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JPH039797B2 - - Google Patents
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JPH039797B2 - - Google Patents

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Publication number
JPH039797B2
JPH039797B2 JP18039182A JP18039182A JPH039797B2 JP H039797 B2 JPH039797 B2 JP H039797B2 JP 18039182 A JP18039182 A JP 18039182A JP 18039182 A JP18039182 A JP 18039182A JP H039797 B2 JPH039797 B2 JP H039797B2
Authority
JP
Japan
Prior art keywords
mixed bed
condensate
water
hydrazine
mixed
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.)
Expired
Application number
JP18039182A
Other languages
Japanese (ja)
Other versions
JPS5969188A (en
Inventor
Junichi Sato
Hiroshi Tawara
Taizo Sugyama
Takeshi Tsurumi
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kansai Electric Power Co Inc
Original Assignee
Kansai Denryoku KK
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 Kansai Denryoku KK filed Critical Kansai Denryoku KK
Priority to JP18039182A priority Critical patent/JPS5969188A/en
Publication of JPS5969188A publication Critical patent/JPS5969188A/en
Publication of JPH039797B2 publication Critical patent/JPH039797B2/ja
Granted legal-status Critical Current

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  • Treatment Of Water By Ion Exchange (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

本発明は復水の処理方法に関し、詳しくは、発
電ボイラなどのアンモニアを含む復水を混床式イ
オン交換樹脂塔を用いて処理する方法に関する。 火力発電所などにおいては、ボイラ復水は復水
処理装置で脱塩処理を施した後、アンモニアでPH
値を所定値に調整し、再びボイラ給水として循環
使用されている。 復水処理装置は、通常、並列に配置された混床
塔(混床式イオン交換樹脂床塔)で構成され、混
床塔には水素形強酸性カチオン交換樹脂(以下、
H形カチオン樹脂という)と、遊離塩基形強塩基
性アニオン交換樹脂(以下、OH型アニオン樹脂
という)とを混合状態で充填して、復水中のイオ
ン除去に供されている。 復水中には、ナトリウムイオン、塩素イオン、
鉄イオンなどの不純物の他に、PH調整用のアンモ
ニウムイオンが多量(通常0.5〜10mg/)に含
まれているので、混床塔に復水を通水するとH形
カチオン樹脂は不純物の他に、このアンモニウム
イオンをも捕捉してしまい、飽和後は結局、混床
塔から水酸化アンモニウムがリークすることにな
る。この段階で復水の通水を停止して混床塔を再
生し、再度復水処理に用いる方法を通称H形運転
という。 復水中にはアンモニウムイオンが多量に含まれ
るため、混床塔をH形運転すると再生を頻繁に行
なわれなければならず、再生剤とアンモニアを浪
費することになる。そこで、混床塔内のH形カチ
オン樹脂がアンモニウムイオンを捕捉して飽和し
た後も復水の通水を継続し、復水中の不純物を水
酸化アンモニウムの形で置換することも行なわれ
ており、これを通称NH4形運転という。 火力発電所では、電力需要に合わせて深夜、週
末、盆・暮れ・正月などの時期には運転を停止す
ることがあり、停止中には、ボイラ缶内にヒドラ
ジンを多量(0.5〜500mg/)に添加して腐食を
防止している。また、脱酸素剤としてヒドラジン
を給水中に常時数+μg/程度添加することも
ある。このヒドラジンはH形運転時に混床塔中に
捕捉されているが、H形運転から再生を行なわず
にNH4形運転に移行すると、その転移時にヒド
ラジンが多量にリークする。ヒドラジンが多量に
リークすると、節炭器入口の給水流量に対するヒ
ドラジンの濃度管理が困難になるため、従来の停
止−再起動を繰り返すボイラの復水処理では、H
形運転のみが採用され、H形運転にひきつづいて
NH4形運転ができなかつたという問題があつた。 本発明は、上記の問題点を解決するためになさ
れたものであり、新らたな設備を追加することな
く、また既存設備の機械的改造を行うことなく、
ヒドラジンの一時的大量リークを防止する方法を
提供することを目的とする。 すなわち、水素形強酸性カチオン交換樹脂と遊
離塩基形強塩基性アニオン交換樹脂とを混合して
充填した混床塔にアンモニア含有復水を通水して
復水を処理し、混床塔内の水素形強酸性カチオン
交換樹脂がアンモニウムイオンを捕捉して飽和し
た後も復水の通水を継続する方法において、混床
塔の処理水中にヒドラジンが漏出し始めるまでは
採水し、その後採水を停止して、混床の撹拌を行
つたのち、通水を再開することを特徴とする復水
処理方法である。 混床の撹拌は、混床塔内で行つてもよいし、塔
外で行つてもよい。撹拌手段としては、常法の空
気撹拌法が採用できる。 次に、撹拌を塔外で行う場合を列に挙げる。第
1図は、本発明を実施するための装置について示
す概略図であり、復水はライン1からイオン交換
樹脂2(H形カチオン樹脂およびOH形アニオン
樹脂)を充填した混床塔3に下向流で供給され
る。混床塔3の下部には、集水装置4が設置さ
れ、処理水が流出する。処理水にヒドラジンが漏
出し始めたら通水を停止し、イオン交換樹脂2を
ライン5により、再生塔7へ移送する。従来の混
床塔ではヒドラジンのリークを防止するために、
イオン交換樹脂2に吸着したヒドラジンは、ライ
ン8より注入される酸、塩基等化学薬品による再
生操作により、樹脂よりライン9をへて、系外へ
排出されていた。 火力発電所で腹水脱塩に使用される混床塔の樹
脂は、通常材質の防食の目的で注入されるアンモ
ニア、ヒドラジンを交換、吸着しているのみで、
これらの成分を化学薬剤により樹脂より溶離、排
出することは、資源節約の観点からも望ましくな
い。そこで本発明法では、再生塔7へ移送された
イオン交換樹脂2に対し、ライン8より純水、空
気を導入して物理的撹拌処理を行うものである。
その際、ライン10から酸化鉄のような金属酸化
物を排出してもよい。純水、空気により、混合、
清浄化されたイオン交換樹脂2は、ライン6を経
て、混床塔3へ戻され、通水が再開される。 混床塔に、復水を通水すると、復水中のアンモ
ニア、ヒドラジンは除去され、その量に見合う分
のH形カチオン樹脂は、アンモニア形、ヒドラジ
ン形へ転換し、吸着帯を構成する。第2−a図に
混床塔から、ヒドラジンが漏出し始めた時の混床
塔内のH形カチオン交換樹脂の吸着帯の状態模式
図を示す。 一方、火力発電所の通常の運転においては、復
水中にはアンモニアは含まれるが、ヒドラジンは
非常に微量しか含まれないため、混床塔のアンモ
ニア形運転が実施される。その際、電力需要に合
わせて発電ボイラの停止−再起動を繰り返すと、
保缶中に添加されたヒドラジンが混床塔に流入
し、処理水に漏出し始める。この時点の混床塔内
のイオン交換樹脂の吸着帯の状態模式図を、第2
−b図に示す。第2−a図または第2b図の状態
の混床を前述の第1図に示した要領で撹拌を行つ
たときのカチオン交換樹脂の吸着帯の状態模式図
を第3−a図、第3−b図に示す。 混床塔から漏出するヒドラジンの濃度は、下部
層のヒドラジンの含有比率と、下部層における水
のPHに依存する。第3−a図で明らかなように、
樹脂層におけるヒドラジンの分布は、上部から下
部まで均一で、ピーク状態は消滅し、ヒドラジン
の一時的大量リークは防止され、H形運転から
NH4形運転に円滑に移行する。また第3−b図
で明らかなようにアンモニア形運転時のヒドラジ
ン一時流入に対し、処理水へ漏洩するヒドラジン
量を安定した低い値に保つことができ、停止、再
起動を繰り返すボイラの復水処理であつても、円
滑にNH4形運転を行なうことができる。すなわ
ち、本発明は復水の水質の一時的な急変を、復水
の処理水の水質において長期的緩変とする効果を
有する。 実施例 1 H形に再生された強酸性カチオン交換樹脂(ダ
イヤイオンPK228:(株)三菱化成工業製)の4.0
とOH形に再生された強塩基性アニオン交換樹脂
(ダイヤイオンPA312;同)1.9を混合し、内径
80mmφのカラムに充填して混床塔を形成し、カラ
ム頂部に復水入口、カラム下部に復水出口を設け
た。この混床塔12、アンモニア0.7ppmを含む
復水の一部を、25日間通水した。この間4日目の
1日間は、ボイラの運転が停止され、保缶剤とし
てのヒドラジンが、0.65mg/の濃度で復水に混
入した。 16.2日通水した時点で、カチオン交換樹脂が殆
どアンモニア形になり、処理水中にヒドラジンが
0.010mg/検出されたので、通水を停止し、樹
脂層を空気により混合し純水により上昇流で洗浄
する操作を2回繰り返し、最後に空気により混合
し、復水の通水を再開した。 この時の処理水質は、下表のとおりであつた。
The present invention relates to a method for treating condensate, and more particularly, to a method for treating condensate containing ammonia from a power generation boiler or the like using a mixed-bed ion exchange resin column. In thermal power plants, etc., boiler condensate is desalted in a condensate treatment device and then PH-treated with ammonia.
The value is adjusted to a predetermined value and the water is recycled again as boiler feed water. Condensate treatment equipment usually consists of mixed bed towers (mixed bed type ion exchange resin bed towers) arranged in parallel, and the mixed bed towers contain hydrogen-form strongly acidic cation exchange resins (hereinafter referred to as
The tank is filled with a mixture of a free base type strongly basic anion exchange resin (hereinafter referred to as an OH type anion resin) and used for removing ions from condensate. Condensate contains sodium ions, chloride ions,
In addition to impurities such as iron ions, it contains a large amount (usually 0.5 to 10 mg/) of ammonium ions for pH adjustment, so when condensate is passed through a mixed bed column, H-type cation resin contains not only impurities but also ammonium ions for pH adjustment. , this ammonium ion is also captured, and after saturation, ammonium hydroxide eventually leaks from the mixed bed column. At this stage, the flow of condensate is stopped, the mixed bed tower is regenerated, and the mixed bed tower is used again for condensate treatment, commonly known as H-type operation. Since the condensate contains a large amount of ammonium ions, when the mixed bed column is operated in the H type, regeneration must be performed frequently, resulting in waste of regenerant and ammonia. Therefore, even after the H-type cation resin in the mixed bed column captures ammonium ions and becomes saturated, condensate water continues to flow, and impurities in the condensate are replaced in the form of ammonium hydroxide. , this is commonly known as NH 4 type operation. Thermal power plants sometimes suspend operation at midnight, on weekends, during Obon, end of the year, and New Year's holidays to meet power demand.During shutdown periods, a large amount of hydrazine (0.5 to 500 mg/) is placed in the boiler can. It is added to prevent corrosion. Further, as an oxygen scavenger, hydrazine may be constantly added to the water supply in an amount of approximately several μg/kg. This hydrazine is captured in the mixed bed column during H-type operation, but if H-type operation is transferred to NH 4 type operation without regeneration, a large amount of hydrazine leaks during the transition. If a large amount of hydrazine leaks, it becomes difficult to control the concentration of hydrazine in relation to the water supply flow rate at the inlet of the economizer.
Only type operation was adopted, followed by H type operation.
There was a problem that the NH4 type could not be operated. The present invention was made to solve the above-mentioned problems, and it can be done without adding new equipment or mechanically modifying existing equipment.
The purpose of the present invention is to provide a method for preventing temporary large-scale leakage of hydrazine. That is, ammonia-containing condensate is passed through a mixed-bed column filled with a mixture of a hydrogen-type strongly acidic cation exchange resin and a free-base-type strongly basic anion exchange resin, and the condensate is treated. In a method in which condensate water continues to flow even after the hydrogen-type strongly acidic cation exchange resin captures ammonium ions and becomes saturated, water is sampled until hydrazine begins to leak into the treated water of the mixed bed tower, and then water is sampled. This condensate treatment method is characterized by stopping the water flow, stirring the mixed bed, and then restarting water flow. The mixed bed may be stirred within the mixed bed column or outside the column. As the stirring means, a conventional air stirring method can be employed. Next, cases in which stirring is performed outside the tower are listed. FIG. 1 is a schematic diagram showing an apparatus for carrying out the present invention, in which condensate flows down from line 1 to a mixed bed tower 3 filled with ion exchange resin 2 (H type cation resin and OH type anion resin). Supplied in countercurrent. A water collection device 4 is installed at the bottom of the mixed bed tower 3, and the treated water flows out. When hydrazine begins to leak into the treated water, the water flow is stopped and the ion exchange resin 2 is transferred to the regeneration tower 7 via the line 5. In conventional mixed bed towers, to prevent hydrazine leakage,
The hydrazine adsorbed on the ion exchange resin 2 was discharged from the resin to the outside of the system through a line 9 through a regeneration operation using chemicals such as acids and bases injected through a line 8. The resin in mixed bed towers used for ascites desalination at thermal power plants only replaces and adsorbs ammonia and hydrazine, which are normally injected into the material to prevent corrosion.
It is undesirable from the viewpoint of resource conservation to elute and discharge these components from the resin using chemical agents. Therefore, in the method of the present invention, the ion exchange resin 2 transferred to the regeneration tower 7 is subjected to a physical agitation treatment by introducing pure water and air through the line 8.
At this time, a metal oxide such as iron oxide may be discharged from the line 10. Mixed by pure water and air,
The cleaned ion exchange resin 2 is returned to the mixed bed column 3 via the line 6, and water flow is resumed. When condensate is passed through the mixed bed column, ammonia and hydrazine in the condensate are removed, and an amount of H-type cation resin corresponding to the amount thereof is converted to ammonia and hydrazine forms, forming an adsorption zone. FIG. 2-a shows a schematic diagram of the state of the adsorption zone of the H type cation exchange resin in the mixed bed tower when hydrazine begins to leak out from the mixed bed tower. On the other hand, in normal operation of a thermal power plant, condensate contains ammonia, but only a very small amount of hydrazine, so ammonia-type operation of a mixed bed column is carried out. At that time, if the power generation boiler is repeatedly stopped and restarted according to the electricity demand,
The hydrazine added in the holding tank flows into the mixed bed tower and begins to leak into the treated water. The schematic diagram of the state of the adsorption zone of the ion exchange resin in the mixed bed column at this point is shown in the second diagram.
-b Shown in figure. Figures 3-a and 3 show schematic diagrams of the state of the adsorption zone of the cation exchange resin when the mixed bed in the state shown in Figure 2-a or Figure 2-b is stirred in the manner shown in Figure 1 above. -b Shown in figure. The concentration of hydrazine leaking from the mixed bed tower depends on the content ratio of hydrazine in the lower layer and the pH of water in the lower layer. As is clear from Figure 3-a,
The distribution of hydrazine in the resin layer is uniform from the top to the bottom, the peak state disappears, the temporary large amount of leakage of hydrazine is prevented, and the H-type operation is stopped.
Smooth transition to NH4 type operation. In addition, as shown in Figure 3-b, the amount of hydrazine leaking into the treated water can be kept at a stable low value against the temporary inflow of hydrazine during ammonia type operation, and the condensate of the boiler that is repeatedly stopped and restarted can be kept at a stable low value. Even when processing, NH 4 type operation can be carried out smoothly. That is, the present invention has the effect of making a temporary sudden change in the water quality of condensate into a long-term gradual change in the water quality of treated condensate water. Example 1 4.0 of strongly acidic cation exchange resin (Diaion PK228: manufactured by Mitsubishi Chemical Industries, Ltd.) regenerated into H-form
and strong basic anion exchange resin (Diaion PA312; the same) 1.9% regenerated into OH form.
A mixed bed column was formed by filling an 80 mmφ column, with a condensate inlet at the top of the column and a condensate outlet at the bottom of the column. A portion of the condensate containing 0.7 ppm of ammonia was passed through this mixed bed column 12 for 25 days. During this period, the boiler operation was stopped for one day, the fourth day, and hydrazine as a preservative was mixed into the condensate at a concentration of 0.65 mg/day. 16. After 2 days of water passage, the cation exchange resin becomes mostly ammonia, and hydrazine is present in the treated water.
0.010 mg/ was detected, so water flow was stopped, the resin layer was mixed with air, and purified water was washed in an upward flow twice. Finally, after mixing with air, water flow of condensate was resumed. . The quality of the treated water at this time was as shown in the table below.

【表】 比較例 1 実施例1と同様の混床塔を用い、実施例1と平
行して腹水脱塩を行い、ヒドラジンが漏出し始め
ても、樹脂の撹拌を行わないで通水を継続したと
ころ、処理水中のヒドラジンは下表のようであつ
た。
[Table] Comparative Example 1 Using the same mixed bed tower as in Example 1, ascites desalination was carried out in parallel with Example 1, and even when hydrazine started leaking, water flow was continued without stirring the resin. However, the hydrazine in the treated water was as shown in the table below.

【表】 この表から通水日17日目では、最大0.84mg/
のヒドラジンが処理水に漏洩し、ボイラ給水とし
ては適さないことがわかる。 実施例 2 実施例1に引き続き、26日目はボイラの運転が
停止され、27日目にアンモニア形の運転を再開し
たところ、急に復水に0.65mg/のヒドラジンが
5時間流入した。その直後の処理水中のヒドラジ
ン量は、0.005mg/以下であつたが、10時間後
のヒドラジン量が、0.010mg/に上昇し始めた。
そこで、通水を一時停止し、樹脂層を空気撹拌し
たのち、通水を再開した。再開直後から、3日間
はヒドラジンの漏出濃度は安定して、0.030mg/
であつた。 比較例 2 比較例1に引き続く復水処理において、27日目
の0.65mg/のヒドラジンが5時間流入した直後
の処理水中のヒドラジン量は、0.005mg/以下
であつたが10時間後のヒドラジン量が0.010mg/
となり、さらに増加を続け、28日目には、0.14
mg/に達し、後漸滅した。
[Table] From this table, on the 17th day of water flow, the maximum
It can be seen that hydrazine leaked into the treated water, making it unsuitable for boiler feed water. Example 2 Continuing from Example 1, the boiler operation was stopped on the 26th day, and when the ammonia boiler operation was restarted on the 27th day, 0.65 mg/hydrazine suddenly flowed into the condensate for 5 hours. Immediately after that, the amount of hydrazine in the treated water was 0.005 mg/or less, but after 10 hours, the amount of hydrazine began to rise to 0.010 mg/.
Therefore, the water flow was temporarily stopped, the resin layer was agitated with air, and then the water flow was restarted. Immediately after restarting, the leakage concentration of hydrazine remained stable for 3 days, at 0.030mg/
It was hot. Comparative Example 2 In the condensate treatment following Comparative Example 1, the amount of hydrazine in the treated water immediately after 5 hours of inflow of 0.65 mg/hydrazine on the 27th day was 0.005 mg/or less, but the amount of hydrazine 10 hours later is 0.010mg/
It continued to increase and reached 0.14 on the 28th day.
mg/, and then gradually decreased.

【図面の簡単な説明】[Brief explanation of drawings]

第1図は本発明を実施するための装置の一例を
示す概略図である。第2−a図、第2−b図、第
3−a図および第3−b図は混床塔内のH形カチ
オン樹脂の吸着帯の状態についての模式図であ
る。 2……イオン交換樹脂、3……混床塔、4……
集水装置、7……再生塔。
FIG. 1 is a schematic diagram showing an example of an apparatus for implementing the present invention. Figures 2-a, 2-b, 3-a and 3-b are schematic views of the state of the adsorption zone of the H-type cation resin in the mixed bed column. 2...Ion exchange resin, 3...Mixed bed column, 4...
Water collection device, 7... regeneration tower.

Claims (1)

【特許請求の範囲】 1 水素形強酸性カチオン交換樹脂と遊離塩基形
強塩基性アニオン交換樹脂とを混合して充填した
混床塔にアンモニア含有復水を通水して復水を処
理し、混床塔内の水素形強酸性カチオン交換樹脂
がアンモニウムイオンを捕捉して飽和した後も復
水の通水を継続する方法において、混床塔の処理
水中にヒドラジンが漏出し始めるまでは採水し、
その後採水を停止して、混床の撹拌を行つたの
ち、通水を再開することを特徴とする復水処理方
法。 2 混床の撹拌は、混床塔内で行う特許請求の範
囲第1項記載の復水処理方法。 3 混床の撹拌は、混床を別塔に移送して別塔内
で行い、撹拌後に混床を混床塔に戻すことを特徴
とする特許請求の範囲第1項記載の復水処理方
法。
[Claims] 1. Treating the condensate by passing ammonia-containing condensate through a mixed bed tower filled with a mixture of a hydrogen-type strongly acidic cation exchange resin and a free-base type strongly basic anion exchange resin, In a method in which condensate water continues to flow even after the hydrogen-type strongly acidic cation exchange resin in the mixed-bed tower captures ammonium ions and becomes saturated, water sampling is continued until hydrazine begins to leak into the treated water of the mixed-bed tower. death,
A condensate treatment method characterized in that water sampling is then stopped, the mixed bed is stirred, and then water flow is restarted. 2. The condensate treatment method according to claim 1, wherein stirring of the mixed bed is performed in a mixed bed tower. 3. The condensate treatment method according to claim 1, wherein the mixed bed is stirred by transferring the mixed bed to a separate column, performing the mixing in the separate column, and returning the mixed bed to the mixed bed column after stirring. .
JP18039182A 1982-10-14 1982-10-14 Condensate treatment method Granted JPS5969188A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP18039182A JPS5969188A (en) 1982-10-14 1982-10-14 Condensate treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP18039182A JPS5969188A (en) 1982-10-14 1982-10-14 Condensate treatment method

Publications (2)

Publication Number Publication Date
JPS5969188A JPS5969188A (en) 1984-04-19
JPH039797B2 true JPH039797B2 (en) 1991-02-12

Family

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Family Applications (1)

Application Number Title Priority Date Filing Date
JP18039182A Granted JPS5969188A (en) 1982-10-14 1982-10-14 Condensate treatment method

Country Status (1)

Country Link
JP (1) JPS5969188A (en)

Also Published As

Publication number Publication date
JPS5969188A (en) 1984-04-19

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