JPS6251146B2 - - Google Patents
Info
- Publication number
- JPS6251146B2 JPS6251146B2 JP57135709A JP13570982A JPS6251146B2 JP S6251146 B2 JPS6251146 B2 JP S6251146B2 JP 57135709 A JP57135709 A JP 57135709A JP 13570982 A JP13570982 A JP 13570982A JP S6251146 B2 JPS6251146 B2 JP S6251146B2
- Authority
- JP
- Japan
- Prior art keywords
- exchange resin
- iron removal
- resin
- regeneration
- type
- 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
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 98
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 claims description 82
- 229910052742 iron Inorganic materials 0.000 claims description 49
- 238000011069 regeneration method Methods 0.000 claims description 42
- 230000008929 regeneration Effects 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 26
- 235000006408 oxalic acid Nutrition 0.000 claims description 25
- 239000011347 resin Substances 0.000 claims description 24
- 229920005989 resin Polymers 0.000 claims description 24
- 239000003729 cation exchange resin Substances 0.000 claims description 23
- 238000000034 method Methods 0.000 claims description 18
- 150000007522 mineralic acids Chemical class 0.000 claims description 18
- 239000003957 anion exchange resin Substances 0.000 claims description 15
- 239000003456 ion exchange resin Substances 0.000 claims description 10
- 229920003303 ion-exchange polymer Polymers 0.000 claims description 10
- 239000007788 liquid Substances 0.000 claims description 8
- 239000011259 mixed solution Substances 0.000 claims description 6
- 230000001172 regenerating effect Effects 0.000 claims description 5
- 239000000243 solution Substances 0.000 claims description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 20
- 230000000694 effects Effects 0.000 description 19
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 18
- 235000002639 sodium chloride Nutrition 0.000 description 18
- 150000003839 salts Chemical class 0.000 description 16
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 15
- 238000007796 conventional method Methods 0.000 description 13
- 239000003795 chemical substances by application Substances 0.000 description 11
- 229910021529 ammonia Inorganic materials 0.000 description 9
- 239000011734 sodium Substances 0.000 description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 7
- 101100112083 Arabidopsis thaliana CRT1 gene Proteins 0.000 description 6
- 101100238301 Arabidopsis thaliana MORC1 gene Proteins 0.000 description 6
- 102100024405 GPI-linked NAD(P)(+)-arginine ADP-ribosyltransferase 1 Human genes 0.000 description 6
- 101000981252 Homo sapiens GPI-linked NAD(P)(+)-arginine ADP-ribosyltransferase 1 Proteins 0.000 description 6
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 6
- 101100519629 Saccharomyces cerevisiae (strain ATCC 204508 / S288c) PEX2 gene Proteins 0.000 description 6
- 101100468521 Saccharomyces cerevisiae (strain ATCC 204508 / S288c) RFX1 gene Proteins 0.000 description 6
- 238000010612 desalination reaction Methods 0.000 description 6
- 229940062993 ferrous oxalate Drugs 0.000 description 6
- OWZIYWAUNZMLRT-UHFFFAOYSA-L iron(2+);oxalate Chemical compound [Fe+2].[O-]C(=O)C([O-])=O OWZIYWAUNZMLRT-UHFFFAOYSA-L 0.000 description 6
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 5
- 238000005253 cladding Methods 0.000 description 5
- 235000011121 sodium hydroxide Nutrition 0.000 description 5
- 239000003814 drug Substances 0.000 description 4
- 238000012546 transfer Methods 0.000 description 4
- 239000002253 acid Substances 0.000 description 3
- 229940023913 cation exchange resins Drugs 0.000 description 3
- 239000003638 chemical reducing agent Substances 0.000 description 3
- 150000001875 compounds Chemical class 0.000 description 3
- 235000013980 iron oxide Nutrition 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 229940039748 oxalate Drugs 0.000 description 3
- 238000005070 sampling Methods 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 229910052708 sodium Inorganic materials 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 2
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- 150000001450 anions Chemical class 0.000 description 2
- 150000001768 cations Chemical class 0.000 description 2
- GRWZHXKQBITJKP-UHFFFAOYSA-L dithionite(2-) Chemical compound [O-]S(=O)S([O-])=O GRWZHXKQBITJKP-UHFFFAOYSA-L 0.000 description 2
- 229940079593 drug Drugs 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- -1 iron oxide Chemical class 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 239000012047 saturated solution Substances 0.000 description 2
- 239000011780 sodium chloride Substances 0.000 description 2
- ZNCPFRVNHGOPAG-UHFFFAOYSA-L sodium oxalate Chemical compound [Na+].[Na+].[O-]C(=O)C([O-])=O ZNCPFRVNHGOPAG-UHFFFAOYSA-L 0.000 description 2
- 229940039790 sodium oxalate Drugs 0.000 description 2
- LSNNMFCWUKXFEE-UHFFFAOYSA-M Bisulfite Chemical compound OS([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-M 0.000 description 1
- 229910002588 FeOOH Inorganic materials 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 238000005349 anion exchange Methods 0.000 description 1
- 125000000129 anionic group Chemical group 0.000 description 1
- 229910001566 austenite Inorganic materials 0.000 description 1
- 125000002091 cationic group Chemical group 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000005115 demineralization Methods 0.000 description 1
- 230000002328 demineralizing effect Effects 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- IRXRGVFLQOSHOH-UHFFFAOYSA-L dipotassium;oxalate Chemical compound [K+].[K+].[O-]C(=O)C([O-])=O IRXRGVFLQOSHOH-UHFFFAOYSA-L 0.000 description 1
- 238000001125 extrusion Methods 0.000 description 1
- 239000000945 filler Substances 0.000 description 1
- 150000002429 hydrazines Chemical class 0.000 description 1
- 150000002505 iron Chemical class 0.000 description 1
- 150000002506 iron compounds Chemical class 0.000 description 1
- VBMVTYDPPZVILR-UHFFFAOYSA-N iron(2+);oxygen(2-) Chemical class [O-2].[Fe+2] VBMVTYDPPZVILR-UHFFFAOYSA-N 0.000 description 1
- 239000010812 mixed waste Substances 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 150000003891 oxalate salts Chemical class 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000005201 scrubbing Methods 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 229910000859 α-Fe Inorganic materials 0.000 description 1
- 229910006540 α-FeOOH Inorganic materials 0.000 description 1
- 229910006299 γ-FeOOH Inorganic materials 0.000 description 1
Landscapes
- Treatment Of Water By Ion Exchange (AREA)
Description
【発明の詳細な説明】
本発明は、イオン交換樹脂に付着したクラツド
すなわち酸化鉄等の鉄化合物を主体とする腐蝕生
成物を除去する方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for removing corrosion products mainly consisting of iron compounds such as iron oxide, that is, crud adhering to ion exchange resins.
イオン交換樹脂にクラツドが付着すると、その
交換容量が低下するだけでなく鉄分が恒常的に漏
出し処理水質が悪化する。このような状態を避け
るため例えば火力発電所の復水脱塩装置において
は、クラツド付着量が500mg/−RasFe程度以
上になるとクラツド除去処理(以下、「除鉄回生
処理」と記す)が行われている。 When crud adheres to the ion exchange resin, not only does its exchange capacity decrease, but iron content constantly leaks out and the quality of treated water deteriorates. To avoid this situation, for example, in condensate desalination equipment at thermal power plants, crud removal treatment (hereinafter referred to as ``iron removal regeneration treatment'') is performed when the amount of crud adhesion exceeds approximately 500 mg/-RasFe. ing.
従来、除鉄回生処理のため種々の除鉄回生剤が
提案され、かつ実用に供されているが、次のよう
な大きな問題点がある。 Conventionally, various iron removal and regeneration agents have been proposed and put into practical use for iron removal and regeneration treatment, but they have the following major problems.
すなわち、以下復水脱塩装置を例に説明するが
例えばハイドロサルフアイト、亜硫酸塩、亜硫酸
水素塩、ヒドラジン塩等の還元剤をイオン交換樹
脂に接触させ、樹脂に付着しているクラツドを還
元することにより可溶性のものとして除去するこ
とが行われている。また、この際これら還元剤だ
けでなく樹脂イオン型の調整、処理液PHの調整、
有機物の除去等のため食塩あるいはその他の
Na、K、CL、SO4等を含む塩類、アルカリ、酸
が併用されるため、使用する除鉄回生剤に含まれ
る塩類に応じて除鉄回生処理後はカチオン交換樹
脂はNa型、アニオン交換樹脂はCl型等の塩型に
変わつてしまう。 That is, as explained below using a condensate desalination apparatus as an example, for example, a reducing agent such as hydrosulfite, sulfite, bisulfite, hydrazine salt, etc. is brought into contact with an ion exchange resin to reduce the crud adhering to the resin. By doing so, it is removed as a soluble substance. At this time, in addition to these reducing agents, we also adjust the resin ion type, adjust the processing liquid PH,
Add salt or other substances to remove organic matter, etc.
Since salts, alkalis, and acids containing Na, K, CL, SO 4 , etc. are used together, the cation exchange resin may be Na type or anion exchange resin after iron removal regeneration treatment, depending on the salts contained in the iron removal regeneration agent used. The resin turns into a salt type such as Cl type.
復水脱塩装置においては、特にこのような塩型
に変換してしまつた樹脂はアンモニアサイクルを
実施するために大きな障害となるのでほぼ100%
近くカチオン交換樹脂はH型又はNH4型に、アニ
オン交換樹脂はOH型に変換する必要があるが、
これら塩型樹脂の再生には大量の再生剤が必要で
ある。 In condensate desalination equipment, the resin that has been converted into salt type is a major obstacle to carrying out the ammonia cycle, so almost 100% of the resin must be removed.
In the near future, cation exchange resins will need to be converted to H type or NH4 type, and anion exchange resins will need to be converted to OH type.
A large amount of regenerating agent is required to regenerate these salt type resins.
例えば80%がNa型に変換したカチオン交換樹
脂(ポーラス型強酸性陽イオン交換樹脂)は
10eq/−RのH2SO4で再生しても1%のNa型
が残り、アンモニアサイクルを実施するのに必要
な0.1%以下にすることは殆ど不可能である。ま
た、アニオン交換樹脂(ポーラス型、I型強塩基
性陰イオン交換樹脂)のOH型への変換は更に難
しく、100%Cl型の樹脂を10eq/−RのNaOH
で再生しても25%程度は残留してしまい、Clの
漏出量を1.5ppb以下にするのに必要な3%以下
にすることはとてもできない。 For example, cation exchange resin (porous strong acid cation exchange resin) with 80% converted to Na type
Even when regenerated with 10 eq/-R of H 2 SO 4 , 1% Na type remains, and it is almost impossible to reduce the Na type to less than 0.1%, which is necessary to carry out an ammonia cycle. In addition, it is more difficult to convert anion exchange resins (porous type, I-type strongly basic anion exchange resins) to OH type, and converting 100% Cl type resin to 10 eq/-R of NaOH
Even if it is regenerated, about 25% remains, and it is impossible to reduce the amount of Cl leakage to below 3%, which is required to reduce the amount of leakage to below 1.5 ppb.
このように、従来の除鉄回生処理方法では、再
生後も多量の塩型が残り、現在火力発電所で通常
行われているアンモニアサイクルを実施すると大
量のNa、Clの漏出が生じてしまう。それ故除鉄
回生処理後の樹脂は、すぐにはアンモニアサイク
ルを実施できず5サイクル以上、約1ケ月以上は
H−OHサイクルを実施し、塩型の低下したのを
見計つてアンモニアサイクルに移行しているのが
実状である。 As described above, in the conventional iron removal regeneration treatment method, a large amount of salt remains after regeneration, and when the ammonia cycle that is currently used in thermal power plants is implemented, a large amount of Na and Cl leaks. Therefore, the resin after iron removal regeneration treatment cannot be subjected to an ammonia cycle immediately, but is subjected to an H-OH cycle for 5 cycles or more, and for about 1 month or more, and then an ammonia cycle is carried out after the salt content has decreased. The reality is that the situation is shifting.
本発明はこのような従来方法の欠点を解消し、
極めて効果的に除鉄回生処理を行うと共に、その
後の再生工程及び採水工程を円滑に行うことがで
きる方法を提供することを目的とするものであ
る。 The present invention eliminates the drawbacks of such conventional methods,
It is an object of the present invention to provide a method that can extremely effectively perform iron removal regeneration treatment and also smoothly perform the subsequent regeneration process and water sampling process.
本発明は、クラツドの付着したイオン交換樹脂
を除鉄回生するに際し、蓚酸及び/又は蓚酸塩を
含む液で処理した後、無機酸を通薬することを特
徴とするイオン交換樹脂の除鉄回生方法である。 The present invention provides iron removal and regeneration of ion exchange resins, which is characterized in that when iron is removed and regenerated from ion exchange resins with crud attached, the resins are treated with a solution containing oxalic acid and/or oxalate, and then passed through with an inorganic acid. It's a method.
以下、本発明を復水脱塩装置を例にとり詳細に
説明すると、復水脱塩装置のイオン交換樹脂に付
着しているクラツドは、おおよそ磁性酸化鉄
(Fe3O4とγ−Fe2O3)、α−Fe2O3、γ−
FeOOH、α−FeOOH及び非晶質とに分けられ
る。火力発電所では磁性酸化鉄、γ−FeOOH、
非晶質の三つが主体であるといわれる。また、樹
脂に付着しているクラツドの形態はカチオン樹
脂、アニオン樹脂で異なるといわれているが、そ
の詳細は現在不明である。 Hereinafter, the present invention will be explained in detail using a condensate desalination device as an example. Clads attached to the ion exchange resin of the condensate desalination device are composed of approximately magnetic iron oxides (Fe 3 O 4 and γ-Fe 2 O 3 ), α−Fe 2 O 3 , γ−
It is divided into FeOOH, α-FeOOH and amorphous. In thermal power plants, magnetic iron oxide, γ-FeOOH,
It is said that the three main types are amorphous. Furthermore, the morphology of the cladding attached to the resin is said to be different between cationic and anionic resins, but the details are currently unknown.
しかして本発明者等は、実際に火力発電所で使
用されている樹脂の薬品による除鉄回生方法につ
いて鋭意研究した結果、蓚酸及び蓚酸塩がカチオ
ン交換樹脂の除鉄回生に大きな効果を有している
ことを見い出し本発明を完成したものである。 However, as a result of intensive research into iron removal regeneration methods using resin chemicals actually used in thermal power plants, the present inventors found that oxalic acid and oxalate have a great effect on iron removal regeneration from cation exchange resins. The present invention has been completed by discovering that
すなわち、カチオン交換樹脂を蓚酸(塩)で処
理するとクラツドは蓚酸第一鉄となり、この化合
物は溶解度が低いため処理上澄液中には鉄はわず
かしか溶出していないが、蓚酸(塩)で処理した
のち硫酸、塩酸、硝酸等の無機酸を通薬すること
により、沈殿したあるいは樹脂に付着した蓚酸第
一鉄は完全に除去され除鉄効果として硫酸で60〜
70%、塩酸で90%以上が達成され従来法より著し
く高い効果がある。また、蓚酸(塩)単独でなく
蓚酸(塩)と無機酸の混合液で処理したのち無機
酸を通薬すると更に除鉄効果が大きく、一度使用
した蓚酸(塩)あるいは蓚酸(塩)と無機酸との
混合廃液を再使用しても十分な効果がある。 In other words, when a cation exchange resin is treated with oxalic acid (salt), the clad becomes ferrous oxalate, and since this compound has low solubility, only a small amount of iron is eluted into the treated supernatant, but oxalic acid (salt) After treatment, the ferrous oxalate that has precipitated or adhered to the resin is completely removed by passing an inorganic acid such as sulfuric acid, hydrochloric acid, or nitric acid through the resin.
70%, and more than 90% with hydrochloric acid, which is significantly more effective than conventional methods. In addition, treatment with a mixture of oxalic acid (salt) and an inorganic acid, rather than using oxalic acid (salt) alone, and then passing through the inorganic acid has an even greater iron removal effect. Even if the mixed waste liquid with acid is reused, there is a sufficient effect.
本発明方法は、従来方法が還元剤の作用により
一度にクラツドを溶解性のものとして除去するの
に対して、蓚酸第一鉄等の溶解度の小さい化合物
としたのち、再生を兼ねて無機酸により、これら
を除去することに特徴がある。蓚酸第一鉄として
沈殿したものは無機酸(再生剤)によつて、例え
ば硫酸ならびに濃度を4〜8%に調整したもの
を、カチオン交換樹脂1に対してSV2〜4で
200〜400通薬することにより完全に溶解除去で
き、硫酸の通薬後は蓚酸第一鉄が沈殿して残留す
ることは全くなく、その後の採水に問題となるこ
とはない。 In contrast to the conventional method, in which the cladding is removed as a soluble compound at once by the action of a reducing agent, in the method of the present invention, a compound with low solubility such as ferrous oxalate is removed, and then an inorganic acid is used to regenerate the cladding. , is characterized by the removal of these. The precipitated ferrous oxalate is treated with an inorganic acid (regenerating agent), for example, sulfuric acid and the concentration adjusted to 4-8%, at SV2-4 for 1 part cation exchange resin.
It can be completely dissolved and removed by passing 200 to 400 times, and after passing sulfuric acid, ferrous oxalate does not precipitate and remain, causing no problems with subsequent water sampling.
前述した如く除鉄回生処理後も樹脂のイオン型
がH型、OH型に維持されるのが非常に好ましい
が、本発明では蓚酸と無機酸を利用することによ
り、カチオン交換樹脂の塩型への変換は完全に避
けられると共に除鉄効果も従来方法より大きい。
蓚酸塩例えば蓚酸ナトリウム、蓚酸カリウム等も
蓚酸と同等の除鉄効果がある。本発明で用いる蓚
酸(塩)は従来の除鉄回生剤として用いられてい
るハイドロサルフアイト、亜硫酸塩等のように処
理中に有害な亜硫酸ガスを発生することもなく、
取扱いが極めて容易である。 As mentioned above, it is very preferable that the ion type of the resin is maintained in the H type or OH type even after iron removal regeneration treatment, but in the present invention, by using oxalic acid and inorganic acid, the cation exchange resin can be changed to the salt type. The conversion of iron is completely avoided, and the iron removal effect is also greater than that of conventional methods.
Oxalates such as sodium oxalate and potassium oxalate have the same iron removal effect as oxalic acid. The oxalic acid (salt) used in the present invention does not generate harmful sulfur dioxide gas during treatment, unlike hydrosulfite, sulfite, etc. used as conventional iron removal and regeneration agents.
Extremely easy to handle.
一方、アニオン交換樹脂については、蓚酸
(塩)による除鉄効果はカチオン交換樹脂におけ
るほど大きくはない。これは、付着しているクラ
ツドの形態が両者で異なつていることによるもの
であろう。それ故、アニオン交換樹脂に対しては
所望により従来の除鉄回生剤を使用してもよい。
この場合、アニオン交換樹脂は有機物の除去、イ
オン型の調整等のため食塩を用いることが普通で
あるため処理後はCl型になつている。Cl型のま
ま再生を行つても前述の如くCl型をアンモニア
サイクル運転に必要な3%以下にすることは難し
い。それ故、カチオン交換樹脂の除鉄回生と再生
を兼ねて通薬する無機酸(この場合は特に硫酸)
をカチオン交換樹脂、アニオン交換樹脂の順に通
薬することによりアニオン交換樹脂を再生の容易
なSO4型に変換したのち苛性ソーダによつてOH
型にすることが好ましい。この場合、苛性ソーダ
の再生レベルは通常の2〜3倍量で十分であり、
若干SO4型が残るがアンモニアサイクル時もSO4
は漏出しにくいため、そのままアンモニアサイク
ルに移行できる。 On the other hand, for anion exchange resins, the effect of iron removal by oxalic acid (salt) is not as great as that for cation exchange resins. This is probably due to the fact that the morphology of the attached crud is different between the two. Therefore, conventional iron removal and regeneration agents may be used for the anion exchange resin, if desired.
In this case, the anion exchange resin is usually in the Cl type after treatment because common salt is used to remove organic matter and adjust the ionic type. Even if regeneration is performed in the Cl type, it is difficult to reduce the Cl type to 3% or less, which is required for ammonia cycle operation, as described above. Therefore, an inorganic acid (especially sulfuric acid in this case) is used to remove iron and regenerate the cation exchange resin.
The anion exchange resin is converted to the easily regenerated SO 4 type by passing it through a cation exchange resin and an anion exchange resin in that order, and then OH with caustic soda.
It is preferable to make it into a mold. In this case, the regeneration level of caustic soda is sufficient at 2 to 3 times the normal amount.
Although some SO 4 type remains, SO 4 remains even during the ammonia cycle.
Because it is difficult to leak, it can be transferred directly to the ammonia cycle.
次に、本発明の実施態様を第1図に沿つて説明
する。 Next, an embodiment of the present invention will be described with reference to FIG.
(1) 脱塩塔(図示せず)よりカチオン再生塔兼分
離塔(以下、「CRT」と略記する)1へ樹脂を
移送後、通常の逆洗分離操作を行いアニオン交
換樹脂はアニオン再生塔(以下、「ART」と略
記する)2へ移送ラインの弁3を開とし移送す
る。(1) After transferring the resin from the demineralization tower (not shown) to the cation regeneration tower/separation tower (hereinafter abbreviated as "CRT") 1, a normal backwash separation operation is performed and the anion exchange resin is transferred to the anion regeneration tower. (hereinafter abbreviated as "ART") 2, open the valve 3 of the transfer line and transfer.
(2) 移送終了後CRT1へ蓚酸飽和溶液タンク4
よりエゼクタによりカチオン交換樹脂1に対
して蓚酸を1〜20g注入し、かつ濃度が0.5〜
8%になるよう希釈調整する。また、必要に応
じ通常の再生ラインより濃度0.5〜15%の無機
酸を注入する。そして弁7を開として空気を導
入し、エアスクラビングを5〜10分間行い樹脂
を混合する。そして30分毎程度に1〜2分エア
スクラビングを行い30分〜5時間程度放置す
る。この時のカチオン交換樹脂のイオン型はH
型であつてもNH4型であつてもかまわない。蓚
酸の濃度は高い方がよく1〜4%が適当であ
り、無機酸の濃度も4〜10%と高めに設定して
おく方が除鉄効果は大きくなる。(2) After completion of transfer, transfer oxalic acid saturated solution tank 4 to CRT1
Then, 1 to 20 g of oxalic acid is injected to 1 part of the cation exchange resin using the ejector, and the concentration is 0.5 to 1.
Adjust the dilution to 8%. Additionally, if necessary, inorganic acid with a concentration of 0.5 to 15% is injected from the normal regeneration line. Then, valve 7 is opened to introduce air, and air scrubbing is performed for 5 to 10 minutes to mix the resin. Then air scrub for 1 to 2 minutes every 30 minutes and leave it for 30 minutes to 5 hours. The ionic type of the cation exchange resin at this time is H
It does not matter if it is a type or NH4 type. The higher the concentration of oxalic acid, the more appropriate it is 1-4%, and the iron removal effect will be greater if the concentration of inorganic acid is also set higher, 4-10%.
(3) ART2については従来の除鉄回生剤を投入
して処理する。通常食塩と除鉄回生剤が投入さ
れる。(3) Regarding ART2, the conventional iron removal regeneration agent will be used for treatment. Normal table salt and iron removal regeneration agent are added.
(4) CRT1,ART2ともに一定時間放置後押出
しを行い、次いでCRT1へ4〜10%の無機酸
(硫酸の場合、通常再生レベルの2〜3倍量、
200〜400g/−Ras66゜Be´H2SO4)を通常
の再生ラインよりSV3〜4で通薬する。このと
きの再生廃液は再生廃液の通薬ライン6の弁5
を開にしてART2へも通薬し、弁8を開とし
て排出する。次いで押出、洗浄を行う。ここま
での操作でCRT1のカチオン交換樹脂の除
鉄、再生は終了する。ART2のアニオン交換
樹脂は除鉄回生処理により一旦Cl型になるが
CRT1からH2SO4再生廃液の通薬によりSO4型
に変換する。(4) Extrude both CRT1 and ART2 after leaving them for a certain period of time, then add 4 to 10% inorganic acid (in the case of sulfuric acid, 2 to 3 times the normal regeneration level) to CRT1.
200 to 400 g/-Ras66°Be'H 2 SO 4 ) is passed through a normal regeneration line at SV3 to 4. The regenerated waste liquid at this time is
Open valve 8 to allow the medicine to pass through ART2, and open valve 8 to discharge the medicine. Next, extrusion and washing are performed. With the operations up to this point, iron removal and regeneration of the cation exchange resin of CRT1 is completed. The anion exchange resin of ART2 becomes Cl type once due to iron removal regeneration treatment.
By passing the H 2 SO 4 regenerated waste liquid from CRT1, it is converted to SO 4 type.
(5) ART2へ更に通常再生レベルの2〜3倍量
の苛性ソーダを通薬し再生する。(5) ART2 is further regenerated by passing 2 to 3 times the amount of caustic soda at the normal regeneration level.
このように、図示例においては従来の再生装置
にCRT1の再生廃液をART2へ通薬することに
より、除鉄回生後のカチオン交換樹脂にNa型等
の塩型の生成は全くなくまた、アニオン交換樹脂
もOH型に変換され、一部SO4型が残つているが
影響はなく、そのままアンモニアサイクルの実施
に移行できる。 In this way, in the illustrated example, by passing the regenerated waste liquid from CRT1 through the conventional regenerator to ART2, there is no generation of salt types such as Na type in the cation exchange resin after iron removal and regeneration, and anion exchange The resin is also converted to the OH type, and although some SO 4 type remains, it has no effect and can be transferred to the ammonia cycle as is.
次に、本発明の実施例について記す。 Next, examples of the present invention will be described.
実施例
火力発電所で5ケ年間使用したカチオン交換樹
脂について本発明の除鉄回生処理を行つたところ
第2図、第3図の結果を得た。第4図は無機酸の
通薬のみによる処理の結果を示す。EXAMPLE When the iron removal regeneration treatment of the present invention was applied to a cation exchange resin that had been used for five years at a thermal power plant, the results shown in FIGS. 2 and 3 were obtained. FIG. 4 shows the results of treatment with inorganic acid only.
第2図はカチオン交換樹脂1についての処理
液量が蓚酸100g、H2SO4200gとなるように、濃
度4%の蓚酸と、濃度8%の硫酸との混合液で5
時間処理した後濃度8%の各無機酸(4種類)を
SV3で通薬したときの結果を示す。H2SO4(1)は
新品混合液で処理した場合、H2SO4(2)は混合液を
回収し再使用したときの効果を示す。従来法は従
来の除鉄回生剤、すなわち硫黄酸化物を主体とす
るもので処理した後H2SO4を通薬した場合であ
り、最も効果があるといわれるものである。 Figure 2 shows a mixture of oxalic acid with a concentration of 4% and sulfuric acid with a concentration of 8% so that the amount of treated liquid for cation exchange resin 1 is 100 g of oxalic acid and 200 g of H 2 SO 4 .
After treatment for a period of time, each inorganic acid (4 types) at a concentration of 8% was added.
The results are shown when administering the drug using SV3. H 2 SO 4 (1) shows the effect when treated with a new mixed solution, and H 2 SO 4 (2) shows the effect when the mixed solution is recovered and reused. The conventional method is said to be the most effective method, in which H 2 SO 4 is passed through treatment after treatment with a conventional iron removal regeneration agent, that is, one mainly composed of sulfur oxides.
第3図は蓚酸4%液で5時間処理後無機酸を通
薬した場合である。第2図、第3図より本発明法
が従来法に比較して20〜30%除鉄効果が大きいこ
とがわかる。なお第2図、第3図中破線は蓚酸・
硫酸混合液による除鉄効果を、蓚酸による除鉄効
果をそれぞれ示している。従来法においては除鉄
回生剤によりクラツドは溶解しイオン状になつて
しまい、このイオン状の鉄がカチオン交換樹脂に
イオン交換され、このイオン交換された鉄を無機
酸によつて脱着することがかなり困難であるため
従来法の効果が小さいものと考えられる。本発明
法は蓚酸の作用によりクラツドが蓚酸第一鉄のよ
うな沈殿物として樹脂に付着しているため、イオ
ン状になる割合が従来法より少く、それ故カチオ
ン交換樹脂に強固にイオン交換されることが少な
いため従来法より除鉄効果が大きいものと考えら
れる。 Figure 3 shows the case where the sample was treated with a 4% oxalic acid solution for 5 hours and then passed through with an inorganic acid. It can be seen from FIGS. 2 and 3 that the method of the present invention has a 20 to 30% greater iron removal effect than the conventional method. The broken lines in Figures 2 and 3 indicate oxalic acid.
The iron removal effect by sulfuric acid mixture and the iron removal effect by oxalic acid are shown respectively. In the conventional method, the iron removal regeneration agent dissolves the crud and turns it into an ionic form, and this ionic iron is ion-exchanged with a cation exchange resin, and this ion-exchanged iron can be desorbed using an inorganic acid. It is considered that the effect of the conventional method is small because it is quite difficult. In the method of the present invention, the cladding is attached to the resin as a precipitate such as ferrous oxalate due to the action of oxalic acid, so the proportion of the clad in ionic form is lower than in the conventional method, and therefore the cladding is strongly ion-exchanged with the cation exchange resin. It is thought that the iron removal effect is greater than that of the conventional method because there is less iron removal.
本発明法においては塩酸を用いると90%以上の
除鉄効果が得られる。蓚酸塩として蓚酸ナトリウ
ムを用いた場合も第2図と同様の効果が得られ
た。また、第2図より、蓚酸とH2SO4との混合液
をくり返し使用しても十分効果のあることが判明
した。第3図は蓚酸単独で処理した場合であり第
2図の混合液で処理した場合よりやや劣るが、従
来法よりはH2SO4の場合で5〜10%除鉄効果が大
きい。 In the method of the present invention, when hydrochloric acid is used, an iron removal effect of 90% or more can be obtained. The same effect as shown in FIG. 2 was also obtained when sodium oxalate was used as the oxalate. Furthermore, from FIG. 2, it was found that repeated use of a mixed solution of oxalic acid and H 2 SO 4 was sufficiently effective. FIG. 3 shows the case of treatment with oxalic acid alone, which is slightly inferior to the case of treatment with the mixed solution shown in FIG. 2, but the iron removal effect is greater by 5 to 10% in the case of H 2 SO 4 than in the conventional method.
第2図で示した硫酸により処理したカチオン交
換樹脂と、同一の混合液に7日間浸漬したアニオ
ン交換樹脂を苛性ソーダで再生したものの両樹脂
について交換容量を測定したが全く低下していな
かつた。また、両樹脂の混合床で復水の処理を行
つたところ、その処理水は導電率で0.055〜0.06
μS/cmが得られ、本発明法によつて樹脂が劣化
するようなことはないことが確認された。 The exchange capacity was measured for both the cation exchange resin treated with sulfuric acid shown in Figure 2 and the anion exchange resin immersed in the same mixed solution for 7 days and regenerated with caustic soda, and no decrease was found at all. In addition, when condensate was treated in a mixed bed of both resins, the treated water had an electrical conductivity of 0.055 to 0.06.
μS/cm was obtained, and it was confirmed that the resin was not deteriorated by the method of the present invention.
以上述べた如く、本発明法によれば除鉄回生効
果は従来法より著しく大きく、再生剤として硫酸
を用いた場合従来の除鉄回生剤では再生レベルを
通常の2倍量(約300g/−Ras CaCO3)を用
いても50%以下であるのに対し、本発明法では70
%程度の除去率が得られる。このように本発明法
は、除鉄回生の点で効果が大きいだけでなく、従
来法のように処理操作後塩型となることはなく、
その後の再生、採水に非常に好都合な除鉄回生法
であり、その益するところ大である。本発明は復
水脱塩装置に有益であるばかりでなくクラツドの
付着した純水装置、粉末イオン交換樹脂、その他
クラツドの付着した充てん剤の洗浄にも有効に適
用できるものである。 As mentioned above, according to the method of the present invention, the iron removal regeneration effect is significantly greater than that of the conventional method, and when sulfuric acid is used as a regenerating agent, the regeneration level is twice the normal amount (approximately 300 g/- Although it is less than 50% even when Ras CaCO 3 ) is used, the method of the present invention has a reduction of 70%.
% removal rate can be obtained. In this way, the method of the present invention is not only highly effective in terms of regenerating iron removal, but also does not become salt-type after treatment operations, unlike conventional methods.
This iron removal regeneration method is very convenient for subsequent regeneration and water sampling, and the benefits are great. The present invention is not only useful for condensate desalination equipment, but can also be effectively applied to cleaning crud-adhered pure water equipment, powdered ion exchange resins, and other crud-adhered fillers.
第1図は本発明の実施態様を示すフローシー
ト、第2図乃至第4図は本発明の実施例の結果を
示すグラフであつて、除鉄回生条件と除鉄効率の
対応を示すものである。
1……カチオン再生塔兼分離塔(CRT)、2…
…アニオン再生塔(ART)、3,5,7,8……
弁、4……蓚酸飽和溶液タンク、6……通薬ライ
ン。
Fig. 1 is a flow sheet showing an embodiment of the present invention, and Figs. 2 to 4 are graphs showing the results of an embodiment of the present invention, which show the correspondence between iron removal regeneration conditions and iron removal efficiency. be. 1...Cation regeneration tower/separation tower (CRT), 2...
...Anion regeneration tower (ART), 3, 5, 7, 8...
Valve, 4... Oxalic acid saturated solution tank, 6... Medication line.
Claims (1)
生するに際し、蓚酸及び/又は蓚酸塩を含む液で
処理した後、無機酸を通薬することを特徴とする
イオン交換樹脂の除鉄回生方法。 2 前記蓚酸又は蓚酸塩を含む液が、蓚酸及び/
又は蓚酸塩と無機酸との混合液である特許請求の
範囲第1項記載の方法。 3 前記クラツドの付着したイオン交換樹脂がカ
チオン交換樹脂とアニオン交換樹脂との混合樹脂
である場合に、該混合樹脂を個別の塔に分離した
のち前記カチオン交換樹脂について除鉄回生操作
を行う特許請求の範囲第1項又は第2項記載の方
法。 4 前記カチオン交換樹脂についての除鉄回生操
作において通薬した後の無機酸排出液を、アニオ
ン交換樹脂へ通液する特許請求の範囲第3項記載
の方法。[Scope of Claims] 1. An ion-exchange resin that is characterized in that, when regenerating iron removal from an ion-exchange resin to which crud is attached, the resin is treated with a solution containing oxalic acid and/or oxalate, and then passed through with an inorganic acid. Iron removal regeneration method. 2. The liquid containing oxalic acid or oxalate contains oxalic acid and/or oxalate.
Or the method according to claim 1, which is a mixed solution of oxalate and an inorganic acid. 3. When the ion exchange resin to which the crud is attached is a mixed resin of a cation exchange resin and an anion exchange resin, a patent claim in which the mixed resin is separated into individual columns and then an iron removal regeneration operation is performed on the cation exchange resin. The method according to item 1 or 2 of the scope. 4. The method according to claim 3, wherein the inorganic acid discharged liquid after being passed through the anion exchange resin in the iron removal regeneration operation for the cation exchange resin is passed through the anion exchange resin.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57135709A JPS5926143A (en) | 1982-08-05 | 1982-08-05 | Iron removing restoration of ion exchange resin |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57135709A JPS5926143A (en) | 1982-08-05 | 1982-08-05 | Iron removing restoration of ion exchange resin |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5926143A JPS5926143A (en) | 1984-02-10 |
| JPS6251146B2 true JPS6251146B2 (en) | 1987-10-28 |
Family
ID=15158047
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57135709A Granted JPS5926143A (en) | 1982-08-05 | 1982-08-05 | Iron removing restoration of ion exchange resin |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5926143A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6238247A (en) * | 1985-08-12 | 1987-02-19 | Hitachi Ltd | Method for regenerating ion exchange resin |
| US10532351B1 (en) * | 2018-08-29 | 2020-01-14 | Thomas O. Miller | Method for restoring kinetic properties of resin |
-
1982
- 1982-08-05 JP JP57135709A patent/JPS5926143A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5926143A (en) | 1984-02-10 |
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