處理而與上述凝結水的回收水的模擬水一併作為鍋爐供水的實例8~實例19中,鍋爐供水中的鈣濃度為3 mg-CaCO3/L。 In Examples 1 to 17, the calcium concentration in the treated water of the liquid-through type electric double-layer capacitor desalination device is 6 mg-CaCO 3 /L, and the treated water of the through-type electric double-layer capacitor desalination device is further softened. After the treatment, in the example 2 to the example 7 of the boiler water supply together with the simulated water of the condensed water recovered, the calcium concentration of the boiler water supply is less than 0.1 mg-CaCO 3 /L. Further, in the case of the boiler water supply, the treated water of the liquid-through type electric double-layer capacitor desalination apparatus is treated without using the softener and the simulated water of the condensed water recovered as the boiler water supply. The calcium concentration is 3 mg-CaCO 3 /L.

實例2~實例19的相對於鍋爐供水的鈣濃度的聚合物添加濃度比如表1所示。 The polymer addition concentrations of the calcium concentrations of Examples 2 to 19 relative to the boiler water supply are shown in Table 1.

根據表1的實例2~實例19的結果可知,在將蒸氣凝結水回收並再利用的情況下,不使用軟化器,而僅利用通液型電雙層電容器脫鹽裝置添加規定量的分子內具有羧基的水溶性聚合物,藉此可防止銹缺陷而繼續穩定運轉。 According to the results of Examples 2 to 19 of Table 1, it is understood that when the vapor condensed water is recovered and reused, the softener is not used, and only a predetermined amount of molecules are added by the through-liquid type electric double layer capacitor desalination device. A water-soluble polymer of a carboxyl group, thereby preventing rust defects and continuing stable operation.

已使用特定的態樣對本發明進行了詳細說明,但本領域技術人員應當明白只要不脫離本發明的意圖及範圍則可進行各種變更。 The present invention has been described in detail with reference to the specific embodiments of the invention.

另外,本申請案基於2011年9月15日提出申請的日本專利申請案(日本專利特願2011-201947),其整體藉由引用而援用於本文中。 In addition, the present application is based on a Japanese patent application (Japanese Patent Application No. 2011-201947) filed on Sep.

1‧‧‧陰極側的集電極 1‧‧‧ Collector on the cathode side

2、4‧‧‧活性碳層 2, 4‧‧‧active carbon layer

3‧‧‧陽極側的集電極 3‧‧‧ Collector on the anode side

11、21‧‧‧脫鹽裝置 11, 21‧‧‧ desalination device

12‧‧‧軟化器 12‧‧‧Softener

13、22‧‧‧供水箱 13, 22‧‧‧ water supply tank

14、23‧‧‧鍋爐 14, 23‧‧ ‧ boiler

圖1是表示軟化器的原理的模式圖,且表示施加電壓(脫鹽)時。 Fig. 1 is a schematic view showing the principle of a softener, and shows a case where a voltage (desalting) is applied.

圖2是表示軟化器的原理的模式圖,且表示短路(排出)時。 Fig. 2 is a schematic view showing the principle of a softener, and shows a short circuit (discharge).

圖3是表示本發明的第1態樣的水處理方法的實施形態的一例的系統圖。 3 is a system diagram showing an example of an embodiment of a water treatment method according to a first aspect of the present invention.

圖4是表示本發明的第2態樣的水處理方法的實施形態的一例的系統圖。 Fig. 4 is a system diagram showing an example of an embodiment of a water treatment method according to a second aspect of the present invention.

1‧‧‧陰極側的集電極 1‧‧‧ Collector on the cathode side

2、4‧‧‧活性碳層 2, 4‧‧‧active carbon layer

3‧‧‧陽極側的集電極 3‧‧‧ Collector on the anode side

Claims (6)

一種水處理方法,其在將蒸氣凝結水作為供水而回收、再利用的蒸氣產生設備中,將不使用軟化器而將原水通過通液型電雙層電容器脫鹽裝置所獲得的處理水、與上述蒸氣凝結水的回收水作為上述供水而供給至蒸氣產生器,並且在上述供水中,相對於上述供水中的鈣量,添加1重量倍~5重量倍的分子內具有羧基的水溶性聚合物,其特徵在於:調整上述通液型電雙層電容器脫鹽裝置的溶解鹽類的除去率,而以使上述蒸氣產生器的供水的鈣的濃度成為0.1mg-CaCO3/L~10mg-CaCO3/L的方式使鈣殘留。 A water treatment method for treating water obtained by passing a raw water through a liquid-through type electric double layer capacitor desalination apparatus without using a softener in a steam generation apparatus that recovers and reuses steam condensed water as a water supply The recovered water of the steam condensed water is supplied to the steam generator as the water supply, and the water-soluble polymer having a carboxyl group in the molecule is added in an amount of 1 to 5 times by weight with respect to the amount of calcium in the water supply. It is characterized in that the removal rate of dissolved salts of the liquid-pass type electric double layer capacitor desalination device is adjusted so that the concentration of calcium supplied to the steam generator is 0.1 mg-CaCO 3 /L 10 mg-CaCO 3 / The way L makes calcium residue. 如申請專利範圍第1項所述之水處理方法,其中上述具有羧基的水溶性聚合物是選自由以下化合物所組成之群組中的至少一種:丙烯酸及/或其鹽、馬來酸及/或其鹽、伊康酸及/或其鹽、甲基丙烯酸及/或其鹽等的羧酸及/或其鹽的均聚物,共聚物,或三聚物;2-羥基-3-烯丙氧基丙磺酸及/或其鹽與上述羧酸及/或其鹽的共聚物;2-丙烯醯胺-2-甲基丙磺酸及/或其鹽與上述羧酸及/或其鹽的共聚物;雙(聚-2-羧乙基)膦酸及/或其鹽;羧甲基纖維素。 The water treatment method according to claim 1, wherein the water-soluble polymer having a carboxyl group is at least one selected from the group consisting of acrylic acid and/or a salt thereof, maleic acid and/or a homopolymer, a copolymer, or a trimer of a carboxylic acid and/or a salt thereof, or a salt thereof, itaconic acid and/or a salt thereof, methacrylic acid and/or a salt thereof; 2-hydroxy-3-ene a copolymer of propoxypropanesulfonic acid and/or a salt thereof and the above carboxylic acid and/or a salt thereof; 2-propenylamine-2-methylpropanesulfonic acid and/or a salt thereof and the above carboxylic acid and/or a copolymer of a salt; bis(poly-2-carboxyethyl)phosphonic acid and/or a salt thereof; carboxymethylcellulose. 如申請專利範圍第1項所述之水處理方法,其中上述具有羧基的水溶性聚合物為丙烯酸鈉的均聚物。 The water treatment method according to claim 1, wherein the water-soluble polymer having a carboxyl group is a homopolymer of sodium acrylate. 如申請專利範圍第1項所述之水處理方法,其中上述具有羧基的水溶性聚合物為聚丙烯酸-2-羥基-3-烯丙氧基丙磺酸鈉、聚丙烯酸-2-丙烯醯胺-2-甲基丙磺酸 鈉、聚雙(聚-2-羧乙基)膦酸鈉、羧甲基纖維素。 The water treatment method according to claim 1, wherein the water-soluble polymer having a carboxyl group is polyacrylic acid sodium 2-hydroxy-3-allyloxypropane sulfonate or polyacrylic acid-2-acrylamide -2-methylpropanesulfonic acid Sodium, poly(poly-2-carboxyethyl)phosphonate, carboxymethylcellulose. 如申請專利範圍第1項所述之水處理方法,其中上述原水為井水、自來水、或河川水。 The water treatment method according to claim 1, wherein the raw water is well water, tap water, or river water. 如申請專利範圍第1項所述之水處理方法,其中上述通液型電雙層電容器脫鹽裝置的溶解鹽類的除去率為70%~90%。 The water treatment method according to claim 1, wherein the removal rate of dissolved salts of the liquid-through type electric double layer capacitor desalination device is 70% to 90%.
TW101133035A 2011-09-15 2012-09-10 Water treatment method TWI548595B (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2011201947A JP5987286B2 (en) 2011-09-15 2011-09-15 Water treatment method

Publications (2)

Publication Number Publication Date
TW201313619A TW201313619A (en) 2013-04-01
TWI548595B true TWI548595B (en) 2016-09-11

Family

ID=47883164

Family Applications (1)

Application Number Title Priority Date Filing Date
TW101133035A TWI548595B (en) 2011-09-15 2012-09-10 Water treatment method

Country Status (5)

Country Link
JP (1) JP5987286B2 (en)
MY (1) MY171036A (en)
SG (1) SG11201400256PA (en)
TW (1) TWI548595B (en)
WO (1) WO2013038933A1 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI739524B (en) * 2020-07-22 2021-09-11 財團法人工業技術研究院 Water treatment device and water treatment method

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2015068797A1 (en) 2013-11-07 2015-05-14 富士フイルム株式会社 Ion exchange membrane electrode assembly, method for manufacturing same, and capacitor demineralization device
CN104528958B (en) * 2015-01-13 2016-04-06 周新华 The flexible water treatment ion bar of high pressure static electricity
CN111495193A (en) * 2019-05-16 2020-08-07 河北权科环保科技有限公司 Reverse osmosis membrane repairing reagent and preparation method and application thereof
JP6864275B2 (en) * 2020-03-17 2021-04-28 三浦工業株式会社 Fuel cell system
ES2992658T3 (en) * 2022-02-16 2024-12-16 Hygromatik Gmbh Electrode steam humidifier and method for its operation

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002273439A (en) * 2001-03-22 2002-09-24 Kurita Water Ind Ltd Desalination method and device
JP2008221143A (en) * 2007-03-13 2008-09-25 Kurita Water Ind Ltd Magnesium scale inhibitor

Family Cites Families (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000154996A (en) * 1998-08-19 2000-06-06 Miura Co Ltd Method for removing scale of boiler
JP4135801B2 (en) * 1999-09-24 2008-08-20 オルガノ株式会社 Liquid passing method and apparatus for liquid passing capacitor
JP2002210468A (en) * 2001-01-19 2002-07-30 Kurita Water Ind Ltd Desalination apparatus and desalination method
JP2003039070A (en) * 2001-07-27 2003-02-12 Kurita Water Ind Ltd Desalinated water production apparatus and desalinated water production method
JP4117607B2 (en) * 2002-10-01 2008-07-16 栗田工業株式会社 Cooling water treatment method
JP2008006369A (en) * 2006-06-29 2008-01-17 Kurita Water Ind Ltd Scale prevention method
JP2008209126A (en) * 2007-02-23 2008-09-11 Kurita Water Ind Ltd Scale adhesion determination agent and scale adhesion determination method
JP5273378B2 (en) * 2009-03-25 2013-08-28 三浦工業株式会社 Steam boiler apparatus and operation method thereof
JP5402669B2 (en) * 2010-01-22 2014-01-29 栗田工業株式会社 Water treatment method for boiler water system

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002273439A (en) * 2001-03-22 2002-09-24 Kurita Water Ind Ltd Desalination method and device
JP2008221143A (en) * 2007-03-13 2008-09-25 Kurita Water Ind Ltd Magnesium scale inhibitor

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI739524B (en) * 2020-07-22 2021-09-11 財團法人工業技術研究院 Water treatment device and water treatment method

Also Published As

Publication number Publication date
MY171036A (en) 2019-09-23
TW201313619A (en) 2013-04-01
JP5987286B2 (en) 2016-09-07
WO2013038933A1 (en) 2013-03-21
SG11201400256PA (en) 2014-03-28
JP2013063364A (en) 2013-04-11

Similar Documents

Publication Publication Date Title
TWI548595B (en) Water treatment method
JP5873771B2 (en) Organic wastewater treatment method and treatment apparatus
CN103339070B (en) Use the water treatment of Bipolar Membrane
JP4449204B2 (en) Boiler feed water treatment apparatus and boiler feed water treatment method
JP2007528781A (en) Continuous electrodeionization apparatus and method
WO2015012054A1 (en) Method and device for treating boron-containing water
JP2011131210A (en) Device and method for treating nitrogen compound-containing acidic solutions
TWI540103B (en) Method for removing boron from a boron-containing wastewater
CN104532283A (en) Method and device for producing caustic soda through electrolysis by replacing part of fine brine with light salt brine
CN114368866A (en) Method for zero discharge of electroplating nickel wastewater
JP2009226315A (en) Electric deionized water manufacturing device and manufacturing method of deionized water
CN203768157U (en) Ion exchange resin regenerated waste water resource recycling system
KR102543734B1 (en) Desalting apparatus for resource recovery from seawater concentrate
CN103936197B (en) The reverse osmosis concentrated draining reuse technology of trade effluent and device
CN105236527B (en) A three-dimensional electrode device and method for synchronous and continuous desalination and organic pollutant removal of wastewater
Tao et al. RO brine treatment and recovery by biological activated carbon and capacitive deionization process
JP2005066544A (en) Method for recovering monoethanolamine
JP4152544B2 (en) Deionized water production method and apparatus
JP2009160500A (en) Ultrapure water production method and apparatus
JP2011131209A (en) Method and apparatus for treating acidic solution
TW201615557A (en) Processing method and processing device for ammonia-containing drainage water
JP2012196630A (en) Treatment equipment and treatment method of acid liquid
JP2012196626A (en) Treatment equipment and treatment method of acid liquid
JP7261711B2 (en) Ultrapure water production system and ultrapure water production method
JP6924300B1 (en) Wastewater treatment method, ultrapure water production method and wastewater treatment equipment

Legal Events

Date Code Title Description
MM4A Annulment or lapse of patent due to non-payment of fees