JPS6036829B2 - Condensate treatment method - Google Patents
Condensate treatment methodInfo
- Publication number
- JPS6036829B2 JPS6036829B2 JP53101662A JP10166278A JPS6036829B2 JP S6036829 B2 JPS6036829 B2 JP S6036829B2 JP 53101662 A JP53101662 A JP 53101662A JP 10166278 A JP10166278 A JP 10166278A JP S6036829 B2 JPS6036829 B2 JP S6036829B2
- Authority
- JP
- Japan
- Prior art keywords
- condensate
- exchange resin
- column
- tower
- resin
- 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
Links
- 238000000034 method Methods 0.000 title claims description 32
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 50
- 239000011347 resin Substances 0.000 claims description 39
- 229920005989 resin Polymers 0.000 claims description 39
- NWUYHJFMYQTDRP-UHFFFAOYSA-N 1,2-bis(ethenyl)benzene;1-ethenyl-2-ethylbenzene;styrene Chemical compound C=CC1=CC=CC=C1.CCC1=CC=CC=C1C=C.C=CC1=CC=CC=C1C=C NWUYHJFMYQTDRP-UHFFFAOYSA-N 0.000 claims description 21
- 238000010612 desalination reaction Methods 0.000 claims description 20
- 238000011069 regeneration method Methods 0.000 claims description 17
- 238000001914 filtration Methods 0.000 claims description 16
- 230000008929 regeneration Effects 0.000 claims description 14
- 239000003729 cation exchange resin Substances 0.000 claims description 11
- 239000003456 ion exchange resin Substances 0.000 claims description 11
- 229920003303 ion-exchange polymer Polymers 0.000 claims description 11
- 239000012535 impurity Substances 0.000 claims description 10
- 238000001179 sorption measurement Methods 0.000 claims description 7
- 239000003957 anion exchange resin Substances 0.000 claims description 6
- 238000005115 demineralization Methods 0.000 claims description 6
- 230000002328 demineralizing effect Effects 0.000 claims description 6
- 239000000203 mixture Substances 0.000 claims description 4
- 238000011033 desalting Methods 0.000 claims 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 24
- 239000000126 substance Substances 0.000 description 8
- 229910021529 ammonia Inorganic materials 0.000 description 7
- 239000007787 solid Substances 0.000 description 7
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 125000002091 cationic group Chemical group 0.000 description 5
- 230000001172 regenerating effect Effects 0.000 description 5
- 150000003839 salts Chemical class 0.000 description 5
- 230000000968 intestinal effect Effects 0.000 description 4
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 4
- 238000012545 processing Methods 0.000 description 4
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical group [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 3
- 239000011248 coating agent Substances 0.000 description 3
- 238000000576 coating method Methods 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- 239000011734 sodium Substances 0.000 description 3
- 150000001768 cations Chemical class 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 235000013980 iron oxide Nutrition 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 235000011121 sodium hydroxide Nutrition 0.000 description 2
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 1
- 241001125046 Sardina pilchardus Species 0.000 description 1
- ATJFFYVFTNAWJD-UHFFFAOYSA-N Tin Chemical compound [Sn] ATJFFYVFTNAWJD-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 235000011114 ammonium hydroxide Nutrition 0.000 description 1
- 125000000129 anionic group Chemical group 0.000 description 1
- 238000011001 backwashing Methods 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 230000000593 degrading effect Effects 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 210000000936 intestine Anatomy 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- VBMVTYDPPZVILR-UHFFFAOYSA-N iron(2+);oxygen(2-) Chemical class [O-2].[Fe+2] VBMVTYDPPZVILR-UHFFFAOYSA-N 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 239000012492 regenerant Substances 0.000 description 1
- 235000019512 sardine Nutrition 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000005201 scrubbing Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 150000003385 sodium Chemical class 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
Landscapes
- Filtration Of Liquid (AREA)
- Treatment Of Water By Ion Exchange (AREA)
Description
【発明の詳細な説明】
本発明は、ボィラ、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腸イオン交換樹脂の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ァ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 intestine ion 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 is continued using the resin substituted into the ammonia form even after the ammonia in the condensate has broken through.
最近では、復水脱塩装置に再生薬剤の節約と、運転管理
の面から再生頻度の少ないN比サイクルの復水処理を採
用するところが多い。しかしながら、NH3サイクルの
運転においては、Hサイクルとは異なった種々の制限を
受けるために、装置が複雑となったり再生に長時間を要
するなどの欠点もあって、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N馬サイ
クルでは脱塩塔流入水のアンモニアが脱塩塔内で吸着除
去されることなくそのまま流出水に含まれてくるので、
再生脱塩塔に充填されている樹脂に不純物が残っている
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 condensate desalination apparatuses have adopted N-ratio cycle condensate treatment, which requires less regeneration frequency, from the viewpoint of saving regeneration chemicals and operational management. However, the operation of the NH3 cycle is subject to various limitations different from those of the H cycle, and there are drawbacks such as the equipment being complicated and regeneration taking a long time, so it cannot necessarily be said that it is a perfected technology. The current situation is that there is no such thing. In the conventional N-horse cycle, ammonia in the desalination tower inflow is not adsorbed and removed in the desalination tower and is directly included in the outflow water.
If impurities remain in the resin packed in the regenerative desalination tower, these impurities react with ammonia in the condensate, eluting the impurities from the resin and mixing with the treated water, degrading the quality of the treated water. It turns out.
例えば苛性ソーダで陰イオン交予期樹脂を再生するとき
に、若干の腸イオン交≠剣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の一例である
。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が実用
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った。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 intestinal ion exchange resin comes into contact with the caustic soda and becomes Na form, which reacts with ammonia in the condensate during the water flow process, adding Na to the treated water. One example is leakage. Methods to reduce this sodium leakage include passing slaked lime solution and using ammonia water, but both use special chemicals and require a long time for regeneration. There was a drawback. 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
量を大中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。Furthermore, another object of the present invention is to provide an effective treatment method that can significantly reduce the amount of regenerant in a condensate desalination device and facilitate maintenance.
本発明は、賜イオン交去勢樹脂塔1、プレコート炉過機
3と温床式脱塩塔5からなる復水処理装置を用いて高圧
ポィラ復水を処理し、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、ボィラ起動時のように多量
の不純物を含む復水を処理する場合には、復水を粒状の
腸イオン交モ剣樹脂を充填した第1塔に通水し、次いで
粉末の陽、陰イオン交換樹脂を混合してプレコートした
第2塔のプレコート炉過機3へ通水して処理したあと、
引き続いて粒状のH形樹脂とOH形樹脂を混合した混床
式樹脂層6のある第3塔の濠床式脱塩塔5へ直列に通水
して最終仕上げを行なうことを特徴としたものである。The present invention uses a condensate treatment device consisting of an ion-exchanged resin tower 1, a precoat furnace filtration machine 3, and a hot bed desalination tower 5 to treat high-pressure poller condensate, and remove dissolved solids and suspended solids in the condensate. In the method of removing substances, when treating condensate containing a large amount of impurities, such as when starting a boiler, the condensate is passed through a first column filled with granular intestinal ion exchanger resin, and then After processing by passing water through the pre-coat filter 3 of the second tower, which is pre-coated with a mixture of powdered cation and anion exchange resins,
It is characterized in that water is then passed in series to the moat bed type desalination tower 5 of the third tower, which has a mixed bed type resin layer 6 containing a mixture of granular H type resin and OH type resin, to perform the final finishing. It is.
通常ボィラ起動時に復水に含まれる懸濁物質の主成分は
鉄の酸化物となり、それらの約90%はH形の陽イオン
交モ勢樹脂層2で吸着炉過作用によって除去される。樹
脂のイオン形によって濁質の除去率は異なり、NH4形
の樹脂はH形よりも10〜20%除去率が減少する。こ
のことから、第2塔流入復水の濁質濃度をできるだけ低
く保つためには、第1塔内樹脂のイオン形はH形が好ま
しい。第1塔の陽イオン交換樹脂塔2流出水には若干の
懸濁物質が含まれているが、それらは第2塔の粉末イオ
ン交≠期間脂をプレコートしたプレコート炉過機3でほ
ぼ完全に除去される。高濃度の不純物を含む復水を直接
粉末イオン交換樹脂のプレコート層4へ通水すると、プ
レコート炉過機3の差圧上昇が激しく、頻繁にプレコー
ト層4を更新しなければならず、そのつど高価な粉末イ
オン交換樹脂を補給するのは経済的とは言えなかった。
本発明のように第1塔での陽イオン交換樹脂塔1で不溶
性物質を大部分除去すると、第2塔のプレコート炉過機
3での単位重量のプレコート材当りの処理水量は著しく
増加すると共に、不溶性物質で汚染された第1塔は、単
純な水による逆洗あるいは、水と空気によるスクラビン
グによって濁費補促能力を回復させることができること
からも、復水処理装置の運転管理は大中に容易となるも
のである。そしてボィラ起動後、時間の経過につれて復
水処理装置へ流入する復水の純度が徐々に高まり、それ
に伴って、第2搭流出水の純度も上昇する。Normally, when a boiler is started, the main component of suspended solids contained in condensate is iron oxide, and approximately 90% of these are removed by the overaction of the adsorption furnace in the H-type cation-converting resin layer 2. The removal rate of suspended solids differs depending on the ionic form of the resin, and the removal rate of NH4 type resin is 10 to 20% lower than that of H type resin. From this, in order to keep the turbidity concentration of the condensate flowing into the second column as low as possible, the ionic form of the resin in the first column is preferably H type. The water flowing out of the cation exchange resin tower 2 in the first tower contains some suspended solids, but these are almost completely removed by the pre-coating furnace filter 3 pre-coated with powder ion exchange resin in the second tower. removed. When condensate containing high concentration of impurities is directly passed through the precoat layer 4 of powdered ion exchange resin, the differential pressure in the precoat filter 3 increases rapidly, and the precoat layer 4 must be frequently renewed. It was not economical to replenish expensive powdered ion exchange resin.
When most of the insoluble substances are removed in the cation exchange resin column 1 in the first column as in the present invention, the amount of water treated per unit weight of precoat material in the precoat furnace filtration machine 3 in the second column increases significantly. The operational management of condensate treatment equipment is of utmost importance, as the first tower contaminated with insoluble substances can be restored to its turbidity collection capacity by simple backwashing with water or scrubbing with water and air. This makes it easy to use. After the boiler is started, the purity of the condensate flowing into the condensate treatment device gradually increases as time passes, and the purity of the second headwater effluent also increases accordingly.
このような平常時の運転に入ると、第2塔流出水の水質
測定によって、第2塔流出水がボィラ給水基準値を満足
した時点から第3塔の脱塩塔5への通水を停止して、復
水を第1塔と第2塔で処理する方法を彩用する。平常時
の運転においては、通水初期にH形であった第1塔内の
粒状樹脂はもとより、第2塔の粉末陽イオン交樹樹脂も
、通水量の増加に伴なつて次第にN比形に変わってくる
が、引き続き処理を継続してアンモニアサイクルの復水
処理を行うことができるものである。復水処理装置流入
復水の水質測定によって、流入復水に溶解固形物の増加
を検出した場合は、直ちに第2塔流出水を第3塔の濃床
式脱塩塔5へ通水する方法に切り替える。第3塔内の混
床は常時、H形とOH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
溶解塩分の増加に対しても、十分に余裕をもって対処す
ることができるものである。塩分濃度が比較的小さい復
水器漏洩時には、第2塔の粉末混合樹脂のプレコート層
4のみでも処理可能であるが、安全を考えると、復水の
塩分濃度が上昇する場合には第3塔を利用する方法が好
ましい。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。When such normal operation starts, the water flow to the desalination tower 5 of the third tower is stopped from the time when the second tower outflow water satisfies the boiler feed water standard value based on the water quality measurement of the second tower outflow water. Then, a method is used in which condensate is treated in the first and second towers. During normal operation, not only the granular resin in the first tower, which was in the H form at the beginning of water flow, but also the powdered cationic cross-resin in the second tower gradually changed to the N ratio form as the water flow increased. However, it is possible to continue processing and perform condensate treatment in the ammonia cycle. If an increase in dissolved solids is detected in the inflow condensate by measuring the quality of the condensate flowing into the condensate treatment equipment, the second tower effluent is immediately passed to the concentrated bed demineralization tower 5 of the third tower. Switch to Since the mixed bed in the third column is always in the ionic form of H type and OH type, the method of the present invention is sufficient to prevent an increase in dissolved salts due to a major condenser leakage accident. can be dealt with with ease. In the event of a leak in the condenser where the salt concentration is relatively low, it is possible to treat it with only the pre-coated layer 4 of powdered mixed resin in the second column, but for safety reasons, if the salt concentration of the condensate increases, the third column should be used. A method using . Another feature of the present invention is that condensate can be treated continuously.
即ち従来の混床式脱塩塔のみの一驚による復水処理装置
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ったのであるが、本発明の方法
によると、弁の切り替えによって簡単に連続処理が可能
となるので、予備の脱塩塔を必要としない利点がある。
例えば、第1塔内の陽イオン交灘樹脂2を逆洗したり通
薬再生している間は、復水を第1塔をバイパスさせてま
す第2塔へ通水し、引き続き、必要な場合は第3塔へ通
水して処理を行なうことができる。第2塔がプレコート
層を更新しているときは、復水を第1塔から第3塔へ通
水して処理し、また、第3塔の再生を平常時に行えば、
第3塔内樹脂の再生による復水処理の中断もなく連続的
に運転処理することが可能となる。本発明の図示例での
一実施態様では、陽イオン交千剣樹脂層2のある陽イオ
ン交干鰯樹脂塔1、プレコート炉過層4のあるプレコー
ト炉過機3、混床式樹脂層6のある温床式脱塩塔5、と
を弁のある配管経路で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Mi
、プレコート炉過機流出水水質監視計Mc、混床式脱塩
塔流出水水質監視計Me及び弁7,8,9,10,11
,12,13,14,15,16,17が配備されてい
る。In other words, in the conventional condensate treatment equipment using only a mixed-bed demineralization tower, it was necessary to temporarily stop the water flow to the demineralization tower 5 when regenerating the resin, but the method of the present invention According to , continuous treatment is easily possible by switching the valves, so there is no need for a standby demineralization tower.
For example, while the cationic exchange resin 2 in the first column is being backwashed or regenerated, the condensate is bypassed from the first column and then passed to the second column, where the necessary water is continued. In this case, water can be passed to the third tower for treatment. When the second tower is renewing the precoat layer, the condensate is passed from the first tower to the third tower for treatment, and if the third tower is regenerated during normal times,
It becomes possible to perform continuous operation treatment without interruption of condensate treatment due to regeneration of the resin in the third column. In one embodiment of the illustrated example of the present invention, a cationic mixed dried sardine resin tower 1 with a cationic mixed resin layer 2, a precoated furnace 3 with a precoated furnace layer 4, and a mixed bed type resin layer 6 are provided. In a condensate treatment device in which a certain hotbed type demineralization tower 5 is connected in series through a piping route with a valve, an inflow condensate water quality monitoring meter Mi is connected to each piping route.
, pre-coat furnace filtration machine effluent water quality monitor Mc, mixed bed desalination tower effluent water quality monitor Me and valves 7, 8, 9, 10, 11
, 12, 13, 14, 15, 16, and 17 are deployed.
一般に、復水脱塩装置においては、被処理水を複数系列
の処理装置に分割して通水するのが普通である。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
が、他の系列は省略して、ここでは1系列のみを図示し
てある。しかしてボィ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を経て陽イオン交モ期樹脂塔1に導入され、腸イ
オン交換樹脂層2を通過する間に吸着炉過作用によって
懸濁物質と陽イオンが除去されたのち、弁9,11を経
てプレコート炉過機3に導入される。Generally, in a condensate desalination apparatus, it is common to divide the water to be treated into a plurality of treatment apparatuses and pass the water through the treatment apparatuses. Although the method of the present invention similarly has a plurality of processing sequences, only one sequence is shown here, omitting the other sequences. When the boiler is started, the condensate that has passed through valve 7 and whose water quality has been checked by the inflow condensate water quality monitor Mi is introduced into the cation exchange resin tower 1 through valve 8, and enters the ion exchange resin layer 1. After passing through the filter 2, suspended solids and cations are removed by the adsorption furnace filtering action, and then introduced into the precoat filter 3 via valves 9 and 11.
粉末の陽、陰イオン交モ期樹脂炉過層となるプレコート
層4を通ったあと、水質監視計Mcで水質測定され、引
き続いて弁12,15から泥床式脱塩塔5に入り、水質
監視計Meで水質検定を受け、弁16より系外へ導出さ
れる。第1塔の腸イオン交モ剣樹脂塔1の差圧が設定値
を越えたり、塔内樹脂層2の汚染が進むと、弁8,9を
閉じ、弁10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。第1図には再生方法を図示していない
が、塔内再生もしくは搭外再生装置を利用して、第1塔
内の汚染された樹脂層2を逆洗、スクラビング、あるい
は、錫酸通薬などの再生を行なったあと、弁10を閉じ
、弁8,9を開いて、再び通水工程に戻る。このように
して、第1塔内樹脂の再生中においても、復水処理装置
の運転を停止することなく、連続して処理することが可
能なものである。この場合第1塔内の樹脂がH形の場合
には、流入復水中の鉄酸化物の約90%は第1塔で除去
され、N比形の樹脂では70〜80%の懸濁粒子が除去
される。次にボィラ起動後、次第に流入復水純度が上昇
し、それに伴って第2塔流出水純度も高まってくるが、
水質監視計Mcによって第2塔流出水水質がボィラ給水
基準値を満足するのを確認したら、弁15,16を閉じ
、弁13,17を開いて第3塔をバイパスさせて復水処
理を行なう平常時の運転に移行する。After passing through the pre-coat layer 4, which serves as a resin overlay during the positive and negative ion phase of the powder, the water quality is measured by a water quality monitor Mc, and then enters the mud bed desalination tower 5 through valves 12 and 15, where the water quality is measured. The water quality is tested by the monitor Me, and the water is led out of the system through the valve 16. When the differential pressure in the resin column 1 of the first column exceeds the set value or the resin layer 2 in the column becomes contaminated, valves 8 and 9 are closed and valve 10 is opened to transfer condensate to the first column. The water is passed to the second tower by bypassing the tower. Although the regeneration method is not shown in Fig. 1, the contaminated resin layer 2 in the first column can be backwashed, scrubbed, or treated with tin acid by using an in-column regeneration device or an external regeneration device. After performing the regeneration, valve 10 is closed, valves 8 and 9 are opened, and the process returns to the water flow process again. In this way, even during the regeneration of the resin in the first column, continuous treatment is possible without stopping the operation of the condensate treatment device. In this case, if the resin in the first column is H-type, about 90% of the iron oxides in the inflow condensate will be removed in the first column, and if the resin is N-type, 70-80% of the suspended particles will be removed. removed. Next, after the boiler is started, the purity of the inflow condensate gradually increases, and the purity of the second column outflow water increases accordingly.
When it is confirmed by the water quality monitor Mc that the quality of the second column effluent water satisfies the boiler water supply standard value, valves 15 and 16 are closed and valves 13 and 17 are opened to bypass the third column and perform condensate treatment. Shift to normal operation.
平常時の運転においては、第1塔、及び第2※共に、H
サイクルでも、あるいはNAサイクルのいずれの処理方
式を任意に採用することができる。平常時に第1塔を再
生する場合は、復水は第2塔のみで処理される。また、
第2塔のプレコート層4を更新する場合は、弁11,1
2,17を閉じ、弁14,15,16を開いて、復水を
一時的に第1塔から第3塔へ通し、第2塔のプレコート
操作が完了したら元へ復帰させて、第1塔から第2塔へ
の通水方法をとる。第2塔のプレコート操作に関しては
図面には示していないが、常法によって、粉末の陽、陰
イオン交換樹脂を水中で混合したスラリーをプレコート
支持体に楠促させてプレコート層を形成させる。なお前
記流入復水水質監視計Miによって、流入復水中に熔解
塩分の増加を検出したら、直ちに弁13,17を閉じ、
弁15.,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。第3塔の温床式樹脂層6の再生に関しては、特
に図に示してはいないが、塔内再生もしくは繁外再生方
式のいずれの方法によっても実施でき、その方法は通常
のHサイクル復水処理装置で行なわれている方法に準じ
てよく、特殊な薬品とか混合樹脂の厳密な分離は必要と
しない。During normal operation, both the 1st tower and the 2nd *
It is possible to arbitrarily adopt either a cycle or an NA cycle processing method. When regenerating the first column during normal times, condensate is treated only in the second column. Also,
When renewing the precoat layer 4 of the second column, the valves 11 and 1
2 and 17, and open valves 14, 15, and 16, the condensate is temporarily passed from the first column to the third column, and when the precoating operation in the second column is completed, the condensate is returned to the first column. A method is used to pass water from the main tower to the second tower. Although the precoating operation in the second column is not shown in the drawings, a precoat layer is formed by a conventional method in which a slurry prepared by mixing powdered cationic and anionic exchange resins in water is applied to the precoat support. If the inflow condensate water quality monitor Mi detects an increase in dissolved salt in the inflow condensate, immediately close the valves 13 and 17.
Valve 15. , 16 to allow the second column effluent to pass to the third column, the mixed-bed desalination column 5, to continue the treatment. Regarding the regeneration of the hot bed type resin layer 6 of the third column, although not particularly shown in the figure, it can be carried out by either an in-column regeneration method or an off-site regeneration method, and the method is a normal H cycle condensate treatment. The method used in the equipment may be followed, and special chemicals or strict separation of mixed resins are not required.
また、再生時期は、第3塔が待機の状態にあるときを選
ぶと、第3塔の再生のために復水処理装置の運転を停止
する必要もない。本発明の方法によると、平常時におい
ては、不純物含有量の極めて少ない粒状樹脂層と粉末樹
脂プレコート層を通して復水処理を行なうので、Hサイ
クルはもとよりアンモニアサイクルの運転においても特
殊な薬品と再生操作なしで、高純度の処理水を得ること
ができるものである。Further, if the regeneration timing is selected when the third tower is in a standby state, there is no need to stop the operation of the condensate treatment equipment for regenerating the third tower. According to the method of the present invention, under normal conditions, condensate treatment is performed through a granular resin layer with extremely low impurity content and a powder resin precoat layer, so special chemicals and regeneration operations are required not only in the H cycle but also in the operation of the ammonia cycle. Highly purified treated water can be obtained without using
以上述べたように、本発明の方法によれば、ボィラ起動
時と復水器漏洩時のような復水純度の低し、場合には、
腸イオン交予期樹脂層と粉末イオン交換樹脂炉過層と濠
床式樹脂層の直列処理によって、また、復水純度の高い
平常時には、温床塔を除いた2段処理によって連続的に
復水処理を行ない処理能率を著しく高めることができ、
復水処理装置の再生薬剤の使用を大中に減少でき運転維
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大量に得ら
れ処理コストも経済的にできる利益がある。As described above, according to the method of the present invention, in cases where condensate purity is low, such as during boiler startup and condenser leakage,
Condensate is treated continuously by series treatment of intestinal ion exchange resin layer, powdered ion exchange resin furnace layer, and moat bed type resin layer, and also in normal times when condensate purity is high, by two-stage treatment excluding the hot bed tower. processing efficiency can be significantly increased by
The use of regeneration chemicals in the condensate treatment equipment can be drastically reduced, operation and maintenance is easy, and the drawbacks of conventional condensate desalination methods have been eliminated, resulting in extremely high purity even in H cycle as well as NH3 cycle operation. The advantage is that a large amount of treated water can be obtained stably and the treatment cost can be reduced economically.
【図面の簡単な説明】
図面は本発明の一実施態様を示す系統説明図である。
1……腸イオン交予期樹脂塔、2……陽イオン交換樹脂
層、3・…・・プレコート炉過機、4・・・・・・プレ
コート炉過層、5…・・・混床式脱塩塔、6・・・・・
・混床式樹脂層、7,8,9,10,11,12,13
,14,15,16,17・・・・・・弁、Mi・・・
・・・流入復水水質監視計、Mc・・・・・・プレコー
ト炉過機流出水水質監視計、Me・・・・・・濠床式脱
塩塔流出水水質監視計。BRIEF DESCRIPTION OF THE DRAWINGS The drawing is a system explanatory diagram showing one embodiment of the present invention. 1...Resin column for intestinal ion exchange, 2...Cation exchange resin layer, 3...Pre-coating furnace filter, 4...Pre-coating furnace filter, 5...Mixed bed desorption Salt tower, 6...
・Mixed bed type resin layer, 7, 8, 9, 10, 11, 12, 13
, 14, 15, 16, 17... Valve, Mi...
...Inflow condensate water quality monitor, Mc...Precoat furnace filtration machine effluent water quality monitor, Me...Moat bed type desalination tower effluent water quality monitor.
Claims (1)
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、
復水を粒状陽イオン交換樹脂を充填した第1塔へ通して
処理する吸着濾過工程と、引き続いて粉末の陽イオン交
換樹脂と陰イオン交換樹脂とを混合してプレコートした
第2塔のプレコート濾過機へ直列に通水して処理するプ
レコート濾過工程と、復水中の不純物量が比較的多いボ
イラ起動時あるい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塔の混合式脱塩
塔へ通水して処理する脱塩工程とからなる復水処理方法
。 2 前記吸着濾過工程が、H形若しくはNH_4形の陽
イオン交換樹脂を充填された第1塔で行なわれるもので
あり、またプレコート濾過工程が、H形とOH形との組
合せ或いはNH_4形とOH形との組合せとの混合床の
ある第2塔で行なわれるものであつて、且つ、前記脱塩
工程が、H形の陽イオン交換樹脂とOH形の陰イオン交
換樹脂との混合床で処理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。 3 前記プレコート濾過工程が、その第1塔内樹脂を逆
洗又は通薬再生している間は、復水を吸着濾過工程を経
ないで単独で処理するか、もしくは、脱塩工程と直列的
に併用して行なわれるものである特許請求の範囲第1項
、又は第2項記載の復水処理方法。 4 前記プレコート濾過工程が、新しい濾過助材をプレ
コートしている間は、第2塔をバイパスして、復水を吸
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項又は、第2項記載の復水処理方法。 5 前記脱塩工程が、その脱塩塔内樹脂の再生中には、
復水を脱塩工程を経ないで吸着濾過工程とプレコート濾
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、又は第2項記載の
復水処理方法。[Scope of Claims] 1. Impurities in condensate are removed in a condensate treatment process in which boiler condensate is passed through a pre-coated filter pre-coated with powdered ion-exchange resin and an ion-exchange resin column filled with granular ion-exchange resin to remove impurities in condensate. During normal times when the amount is small,
An adsorption filtration process in which condensate is passed through a first column filled with granular cation exchange resin, followed by precoat filtration in a second column in which powdered cation exchange resin and anion exchange resin are mixed and precoated. In the pre-coat filtration step, in which water is passed through the machine in series for treatment, and when the boiler starts up or the condenser leaks, when the amount of impurities in the condensate is relatively large, the condensate treated in the first and second columns is A condensate treatment method comprising a desalination step in which water is passed through a mixed demineralization tower of a third tower filled with a mixture of granular cation exchange resin and anion exchange resin. 2. The adsorption filtration step is carried out in the first column filled with H type or NH_4 type cation exchange resin, and the precoat filtration process is performed using a combination of H type and OH type or NH_4 type and OH type. the desalting step is carried out in a second column with a mixed bed of a combination of H-form cation exchange resin and OH-form anion exchange resin; The condensate treatment method according to claim 1, wherein the condensate treatment method is performed. 3. While the pre-coat filtration step backwashes or regenerates the resin in the first column, the condensate is treated alone without going through the adsorption filtration step, or in series with the desalination step. The condensate treatment method according to claim 1 or 2, which is carried out in combination with. 4. While the pre-coat filtration step pre-coats a new filter aid, the second column is bypassed and the condensate is processed from the adsorption filtration step to the desalination step, or The condensate treatment method according to item 2. 5. During the desalting step, during the regeneration of the resin in the desalting tower,
The method according to claim 1 or 2, wherein the condensate is treated in an adsorption filtration step and a precoat filtration step without going through a desalination step and is omitted from the actual condensate treatment step. Condensate treatment method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53101662A JPS6036829B2 (en) | 1978-08-21 | 1978-08-21 | Condensate treatment method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53101662A JPS6036829B2 (en) | 1978-08-21 | 1978-08-21 | Condensate treatment method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5528733A JPS5528733A (en) | 1980-02-29 |
| JPS6036829B2 true JPS6036829B2 (en) | 1985-08-22 |
Family
ID=14306575
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP53101662A Expired JPS6036829B2 (en) | 1978-08-21 | 1978-08-21 | Condensate treatment method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6036829B2 (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0240447U (en) * | 1988-09-14 | 1990-03-19 | ||
| KR100426051B1 (en) * | 2001-07-26 | 2004-04-06 | 린나이코리아 주식회사 | Condensate water disposal for boiler |
| CN103304070A (en) * | 2013-07-08 | 2013-09-18 | 南通市长海实业有限公司 | Condensate water recycling device |
-
1978
- 1978-08-21 JP JP53101662A patent/JPS6036829B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5528733A (en) | 1980-02-29 |
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