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JPS6059037B2 - Condensate treatment method - Google Patents
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JPS6059037B2 - Condensate treatment method - Google Patents

Condensate treatment method

Info

Publication number
JPS6059037B2
JPS6059037B2 JP53101661A JP10166178A JPS6059037B2 JP S6059037 B2 JPS6059037 B2 JP S6059037B2 JP 53101661 A JP53101661 A JP 53101661A JP 10166178 A JP10166178 A JP 10166178A JP S6059037 B2 JPS6059037 B2 JP S6059037B2
Authority
JP
Japan
Prior art keywords
condensate
column
tower
exchange resin
desalination
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
JP53101661A
Other languages
Japanese (ja)
Other versions
JPS5528732A (en
Inventor
巌 勢渡
茂夫 宮
伸一 臼井
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.)
Ebara Corp
Original Assignee
Ebara Infilco Co Ltd
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 Ebara Infilco Co Ltd filed Critical Ebara Infilco Co Ltd
Priority to JP53101661A priority Critical patent/JPS6059037B2/en
Publication of JPS5528732A publication Critical patent/JPS5528732A/en
Publication of JPS6059037B2 publication Critical patent/JPS6059037B2/en
Expired legal-status Critical Current

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  • Treatment Of Water By Ion Exchange (AREA)
  • Filtration Of Liquid (AREA)

Description

【発明の詳細な説明】 本発明は、ボイラ、タービンのスケール生成および腐食
を防止するために、復水中に存在する不純物質を除去す
る復水処理方法とその装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a condensate treatment method and apparatus for removing impurities present in condensate in order to prevent scale formation and corrosion in boilers and turbines.

一般に、復水脱塩装置には強酸性陽イオン交換樹脂のH
形と強塩基性陰イオン交換樹脂のOH形とを混合して用
い、陽イオン交換樹脂が復水中のアンモニアで飽和した
時点で再生を行なうHサイクル処理方法と:いま一つは
陽イオン交換樹脂が復水のアンモニアで破過したあとも
引き続いてアンモニア形に置換した樹脂を利用して処理
を継続するNH3サイクルの処理方法がある。
In general, condensate desalination equipment uses strongly acidic cation exchange resin H
The other method is the H cycle treatment method, in which a mixture of the OH form and the OH form of a strongly basic anion exchange resin is used, and the cation exchange resin is regenerated when it is saturated with ammonia in the condensate. There is an NH3 cycle treatment method in which the treatment continues using the resin substituted into the ammonia form even after the ammonia in the condensate has broken through.

最近では、復水脱塩装置の再生薬剤の節約と、運転・管
理の面から再生頻度の少ないNH3サイクルの復水処理
を採用するところが多い。しカルながら、NH3サイク
ルの運転においては、Hサイクルとは異なつた種々の制
限を受けるために、装置が複雑となつたり再生に長時間
を要するなどの欠点もあつて、必ずしも完成された技術
とは言えないのが現状である。従来行なわれているNH
3サイクルでは脱塩塔流入水のアンモニアが脱塩塔内て
吸着除去されることなくそのまま流出水に含まれてくる
ので、再生後脱塩塔に充填されている樹脂に不純物が残
つていると、これら不純物と復水中のアンモニアが反応
して、樹脂から不純物が溶離し、それが処理水に混つて
、処理水質を劣化させることになる。
Recently, many companies have adopted condensate treatment using the NH3 cycle, which requires less frequency of regeneration, in order to save on regeneration chemicals for condensate desalination equipment and from the standpoint of operation and management. However, the operation of the NH3 cycle is subject to various limitations different from those of the H cycle, so it has disadvantages such as the equipment being complicated and regeneration taking a long time, so it is not necessarily a perfect technology. The current situation is that it is impossible to say. Conventionally done NH
In the 3rd cycle, ammonia in the demineralization tower inflow is not adsorbed and removed in the demineralization tower and is contained in the outflow water as it is, so if there are impurities remaining in the resin packed in the demineralization tower after regeneration, When these impurities react with ammonia in the condensate, the impurities are eluted from the resin and mixed with the treated water, deteriorating the quality of the treated water.

例えば苛性ソーダで陰イオン交換樹脂を再生するときに
、若干の陽イオン交換樹脂が苛性ソーダと接触してNa
形となり、これが通水工程で復水のアンモニアと反応し
て処理水にNaが漏出してくるのもそ一例てある。この
Na漏出を低減させる方法として、消石灰溶液を通液す
る方法とかアンモニア水を利用する方法等か実用化され
ているが、いずれも特殊な薬品を使用し、さらに再生に
は長時間を要するなどの欠点があつた。本発明は、これ
ら従来の復水脱塩方法の欠点を排除し、Hサイクルはも
とよりNH3サイクルの運転においても極めて高純度の
処理水を安定して得る有効な処理方法を提供することを
目的としている。
For example, when regenerating an anion exchange resin with caustic soda, some of the cation exchange resin comes into contact with the caustic soda and becomes Na.
One example is when this reacts with ammonia in the condensate during the water flow process, causing Na to leak into the treated water. Methods to reduce this sodium leakage have been put to practical use, such as passing a slaked lime solution through or using ammonia water, but both require special chemicals and require a long time for regeneration. There were some shortcomings. The present invention aims to eliminate the drawbacks of these conventional condensate desalination methods and provide an effective treatment method for stably obtaining treated water of extremely high purity not only in H cycle but also in NH3 cycle operation. There is.

さらにまた本発明の他の目的は、復水脱塩装置の再生剤
量を大巾に低減させると共に維持管理を容易にすること
が可能な有効な処理方法とすることにある。本発明は、
プレコートt過機1,陽イオン交換樹脂3と混床式脱塩
塔5からなる復水処理装置を用いて高圧ポイラ復水を処
理し、復水中の溶解固形物並びに懸濁物質を除去する方
法において、ボ.イラ起動時のように多量の懸濁物質を
含む復水を処理する場合には、復水を粉末セルロースと
か、粉末合成繊維、粉末合成樹脂もしくは粉末活性炭の
ような非イオン交換性粉末;ろ過助剤のうちの1種類あ
るいは、これら沖過助剤を数種混合した複二層にプレコ
ートしたプレコート層2を有する第1塔のプレコート枦
過機1へ通水して復水中の懸濁物質の大部分を除去した
後、引き続いて粒状のH形強酸性陽イオン交換樹脂層4
を有する第2塔での陽イオン交換樹脂塔3へ通して残り
の懸濁物質4と溶解性カチオンを吸着分離し、次いで粒
状のH形強酸性陽イオン交換樹脂と0H形強塩基性陰イ
オン交換樹脂を混合した混床式樹脂層6のある第3塔の
混床式脱塩塔5へ復水を通して最終仕上げを行なうこと
を特徴としたものである。
Still another object of the present invention is to provide an effective treatment method that can greatly reduce the amount of regenerant in a condensate desalination device and facilitate maintenance. The present invention
A method for treating high-pressure boiler condensate using a condensate treatment device consisting of a precoat t-filter 1, a cation exchange resin 3, and a mixed bed demineralization tower 5 to remove dissolved solids and suspended solids in the condensate In Bo. When treating condensate containing a large amount of suspended solids, such as at the time of starting a furnace, the condensate can be treated with non-ion exchange powders such as powdered cellulose, powdered synthetic fiber, powdered synthetic resin or powdered activated carbon; The water is passed through the pre-coating filter 1 in the first tower, which has a double-layer pre-coating layer 2 containing one type of Oki filter aid or a mixture of several types of these Oki filter aids, to remove suspended solids in the condensate. After removing most of the resin, a granular H-type strongly acidic cation exchange resin layer 4 is added.
The remaining suspended solids 4 and soluble cations are adsorbed and separated through the cation exchange resin column 3 in the second column having This system is characterized in that the condensate is passed through the mixed bed demineralization tower 5 of the third tower, which has a mixed bed resin layer 6 mixed with exchange resin, for final finishing.

通常ボイラ起動時に復水に含まれる懸濁物質の主成分は
鉄の酸化物であつて、それらの50%以上は前記非イオ
ン交換性ろ過助材のうちの1種類をプレコートしたプレ
コート枦過機1で除去されるのであが、さらに除去率を
高めるためには、数種のろ過助材を組も合せたプレコー
ト層2によつて懸濁物質の除去率は向上する。
Normally, the main component of suspended solids contained in condensate when starting a boiler is iron oxide, and more than 50% of them are precoated with one type of non-ion exchange filter aid. 1, but in order to further increase the removal rate, the removal rate of suspended solids can be improved by using a precoat layer 2 that also includes several types of filter aids.

前記プレコート沖過機1の型式は特に限定するものでは
なく、一般フに使用されている管型エレメントにプレコ
ート層を形成する方式、あるいは、葉状の支持体にプレ
コート層を形成するいずれの型式のものでも用いること
ができる。また前記第1塔のプレコートp過機1からの
流門出水には若干の懸濁物質が含まれているので、これ
らを、第2塔の陽イオン交換樹脂塔3で吸着p過作用に
よつて分離除去する。
The type of the precoat offshore filter 1 is not particularly limited, and it may be of any type, such as a method in which a precoat layer is formed on a tubular element commonly used, or a method in which a precoat layer is formed on a leaf-shaped support. It can also be used. In addition, since the stream water discharged from the precoat p-filter 1 in the first column contains some suspended solids, these are removed by adsorption and p-filtration in the cation exchange resin column 3 of the second column. Separate and remove.

この際、復水中にナトリウム、マグネシウム、カルシウ
ム等の陽イオンが含まれている場合には、そそれらの不
純物・も第2塔のH形の強酸性陽イオン交換樹脂に吸着
さるれ。第2塔陽イオン交換樹脂のイオン形はH形強酸
性陽イオン交換樹脂、もしくはアンモニア形に置換した
樹脂のNF[4形とするが、ボイラ起動時のように懸濁
物質の多い場合には金属酸化物の吸着能の大きいH形が
より好ましい。第2塔の前段にプレコートした枦過機1
があるので、懸濁物質によるイオン交換樹脂の汚染が著
しく軽減されるわけである。さらに第2塔流出水には極
く微量の濁質と溶解性アニオンしか含まれていなく、こ
れらは第3塔のH,CR形混床式脱塩塔を通過する間に
ほぼ完全に除去され、第3塔からは極めて高純度の処理
水を得ることができるようにしてある。そしてポイラ起
動時、時間の経過につれて復水処理装置へ流入してくる
復水の純度は徐々に高まり、懸濁性物質はもとより溶解
性物質の濃度は減少してくるが、それに伴つて、第2塔
流出水純度が高まる。
At this time, if the condensate contains cations such as sodium, magnesium, and calcium, these impurities are also adsorbed by the H-type strongly acidic cation exchange resin in the second column. The ionic form of the second column cation exchange resin is H-type strongly acidic cation-exchange resin, or NF [4-type] of resin substituted with ammonia form, but when there are many suspended solids such as when starting a boiler, H-type is more preferable because it has a high ability to adsorb metal oxides. Filtering machine 1 pre-coated in the front stage of the second tower
As a result, contamination of the ion exchange resin by suspended solids is significantly reduced. Furthermore, the water effluent from the second tower contains only trace amounts of suspended solids and soluble anions, which are almost completely removed while passing through the H and CR mixed bed desalination tower of the third tower. , from the third column, it is possible to obtain treated water of extremely high purity. When the boiler is started, the purity of the condensate flowing into the condensate treatment equipment gradually increases over time, and the concentration of soluble substances as well as suspended substances decreases. The purity of the effluent water from the two towers increases.

このような平常時の運転に入ると、第2塔流出水の水質
を連続的に監視して、第2塔流出水水質がボイラ給水基
準値に到達した時点から第3塔への通水を停止し、復水
を第1塔と第2塔で処理する方法に切り替える。このよ
うな平常時の運転においては、通水初期にH形であつた
第2塔内樹脂は復水中のアンモニアを吸着して次第にN
H4形へ置換されてくが、引き続いてNH4形樹脂によ
る復水処理を継続してアンモニアサイクルの運転を行な
うことができる。復水処理装置流入復水の水質測定によ
つて、流入復水に陰イオンの増加を検出した場合は、直
ちに第2塔流出水を第3塔の混床式脱塩塔5へ通して最
終仕上げを行なう。第3塔内の樹脂は常時、H形と0H
形のイオン形で待機しているので、本発明の方法によれ
ば、大きな復水器漏洩事故による溶解固形物の急激な増
加に対しても十分に余裕をもつて対処することができる
わけである。本発明のいま一つの特徴は、連続的に復水
を処理することができることである。従来の混床式脱塩
塔のみの一塔による復水処理方法においては、樹脂の再
生時には、脱塩塔5への通水を一旦停止しなければなら
なかつたのであるが、本発明の方法によると弁の切り替
えによつて連続的に処理可能となるため、予備の脱塩塔
等を必要としない利点がある。即ち、第1塔内の?材を
プレコート中には、復水を第2塔単独もしくは第2塔と
第3塔で処理し、第2塔の樹脂の再生中には第1塔と第
3塔で処理を行ない、第3塔内の樹脂の再生中には第1
塔と第2塔で復水処理を行なうことができるものてある
。本発明の図示例での一実施態様では、プレコート層2
のあるプレコートろ過機1と、陽イオン交換樹脂層4の
ある陽イオン交換樹脂塔3,及び、混床式樹脂層6のあ
る混床式脱塩塔5,とを弁のある配管経路て直列に連結
した復水処理装置において、この配管経路にそれぞれ流
入復水水質監視計Mj,陽イオン交換樹脂塔流出水質監
視計Mc,混床式脱塩塔流出水水質監視計Me,及ひ弁
7,8,9,10,11,12,13,14,15,1
6,17が配備されている。
When such normal operation begins, the water quality of the second tower effluent is continuously monitored, and the water flow to the third tower is stopped from the moment the second tower effluent water quality reaches the boiler feed water standard value. The system is stopped and the method is changed to one in which condensate is treated in the first and second towers. In such normal operation, the resin in the second column, which was in H type at the beginning of water flow, adsorbs ammonia in the condensate and gradually becomes N.
Although it is replaced with H4 type resin, the condensate treatment with NH4 type resin can be continued to operate the ammonia cycle. If an increase in anions is detected in the inflowing condensate by measuring the quality of the condensate flowing into the condensate treatment equipment, the outflow water from the second tower is immediately passed to the mixed bed desalination tower 5 in the third tower for final treatment. Perform finishing touches. The resin in the third tower is always H type and 0H type.
Since the ionized solids are on standby in the ionic form, the method of the present invention can deal with a sudden increase in dissolved solids due to a major condenser leakage accident with sufficient margin. be. Another feature of the present invention is that condensate can be treated continuously. In the conventional condensate treatment method using only one mixed-bed demineralization tower, it was necessary to temporarily stop the water flow to the demineralization tower 5 during resin regeneration, but the method of the present invention According to the paper, continuous treatment is possible by switching the valves, so there is an advantage that there is no need for a standby desalination tower or the like. In other words, inside the first tower? During precoating of materials, condensate is treated in the second column alone or in the second column and the third column, and while the resin in the second column is being regenerated, the condensate is treated in the first column and the third column. During the regeneration of resin in the tower, the first
There are some that can perform condensate treatment in the tower and the second tower. In one illustrated embodiment of the invention, the precoat layer 2
A precoat filter 1 with a cation exchange resin layer 4, a cation exchange resin tower 3 with a cation exchange resin layer 4, and a mixed bed desalination tower 5 with a mixed bed resin layer 6 are connected in series through a piping route with a valve. In the condensate treatment equipment connected to the piping route, an inflow condensate water quality monitor Mj, a cation exchange resin tower effluent water quality monitor Mc, a mixed bed desalination tower effluent water quality monitor Me, and a valve 7 are installed in the piping route. ,8,9,10,11,12,13,14,15,1
6,17 are deployed.

一般に、復水処理装置においては、被処理水を複数系列
の処理装置に分割して流水するのが普通である。
In general, in a condensate treatment device, it is common to divide the water to be treated into a plurality of treatment devices and flow the water therethrough.

本発明の方法においても同様に複数個の処理系列を有し
ているのであるが、ここでは1系列のみを図示し、他の
系列は省略してある。しかしてホイラ起動時においては
弁7を通り流入復水水質監視計Miで水質をチェックさ
れた復水は、弁8を経てプレコート泊過機1に導入され
、プレコート層2を通過する間に吸着枦過作用により濁
質が除去されたのち、弁9,13を介して陽イオン交換
樹脂塔3に導入され、水質監視計Mcで水質測定され、
引き続いて、弁14を経て混床式脱塩塔5に導入され、
最終仕上げを受けてから水質監視計Meで連続的に水質
チェックを受け、弁16より系外へ導出される。
Although the method of the present invention similarly has a plurality of processing sequences, only one sequence is illustrated here, and the other sequences are omitted. When the wheeler is started, the condensate passes through valve 7 and whose water quality is checked by the inflow condensate water quality monitor Mi.The condensate passes through valve 8 and is introduced into the precoat overnight machine 1, where it is adsorbed while passing through the precoat layer 2. After the suspended solids are removed by the filtration action, the water is introduced into the cation exchange resin tower 3 via valves 9 and 13, and the water quality is measured by a water quality monitor Mc.
Subsequently, it is introduced into the mixed bed desalination tower 5 via the valve 14,
After receiving the final finishing, the water quality is continuously checked by a water quality monitor Me, and the water is led out of the system through a valve 16.

プレコート?過機1の差圧が設定値を越えると、弁8,
9を閉じ、弁10,11,12を開いて復水を第1塔を
バイパスさせて第2塔へ通水すると同時に、加圧水を弁
11から第1塔へ導入してプレコート層2を剥離させて
弁12から塔外へ排出する。次いで弁11,12を閉じ
、該図面には記入していないが、通常の方法につて非イ
オン交換性枦過助材を再度プレコートしてから、弁8,
9を開き弁10を閉じて復水を第1塔から順次通水処理
する方法を繰り返す。このようにしてプレコート層2を
更新する作業中においても、復水処理装置の運転を停止
することなく、連続して処理が可能なものである。ボイ
ラ起動時の復水には、懸濁物質が数十〜数千μy/l含
まれているが、第1塔流出水には、これが数μ′/′〜
数十μy/l程度となり、第2塔流出水には高々数μy
/e検出される程度に減少する。ポイラ起動後、徐々に
流入復水純度が上昇し、それに伴つた第2塔流出水純度
も高まつてくるが、水質監視計Mcによつて第2塔流出
水水質がボイラ給水基準値を満足するのを確認したら、
弁14,16を閉じ、弁17を開いて第3塔をバイパス
させて処理を行なう平常時にの運転に移行する。
Pre-coat? When the differential pressure of the filter 1 exceeds the set value, the valve 8,
9 is closed and valves 10, 11, and 12 are opened to allow condensate to bypass the first column and flow to the second column, and at the same time, pressurized water is introduced from valve 11 into the first column to peel off the precoat layer 2. and discharged from the tower through valve 12. The valves 11 and 12 are then closed, and although not shown in the drawing, a non-ion-exchangeable filter aid is again precoated using a conventional method, and then the valves 8 and
The method of sequentially passing condensate from the first tower by opening valve 9 and closing valve 10 is repeated. In this way, even during the work of renewing the precoat layer 2, continuous treatment is possible without stopping the operation of the condensate treatment apparatus. The condensate at the time of boiler startup contains suspended solids in the range of tens to thousands of μy/l, but the amount of suspended solids in the effluent from the first column is several μ'/' to
The amount is on the order of several tens of μy/l, and the amount of water flowing out from the second tower is several μy/l at most.
/e decrease to the extent that it is detected. After the boiler is started, the purity of the inflow condensate gradually increases, and the purity of the second tower outflow water increases accordingly, but the water quality of the second tower outflow water satisfies the boiler feed water standard value according to the water quality monitor Mc. After confirming that
The valves 14 and 16 are closed and the valve 17 is opened to bypass the third column and proceed to normal operation.

平常時においては、プレコート枦過機1のプ”レコード
層2の更新は先と同じように行なうが、復水は第2塔の
陽イオン交換樹脂塔3のみで処理される。この第2塔は
Hサイクルはもとより、NH3サイクルても使用される
が、不純物の吸着によつて再生を行なわなければならな
い場合には、.弁13,17を閉じ、弁15,16を開
いて復水を一時的に第2塔をバイパスさせて第3塔の混
床式脱塩塔5へ導入して処理を行なう。第2塔内の樹脂
は、同塔内あるいは、別個に設けた塔外再生装置でもつ
て、逆洗もしくは、鉱酸による再生をノ受けたのち、再
度通水工程へ復帰するが、再生後しばらくは、第2塔か
ら第3塔へ連結して復水処理を行ない、第2塔流出水の
純度が基準値を満足した時点から第3塔を切り離す。な
お前記流入復水水質監視計Miによつて、流入復水中に
溶解固形物、特に陰イオンの増加を検出したら、直ちに
弁17を閉じ、弁14,16を開いて第2塔流出水を第
3塔の混床式脱塩塔5へ通して処理を継続するようにす
るのが合理的である。
In normal times, the pre-record layer 2 of the pre-coat filter 1 is renewed in the same way as before, but condensate is treated only in the cation exchange resin column 3 of the second column. is used not only in the H cycle but also in the NH3 cycle, but if regeneration is required by adsorption of impurities, valves 13 and 17 are closed and valves 15 and 16 are opened to temporarily release the condensate. The resin in the second column is treated by bypassing the second column and introducing it into the mixed bed desalination column 5 of the third column. Then, after being backwashed or regenerated with mineral acid, the water flow process is resumed. However, for a while after regeneration, the second tower is connected to the third tower for condensate treatment, and the second tower The third tower is disconnected from the point at which the purity of the outflow water satisfies the standard value.If the inflow condensate water quality monitor Mi detects an increase in dissolved solids, especially anions, in the inflow condensate, the valve is immediately shut off. It is reasonable to close valve 17 and open valves 14 and 16 to pass the second column effluent to the mixed bed demineralization column 5 of the third column to continue the treatment.

該混床式脱塩塔5内樹脂の再生に関しては図に示してい
ないが、塔内方式あるいは塔外再出方式いずれの方法に
よつても実施でき、その方法は通常のHサイクル復水脱
塩法で使用されている方法に準じて行なつてもよく、そ
の時期は、第3塔が待機の状態にあるときを選定すると
、復水処理装置の運転を停止することなく実施可能なも
のである。
Regeneration of the resin in the mixed bed demineralization tower 5 is not shown in the figure, but it can be carried out by either an internal method or an external re-extraction method, and this method is similar to the normal H cycle condensate demineralization method. It may be carried out according to the method used in the salt method, and if the timing is selected when the third tower is on standby, it can be carried out without stopping the operation of the condensate treatment equipment. It is.

本発明の方法によると、第2塔内の樹脂を完全に再生し
ておくだけで、アンモニアサイクルの運転においても高
純度の処理水を得ることができ、消石灰とかアンモニア
水のような特殊な薬品は一切必要としないで運転できる
According to the method of the present invention, high purity treated water can be obtained even when operating an ammonia cycle by simply regenerating the resin in the second column, and special chemicals such as slaked lime and aqueous ammonia can be used. You can drive without needing any.

以上述べたように、本発明の方法によれば、ボイラ起動
時と復水器漏洩時のような復水純度の低=い場合には、
プレコートろ過機1,陽イオン交換樹脂層4と温床式樹
脂層6の直列処理によつて、また流入復水純度の高い平
常時には、混床塔を除いた2段処理によつて復水処理を
行なうことができ、復水処理装置の再生薬剤の使用を大
巾に減少でき運転維持管理も容易となると共に、従来の
復水脱塩方法の欠点を排除し、HサイクルはもとよりN
H3サイクルの運転においても極めて高純度の処理水を
安定して大量に得るものである。
As described above, according to the method of the present invention, when the condensate purity is low, such as during boiler startup and condenser leakage,
Condensate treatment is carried out by serial treatment of pre-coat filter 1, cation exchange resin layer 4 and hotbed type resin layer 6, and in normal times when the purity of inflow condensate is high, by two-stage treatment excluding the mixed bed column. This method greatly reduces the use of regenerating chemicals in condensate treatment equipment, simplifies operation and maintenance, and eliminates the drawbacks of conventional condensate desalination methods, allowing it to be used not only in the H cycle but also in the N cycle.
Even in the operation of the H3 cycle, extremely high purity treated water can be stably obtained in large quantities.

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

図面は本発明の一実施態様を示す系統説明図である。 1:プレコート沖過機、2:プレコート層、3:陽イオ
ン交換樹脂塔、4:陽イオン交換樹脂層、5:混床式脱
塩塔、6:混床式樹脂層、7,8,9,10,11,1
2,13,14,15,16,17:弁、M1:流入復
水水質監視計、MC:陽イオン交換樹脂塔流出水水質監
視計、Me:混床式脱塩塔流出水水質監視計。
The drawing is a system explanatory diagram showing one embodiment of the present invention. 1: Precoat filter, 2: Precoat layer, 3: Cation exchange resin tower, 4: Cation exchange resin layer, 5: Mixed bed desalination tower, 6: Mixed bed resin layer, 7, 8, 9 ,10,11,1
2, 13, 14, 15, 16, 17: valve, M1: inflow condensate water quality monitor, MC: cation exchange resin tower effluent water quality monitor, Me: mixed bed desalination tower effluent water quality monitor.

Claims (1)

【特許請求の範囲】 1 非イオン交換性粉末濾過助剤をプレコートした濾過
機と粒状イオン交換樹脂を充填したイオン交換樹脂塔に
ボイラ復水を通して復水中の不純物を除去する復水処理
工程において、復水中の不純物量が少ない平常時には、
復水を非イオン交換性濾過助材をプレコートした第1塔
のプレコート濾過機を通してプレコート濾過工程を経て
、引き続いて、粒状の陽イオン交換樹脂を充填した第2
塔へ通水して吸着濾過工程で処理し、復水中の不銃物量
が比較的多いボイラ起動時または復水器漏洩時には、前
記第1塔と第2塔で処理された復水を、粒状の陽イオン
交換樹脂と陰イオン交換樹脂を混合して充填した第3塔
の混床式脱塩塔へ通水して脱塩工程で処理することを特
徴とする復水処理方法。 2 前記プレコート濾過工程が、その第1塔のプレコー
トを更新している間は、復水を吸着濾過工程単独で処理
するか、もしくは吸着濾過工程から脱塩工程を経て処理
する特許請求の範囲第1項記載の復水処理方法。 3 前記吸着濾過工程が、その第2塔内樹脂を逆流ある
いは通薬再生中には、復水をプレコート濾過工程から直
接脱塩工程を経て、処理して実質的な復水処理工程から
省略されるものである特許請求の範囲第1項記載の復水
処理方法。 。4 前記脱塩工程が、その第3塔内樹脂の再生中には
、復水をプレコート濾過工程と吸着濾過工程とで処理し
て実質的な復水処理工程から省略されるものである特許
請求の範囲第1項記載の復水処理方法。
[Claims] 1. In a condensate treatment process in which impurities in condensate are removed by passing boiler condensate through a filter pre-coated with a non-ion exchange powder filter aid and an ion exchange resin tower filled with granular ion exchange resin, During normal times when the amount of impurities in condensate is low,
The condensate is passed through a pre-coat filter in the first column pre-coated with a non-ion exchange filter aid, and then undergoes a pre-coat filtration process, followed by a second column pre-coated with a granular cation exchange resin.
Water is passed through the tower and treated in an adsorption filtration process, and when the boiler starts up or the condenser leaks, when the amount of non-guns in the condensate is relatively large, the condensate treated in the first and second towers is turned into granules. A condensate treatment method characterized by passing water through a third column, a mixed-bed desalination tower, filled with a mixture of a cation exchange resin and an anion exchange resin, and treating the condensate in a desalination step. 2. While the precoat filtration process is renewing the precoat in the first column, the condensate is treated in the adsorption filtration process alone or from the adsorption filtration process through a desalination process. The condensate treatment method described in item 1. 3. During the adsorption filtration step, the resin in the second column is regenerated by backflow or drug flow, and the condensate is directly processed from the precoat filtration step through the desalination step, so that it is omitted from the actual condensate treatment step. The condensate treatment method according to claim 1, wherein: . 4. A patent claim in which the desalination step is omitted from the actual condensate treatment step by treating the condensate with a precoat filtration step and an adsorption filtration step during the regeneration of the resin in the third column. The condensate treatment method according to item 1.
JP53101661A 1978-08-21 1978-08-21 Condensate treatment method Expired JPS6059037B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP53101661A JPS6059037B2 (en) 1978-08-21 1978-08-21 Condensate treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP53101661A JPS6059037B2 (en) 1978-08-21 1978-08-21 Condensate treatment method

Publications (2)

Publication Number Publication Date
JPS5528732A JPS5528732A (en) 1980-02-29
JPS6059037B2 true JPS6059037B2 (en) 1985-12-23

Family

ID=14306548

Family Applications (1)

Application Number Title Priority Date Filing Date
JP53101661A Expired JPS6059037B2 (en) 1978-08-21 1978-08-21 Condensate treatment method

Country Status (1)

Country Link
JP (1) JPS6059037B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5750697A (en) * 1980-09-12 1982-03-25 Hitachi Ltd Method of treating radioactive liquid

Also Published As

Publication number Publication date
JPS5528732A (en) 1980-02-29

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