JPH05261368A - Method and apparatus for producing pure water - Google Patents
Method and apparatus for producing pure waterInfo
- Publication number
- JPH05261368A JPH05261368A JP4091907A JP9190792A JPH05261368A JP H05261368 A JPH05261368 A JP H05261368A JP 4091907 A JP4091907 A JP 4091907A JP 9190792 A JP9190792 A JP 9190792A JP H05261368 A JPH05261368 A JP H05261368A
- Authority
- JP
- Japan
- Prior art keywords
- tower
- dissolved oxygen
- exchange resin
- pure water
- inert gas
- 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.)
- Granted
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 71
- 238000000034 method Methods 0.000 title description 24
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 45
- 239000001301 oxygen Substances 0.000 claims abstract description 45
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 45
- 239000011261 inert gas Substances 0.000 claims abstract description 32
- 239000003957 anion exchange resin Substances 0.000 claims abstract description 22
- 238000004519 manufacturing process Methods 0.000 claims abstract description 17
- 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 abstract description 16
- 239000003729 cation exchange resin Substances 0.000 claims abstract description 12
- 238000006114 decarboxylation reaction Methods 0.000 claims description 4
- 239000007788 liquid Substances 0.000 abstract description 21
- 239000010419 fine particle Substances 0.000 abstract description 17
- 239000007789 gas Substances 0.000 abstract description 11
- 150000002500 ions Chemical class 0.000 abstract description 8
- 238000005273 aeration Methods 0.000 abstract description 7
- 239000012535 impurity Substances 0.000 abstract description 7
- 239000003456 ion exchange resin Substances 0.000 abstract description 5
- 229920003303 ion-exchange polymer Polymers 0.000 abstract description 5
- 150000001450 anions Chemical class 0.000 abstract description 3
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 12
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 12
- 238000007796 conventional method Methods 0.000 description 11
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 8
- 229910001873 dinitrogen Inorganic materials 0.000 description 8
- 229910021642 ultra pure water Inorganic materials 0.000 description 7
- 239000012498 ultrapure water Substances 0.000 description 7
- 229910002092 carbon dioxide Inorganic materials 0.000 description 6
- 239000001569 carbon dioxide Substances 0.000 description 6
- 238000010586 diagram Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- 150000001768 cations Chemical class 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 230000006866 deterioration Effects 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 230000008929 regeneration Effects 0.000 description 2
- 238000011069 regeneration method Methods 0.000 description 2
- 239000011347 resin Substances 0.000 description 2
- 229920005989 resin Polymers 0.000 description 2
- 239000004065 semiconductor Substances 0.000 description 2
- 238000009849 vacuum degassing Methods 0.000 description 2
- 238000009423 ventilation Methods 0.000 description 2
- 239000002349 well water Substances 0.000 description 2
- 235000020681 well water Nutrition 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 1
- 230000002730 additional effect Effects 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 238000005349 anion exchange Methods 0.000 description 1
- 230000001580 bacterial effect Effects 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- -1 carbon dioxide ion Chemical class 0.000 description 1
- 238000005341 cation exchange Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000002542 deteriorative effect Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 230000007704 transition Effects 0.000 description 1
Landscapes
- Degasification And Air Bubble Elimination (AREA)
- Treatment Of Water By Ion Exchange (AREA)
- Physical Water Treatments (AREA)
Abstract
(57)【要約】
【目的】 液中に微粒子及び不純物イオンの増加を起こ
さずに純水を製造でき、純水中の溶存酸素を極低濃度ま
で除去しうる純水製造方法及び装置を提供すること。
【構成】 陽イオン交換樹脂塔2、脱炭酸塔3及び陰イ
オン交換樹脂塔6を含み、脱炭酸塔3の底部に不活性ガ
ス供給装置5を接続して不活性ガスで曝気するか又は陰
イオン交換樹脂塔6の後段に溶存酸素除去塔8を接続
し、その底部に不活性ガス供給装置5を接続し、溶存酸
素除去塔8の上部から排出されるガスを不活性ガス配管
10を介して脱炭酸塔3の底部に供給する。
(57) [Summary] [Purpose] To provide a pure water production method and apparatus capable of producing pure water without increasing fine particles and impurity ions in the liquid and removing dissolved oxygen in the pure water to an extremely low concentration. To do. [Structure] A cation exchange resin tower 2, a decarbonation tower 3 and an anion exchange resin tower 6 are included, and an inert gas supply device 5 is connected to the bottom of the decarbonation tower 3 for aeration with an inert gas or an anion. The dissolved oxygen removing tower 8 is connected to the subsequent stage of the ion exchange resin tower 6, the inert gas supply device 5 is connected to the bottom thereof, and the gas discharged from the upper portion of the dissolved oxygen removing tower 8 is passed through the inert gas pipe 10. Is supplied to the bottom of the decarbonation tower 3.
Description
【0001】[0001]
【産業上の利用分野】本発明は、空気中の不純物の混入
のない純水の製造方法及び装置に係り、特に、2B3T
型、4B5T型などのイオン交換樹脂塔と脱炭酸塔を組
み合わせてなる純水製造装置及びこれを用いた純水の製
造方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for producing pure water which does not contain impurities in the air, and particularly to 2B3T.
Type and 4B5T type ion exchange resin towers and decarbonation towers in combination, and a pure water manufacturing method using the same.
【0002】[0002]
【従来の技術】水中の各種イオンの除去にはイオン交換
法が広く使用されている。特に、大容量の純水を製造す
る場合には、陽イオン交換樹脂塔と陰イオン交換樹脂塔
との間に水中の炭酸イオンを除去する目的で脱炭酸塔が
設置されている。この脱炭酸塔は、陽イオン交換樹脂塔
からの流出水が低pHであり、後段の陰イオン交換樹脂の
負荷となる炭酸イオンを容易に炭酸ガスとして系外に排
出除去できることから、陽イオン交換樹脂塔と陰イオン
交換樹脂塔との間で空気曝気を行い、液中の炭酸ガスを
除去するものである。2. Description of the Related Art Ion exchange method is widely used to remove various ions in water. In particular, when producing a large volume of pure water, a decarbonation tower is installed between the cation exchange resin tower and the anion exchange resin tower for the purpose of removing carbonate ions in water. In this decarboxylation tower, the effluent water from the cation exchange resin tower has a low pH, and the carbonate ions that load the anion exchange resin in the subsequent stage can be easily discharged to the outside of the system as carbon dioxide gas. Air is aerated between the resin tower and the anion exchange resin tower to remove carbon dioxide gas in the liquid.
【0003】水中の炭酸イオンは、純水製造に用いる原
水、例えば、市水、井戸水などによってその含有量が異
なり、市水では10〜30ppm 、井戸水では20〜50
ppmの炭酸イオンが含まれている。したがって、この炭
酸イオンを除去することは、後段の陰イオン交換樹脂の
効率を高める上で重要であり、脱炭酸塔の役割は大き
い。The content of carbonate ions in water varies depending on the raw water used for producing pure water, for example, city water, well water, etc., and is 10 to 30 ppm in city water and 20 to 50 in well water.
Contains ppm carbonate ions. Therefore, the removal of the carbonate ion is important for increasing the efficiency of the anion exchange resin in the latter stage, and the role of the decarbonation tower is great.
【0004】しかしながら、空気曝気による脱炭酸法
は、純水中の炭酸ガスのみを対象とした場合には、従来
は大きな問題は生じなかったが、最近では、純水中に含
まれている有機物又は微粒子の問題が顕在化してきてい
る。このため、脱炭酸塔に吹き込む空気をフィルターに
かけ、空気中の微粒子を除去するなどの装置上の改善が
行われている。しかし、空気中の0.1〜0.5μmという
ような微細な粒子をフィルターによって充分に除去する
ことは困難である。また、脱炭酸塔を空気曝気すること
により微粒子以外の空気中の不純物、例えば、イオン、
有機物、細菌などが多く混入する。これらの不純物は、
脱炭酸塔の後段にある陰イオン交換樹脂塔及び混床塔に
悪影響を及ぼし、樹脂の再生頻度が増加する、純水中の
微粒子が増加するなどの問題が生じる。However, the decarbonation method by air aeration has not caused a big problem in the past when only carbon dioxide gas in pure water was targeted, but recently, organic matter contained in pure water has been produced. Or, the problem of fine particles has become apparent. For this reason, improvements in the apparatus have been made, such as filtering the air blown into the decarbonation tower to remove the fine particles in the air. However, it is difficult to sufficiently remove fine particles of 0.1 to 0.5 μm in the air with a filter. Further, by aerating the decarbonation tower with air, impurities other than fine particles in the air, such as ions,
A lot of organic substances and bacteria are mixed. These impurities are
This adversely affects the anion exchange resin column and the mixed bed column in the subsequent stage of the decarbonation column, and causes problems such as an increase in the frequency of resin regeneration and an increase in fine particles in pure water.
【0005】さらに、半導体洗浄用の純水や超純水中の
溶存ガス、特に溶存酸素は、イオン交換樹脂の酸化、各
種金属部材の腐食などの防止の観点から除去されてき
た。最近、半導体素子製造におけるSi ウエハ洗浄時に
液中に溶存酸素が存在すると、Si ウエハ表面に自然酸
化膜が形成され、高性能デバイスを製作する上での問題
点が指摘されており、純水及び超純水中の溶存酸素濃度
を数ppb 以下とする技術開発がなされている。Further, dissolved gases in pure water and ultrapure water for cleaning semiconductors, particularly dissolved oxygen, have been removed from the viewpoint of preventing oxidation of ion exchange resins and corrosion of various metal members. Recently, it has been pointed out that if dissolved oxygen is present in the liquid during Si wafer cleaning in the manufacture of semiconductor devices, a natural oxide film is formed on the surface of the Si wafer, which causes problems in manufacturing high-performance devices. Technology has been developed to reduce the dissolved oxygen concentration in ultrapure water to several ppb or less.
【0006】従来、溶存酸素除去には真空脱気法が広く
採用されてきた。この方法は、塔高10m程度の真空塔
の上部から被処理水をスプレーし、酸素分圧の低い気相
に液滴を接触させる過程で溶存酸素を除去するものであ
る。しかしながら、この方法は、真空塔内の真空レベル
によって、液中に残存する溶存酸素濃度は限界となり、
通常の限界真空レベルである20〜30 Torr では、液
中に溶存酸素が50〜100ppb 残留する。したがっ
て、この真空脱気法は性能的に問題がある。Conventionally, a vacuum degassing method has been widely adopted for removing dissolved oxygen. In this method, the water to be treated is sprayed from the upper part of a vacuum tower having a tower height of about 10 m, and the dissolved oxygen is removed in the process of bringing the droplets into contact with the gas phase having a low oxygen partial pressure. However, in this method, the concentration of dissolved oxygen remaining in the liquid becomes a limit due to the vacuum level in the vacuum tower,
At the normal limit vacuum level of 20 to 30 Torr, 50 to 100 ppb of dissolved oxygen remains in the liquid. Therefore, this vacuum degassing method has a performance problem.
【0007】これに対し、様々な液中の溶存酸素を極低
濃度にする方法が現在検討されており、その一つに液中
に窒素ガスなどの不活性ガスを通気する不活性ガス曝気
法がある。この方法は液中に窒素ガスなどの不活性ガス
を通気することによって溶存酸素を除去し、1ppb の濃
度まで溶存酸素を除去することが可能であるが、反面、
通気する不活性ガス量が比較的多量となるという欠点が
ある。On the other hand, a method of making dissolved oxygen in various liquids to an extremely low concentration is currently being studied, and one of them is an inert gas aeration method in which an inert gas such as nitrogen gas is passed through the liquid. There is. This method is capable of removing dissolved oxygen by passing an inert gas such as nitrogen gas into the liquid and removing dissolved oxygen up to a concentration of 1 ppb.
There is a drawback that the amount of inert gas to be ventilated is relatively large.
【0008】一方、一次純水システムでは、前記のよう
に、陰イオン交換塔のイオン量を低減するため、陽イオ
ン交換塔から流出する液中の炭酸イオンを除去する操作
が行われる。これが脱炭酸塔の役目であり、通常、この
塔の下部から空気を通気して液中の炭酸イオンを除去し
ている。このため、純水中の溶存酸素は、この脱炭酸塔
の出口で大気と飽和の8000〜9000ppb となり、
後段の溶存酸素除去塔に対して大きな負担となってい
る。また、前述のように、溶存酸素の存在によって陰イ
オン交換樹脂の劣化を促進するマイナス面も生じてい
る。On the other hand, in the primary pure water system, as described above, in order to reduce the amount of ions in the anion exchange column, the operation of removing carbonate ions in the liquid flowing out from the cation exchange column is performed. This is the role of the decarbonation tower, and normally, air is aerated from the lower part of the tower to remove carbonate ions in the liquid. Therefore, the dissolved oxygen in pure water becomes 8000 to 9000 ppb which is saturated with the atmosphere at the outlet of this decarbonation tower,
It is a heavy burden on the dissolved oxygen removal tower in the latter stage. In addition, as described above, the presence of dissolved oxygen has a negative effect of promoting the deterioration of the anion exchange resin.
【0009】[0009]
【発明が解決しようとする課題】本発明は、前記従来技
術の問題点を解消し、脱炭酸塔の通気口にフィルターを
用いることなく、炭酸イオンを炭酸ガスとして除去する
ための通気を行うことができ、これにより液中に微粒子
の増加及び不純物イオンの増加を起こさずに純水を製造
することができ、さらに純水中の溶存酸素を極低濃度ま
で除去しうる純水の製造方法及び装置を提供することを
目的とする。DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned problems of the prior art, and performs ventilation for removing carbonate ions as carbon dioxide gas without using a filter at the ventilation port of the decarbonation tower. By this, it is possible to produce pure water without increasing the number of fine particles and the number of impurity ions in the liquid, and a method for producing pure water capable of removing dissolved oxygen in pure water to an extremely low concentration, and The purpose is to provide a device.
【0010】[0010]
【課題を解決するための手段】本発明は、脱炭酸塔にお
いて空気曝気の代わりに不活性ガスで曝気することによ
って前記目的を達成したものである。すなわち、本発明
による純水の製造方法は、陽イオン交換樹脂塔、脱炭酸
塔及び陰イオン交換樹脂塔に順次通水することによって
純水を製造する場合、脱炭酸塔の底部から不活性ガスを
導入することを特徴とする。また、本発明による純水製
造装置は、陽イオン交換樹脂塔、脱炭酸塔及び陰イオン
交換樹脂塔を含む純水製造装置において、脱炭酸塔の底
部に不活性ガス供給装置を接続したことを特徴とする。The present invention has achieved the above object by aeration with an inert gas instead of air aeration in a decarbonation tower. That is, in the method for producing pure water according to the present invention, when pure water is produced by sequentially passing water through a cation exchange resin tower, a decarbonation tower and an anion exchange resin tower, an inert gas is supplied from the bottom of the decarbonation tower. It is characterized by introducing. The pure water producing apparatus according to the present invention is a pure water producing apparatus including a cation exchange resin tower, a decarboxylation tower and an anion exchange resin tower, and an inert gas supply device is connected to the bottom of the decarbonation tower. Characterize.
【0011】本発明においては、前記陰イオン交換樹脂
塔の後段に溶存酸素除去塔を設け、該溶存酸素除去塔の
底部に不活性ガス供給装置を接続し、該溶存酸素除去塔
の上部から排出される不活性ガスの一部又は全部を不活
性ガス配管を介して上記脱炭酸塔の底部へ導入すること
もできる。In the present invention, a dissolved oxygen removing tower is provided at the latter stage of the anion exchange resin tower, an inert gas supply device is connected to the bottom of the dissolved oxygen removing tower, and the dissolved oxygen removing tower is discharged from the upper portion thereof. It is also possible to introduce a part or all of the generated inert gas into the bottom of the decarbonation tower through an inert gas pipe.
【0012】[0012]
【実施例】図1は、本発明の一実施例を示す純水製造装
置の系統図である。図1において被処理水は、前処理装
置1を経て陽イオン交換樹脂塔2に流入する。ここで、
被処理水中に存在している各種イオンのうちNa 、Kな
どの陽イオンがイオン交換樹脂の交換基と反応して除去
される。また、このときにHイオンが水中に放出される
ため、液のpHが低下する。脱炭酸塔3ではpHの低い被処
理水を塔の上部からスプレーする被処理水導入管4及び
不活性ガス供給装置5が設置され、塔内下部の貯留水に
窒素ガスなどの不活性ガスを吹き込み、この曝気効果に
よって水中の炭酸イオンを系外に除去する。次に、陰イ
オン交換樹脂塔6では、炭酸イオン以外の陰イオンを除
去し、さらに混床塔7で残留する各種イオンを除去し、
この一連のシステムを通過することによって純水が製造
される。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 is a system diagram of a pure water producing apparatus showing an embodiment of the present invention. In FIG. 1, the water to be treated flows into the cation exchange resin tower 2 through the pretreatment device 1. here,
Of the various ions present in the water to be treated, cations such as Na and K react with the exchange groups of the ion exchange resin and are removed. Further, at this time, since H ions are released into water, the pH of the liquid is lowered. The decarbonation tower 3 is provided with a treated water introduction pipe 4 for spraying treated water having a low pH from the upper part of the tower and an inert gas supply device 5, and an inert gas such as nitrogen gas is supplied to the stored water in the lower part of the tower. Blow in and remove carbonate ions in water out of the system by this aeration effect. Next, in the anion exchange resin tower 6, anions other than carbonate ions are removed, and further various ions remaining in the mixed bed tower 7 are removed,
Pure water is produced by passing through this series of systems.
【0013】図2は、市水を原水としたときの本発明方
法及び従来方法の脱炭酸塔出口水の水質の経時変化を示
すグラフである。脱炭酸塔を空気曝気する従来方法は、
炭酸の除去効果は充分であるが、処理液中の 0.2μm以
上の微粒子数は1×105 〜5×105 個/mlと多量含
まれる。これに対し、本発明方法により不活性ガス(例
えば、窒素ガス)を従来法の空気と同量の80リットル
/分(ガス通気速度:約60m/時間)を吹き込んだ場
合には、炭酸除去性能はほぼ同程度であるが、処理液中
の微粒子数は1×104 個/ml以下であった。すなわ
ち、本発明方法によって、処理液中の微粒子数を90%
以上低減することが可能となる。この微粒子除去効果の
違いは、脱炭酸塔の次工程である陰イオン交換樹脂塔の
出口水に大きな影響を与える。FIG. 2 is a graph showing changes over time in the water quality of the decarbonation tower outlet water of the method of the present invention and the conventional method when city water is used as raw water. The conventional method of aerating the decarbonation tower is
Although the effect of removing carbonic acid is sufficient, the number of fine particles having a particle size of 0.2 μm or more in the treatment liquid is as large as 1 × 10 5 to 5 × 10 5 particles / ml. On the other hand, when an inert gas (for example, nitrogen gas) is blown by the method of the present invention at a rate of 80 liters / minute (gas aeration rate: about 60 m / hour), the carbon dioxide removal performance is the same. However, the number of fine particles in the treatment liquid was 1 × 10 4 particles / ml or less. That is, the number of fine particles in the treatment liquid is 90% by the method of the present invention.
It is possible to reduce the above. This difference in the effect of removing fine particles has a great influence on the outlet water of the anion exchange resin tower, which is the next step of the decarbonation tower.
【0014】図3は、従来方法と本発明方法を採用した
場合の陰イオン交換樹脂の出口水における微粒子濃度の
経時変化を示すグラフである。従来方法では、陰イオン
交換樹脂塔出口水の微粒子は、通水時間約12時間から
急激に増加するが、本発明方法では通常の再生サイクル
である通水時間20時間においても微粒子の流出は殆ど
ない。また、表1には、従来法と本発明方法の流出水の
有機物量、総カチオン量及び総アニオン量を示す。この
結果から、本発明方法は微粒子の他の不純物の低減に対
しても効果的であることが分かる。FIG. 3 is a graph showing changes with time in the concentration of fine particles in the outlet water of the anion exchange resin when the conventional method and the method of the present invention are adopted. In the conventional method, the fine particles of water in the outlet of the anion exchange resin tower rapidly increase from the water passage time of about 12 hours, but in the method of the present invention, the outflow of the fine particles hardly occurs even at the water passage time of 20 hours which is a normal regeneration cycle. Absent. In addition, Table 1 shows the amount of organic matter, the total amount of cations and the total amount of anions in the effluent water of the conventional method and the method of the present invention. From these results, it can be seen that the method of the present invention is effective for reducing other impurities in the fine particles.
【0015】[0015]
【表1】 [Table 1]
【0016】図4は、従来の空気を通気する脱炭酸塔を
有する純水製造装置の溶存酸素の推移を示すグラフであ
る。液中の溶存酸素は、炭酸イオンを除去するための脱
炭酸塔を通過すると急激に上昇してしまい、後段の溶存
酸素の除去装置に対して大きな負担となっていることが
分かる。FIG. 4 is a graph showing the transition of dissolved oxygen in a pure water producing apparatus having a conventional decarbonation tower through which air is passed. It can be seen that the dissolved oxygen in the liquid sharply rises when passing through the decarbonation tower for removing carbonate ions, which imposes a heavy burden on the dissolved oxygen removing device in the subsequent stage.
【0017】図5は、本発明の実施例を示す純水及び超
純水製造装置の系統図である。図5に示した装置は、主
として、凝集などの前処理装置1、活性炭塔11、2B
3Tと称される陽イオン交換樹脂塔2、脱炭酸塔3、陰
イオン交換樹脂塔6、さらに混床塔7、溶存酸素除去塔
8、超純水製造システム9及び不活性ガス供給装置5か
ら構成されている。原水である市水は、この装置を順次
通過する過程で高純度化される。この装置では、不活性
ガス供給装置5は、溶存酸素除去塔8の底部に接続さ
れ、溶存酸素除去塔8の上部から排出されるガスは、不
活性ガス配管10を介して前段の脱炭酸塔3の底部に供
給され、該脱炭酸塔3において水中の炭酸イオン及び溶
存酸素を同時に除去するように構成されている。FIG. 5 is a system diagram of an apparatus for producing pure water and ultrapure water showing an embodiment of the present invention. The apparatus shown in FIG. 5 mainly comprises a pretreatment apparatus 1 for coagulation and the like, activated carbon towers 11 and 2B.
From a cation exchange resin tower 2, a decarbonation tower 3, an anion exchange resin tower 6 called 3T, a mixed bed tower 7, a dissolved oxygen removal tower 8, an ultrapure water production system 9 and an inert gas supply device 5. It is configured. City water, which is raw water, is highly purified in the process of sequentially passing through this device. In this apparatus, the inert gas supply device 5 is connected to the bottom of the dissolved oxygen removal tower 8, and the gas discharged from the upper part of the dissolved oxygen removal tower 8 is passed through the inert gas pipe 10 to the decarbonation tower of the preceding stage. The carbon dioxide ion and the dissolved oxygen contained in the water are simultaneously removed in the decarbonation tower 3.
【0018】図5に示した装置で実施した場合の水中の
溶存酸素濃度を図4に併記した。図4から分かるよう
に、従来方法による脱炭酸を行うことにより炭酸イオン
の除去性能を低下させることなく、溶存酸素を600〜
800ppb にまで低減することができる。Dissolved oxygen concentration in water when the apparatus shown in FIG. 5 was used is also shown in FIG. As can be seen from FIG. 4, by carrying out decarboxylation according to the conventional method, it is possible to remove dissolved oxygen from 600 to 600 without deteriorating the removal performance of carbonate ions.
It can be reduced to 800 ppb.
【0019】さらに、図6は、溶存酸素除去塔8の入口
液中の溶存酸素に対する必要ガス量についてまとめたも
のであるが、被処理液中の溶存酸素を1〜3ppb にまで
除去するのに必要な窒素ガス量は、従来法では供給液量
に対して 0.8Nl/lであったのに対して、本発明方法
では 0.4Nl/lとなり、吹き込み窒素ガス量を約1/
2に低減可能であった。Further, FIG. 6 shows a summary of the amount of gas required for the dissolved oxygen in the inlet liquid of the dissolved oxygen removing tower 8, but it is possible to remove the dissolved oxygen in the liquid to be treated up to 1 to 3 ppb. The required nitrogen gas amount was 0.8 Nl / l with respect to the supply liquid amount in the conventional method, while it was 0.4 Nl / l in the method of the present invention, and the blown nitrogen gas amount was about 1 / l
It could be reduced to 2.
【0020】[0020]
【発明の効果】本発明によれば、脱炭酸塔における微粒
子をはじめとする各種不純物を効果的に低減でき、後段
の陰イオン交換樹脂塔出口水の水質を大幅に向上するこ
とができる。また、窒素ガスなどの不活性ガスを吹き込
むことによりイオン交換樹脂の劣化の原因となる液中の
溶存酸素も同時に除去することが可能となり、脱炭酸塔
の後段に設置された陰イオン交換樹脂の交換頻度を向上
でき、系内での細菌繁殖を防止できるという付随的効果
もある。さらに、溶存酸素除去塔に不活性ガスを吹き込
み、その排出ガスを脱炭酸塔へ導入する方式とすること
により、不活性ガス使用量を大幅に低減できる。According to the present invention, various impurities such as fine particles in the decarbonation tower can be effectively reduced, and the water quality of the outlet water of the anion exchange resin tower at the latter stage can be greatly improved. In addition, by blowing an inert gas such as nitrogen gas, it is possible to simultaneously remove dissolved oxygen in the liquid that causes deterioration of the ion-exchange resin. There is also an additional effect that the exchange frequency can be increased and bacterial growth in the system can be prevented. Furthermore, by using a system in which an inert gas is blown into the dissolved oxygen removal tower and the exhaust gas is introduced into the decarbonation tower, the amount of inert gas used can be greatly reduced.
【図1】本発明の一実施例を示す純水製造装置の系統図
である。FIG. 1 is a system diagram of a pure water production apparatus showing an embodiment of the present invention.
【図2】従来法及び本発明方法を実施した場合の脱炭酸
塔流出水の水質の経時変化を示すグラフである。FIG. 2 is a graph showing changes over time in the water quality of the water discharged from the decarbonation tower when the conventional method and the method of the present invention are carried out.
【図3】従来法及び本発明方法を実施した場合の陰イオ
ン交換樹脂塔からの流出水中の微粒子数の経時変化を示
すグラフである。FIG. 3 is a graph showing the change over time in the number of fine particles in the outflow water from the anion exchange resin tower when the conventional method and the method of the present invention are carried out.
【図4】従来法及び本発明方法を実施した場合の純水及
び超純水製造装置における溶存酸素の推移を示すグラフ
である。FIG. 4 is a graph showing changes in dissolved oxygen in pure water and ultrapure water production apparatuses when the conventional method and the method of the present invention are carried out.
【図5】本発明の別の実施例を示す超純水製造装置の系
統図である。FIG. 5 is a system diagram of an ultrapure water production system showing another embodiment of the present invention.
【図6】従来法及び本発明方法を実施した場合の溶存酸
素除去塔入口の溶存酸素と吹き込み窒素ガス必要量との
関係を示すグラフである。FIG. 6 is a graph showing the relationship between the dissolved oxygen at the inlet of the dissolved oxygen removing column and the required amount of nitrogen gas blown in when the conventional method and the method of the present invention are carried out.
1・・・前処理装置、2・・・陽イオン交換樹脂塔、3
・・・脱炭酸塔、4・・・処理液流入管、5・・・不活
性ガス供給装置、6・・・陰イオン交換樹脂塔、7・・
・混床塔、8・・・溶存酸素除去塔、9・・・超純水製
造システム、10・・・不活性ガス配管、11・・・活
性炭塔1 ... Pretreatment device, 2 ... Cation exchange resin tower, 3
... Decarbonation tower, 4 ... Treatment liquid inflow pipe, 5 ... Inert gas supply device, 6 ... Anion exchange resin tower, 7 ...
・ Mixed bed tower, 8 ・ ・ ・ Dissolved oxygen removal tower, 9 ・ ・ ・ Ultrapure water production system, 10 ・ ・ ・ Inert gas piping, 11 ・ ・ ・ Active carbon tower
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.5 識別記号 庁内整理番号 FI 技術表示箇所 C02F 1/42 A ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 5 Identification code Office reference number FI technical display location C02F 1/42 A
Claims (4)
オン交換樹脂塔に順次通水することによって純水を製造
する場合、脱炭酸塔の底部から不活性ガスを導入するこ
とを特徴とする純水の製造方法。1. When producing pure water by sequentially passing water through a cation exchange resin tower, a decarbonation tower and an anion exchange resin tower, an inert gas is introduced from the bottom of the decarbonation tower. A method for producing pure water.
オン交換樹脂塔を含む純水製造装置において、脱炭酸塔
の底部に不活性ガス供給装置を接続したことを特徴とす
る純水の製造装置。2. A pure water production apparatus including a cation exchange resin tower, a decarbonation tower and an anion exchange resin tower, wherein an inert gas supply device is connected to the bottom of the decarbonation tower. Manufacturing equipment.
ン交換樹脂塔及び溶存酸素除去塔に順次通水することに
よって純水を製造する場合、溶存酸素除去塔の底部に不
活性ガスを導入し、該溶存酸素除去塔の上部から排出さ
れる不活性ガスの一部又は全部を上記脱炭酸塔の底部へ
導入することを特徴とする純水の製造方法。3. When producing pure water by sequentially passing water through a cation exchange resin tower, a decarbonation tower, an anion exchange resin tower and a dissolved oxygen removal tower, an inert gas is added to the bottom of the dissolved oxygen removal tower. A method for producing pure water, characterized in that a part or all of the inert gas introduced and discharged from the upper portion of the dissolved oxygen removing tower is introduced into the bottom portion of the decarbonation tower.
ン交換樹脂塔及び溶存酸素除去塔を含む純水製造装置に
おいて、溶存酸素除去塔の底部に不活性ガス供給装置を
接続し、該溶存酸素除去塔の上部から排出される不活性
ガスの一部又は全部を上記脱炭酸塔の底部へ導入する不
活性ガス配管を設けたことを特徴とする純水の製造装
置。4. A pure water production apparatus including a cation exchange resin tower, a decarboxylation tower, an anion exchange resin tower and a dissolved oxygen removal tower, wherein an inert gas supply device is connected to the bottom of the dissolved oxygen removal tower, 1. An apparatus for producing pure water, comprising an inert gas pipe for introducing a part or all of the inert gas discharged from the upper part of the dissolved oxygen removing tower to the bottom part of the decarbonation tower.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4091907A JP3057890B2 (en) | 1992-03-17 | 1992-03-17 | Method and apparatus for producing pure water |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4091907A JP3057890B2 (en) | 1992-03-17 | 1992-03-17 | Method and apparatus for producing pure water |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH05261368A true JPH05261368A (en) | 1993-10-12 |
| JP3057890B2 JP3057890B2 (en) | 2000-07-04 |
Family
ID=14039653
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP4091907A Expired - Fee Related JP3057890B2 (en) | 1992-03-17 | 1992-03-17 | Method and apparatus for producing pure water |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3057890B2 (en) |
-
1992
- 1992-03-17 JP JP4091907A patent/JP3057890B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JP3057890B2 (en) | 2000-07-04 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| JP3426072B2 (en) | Ultrapure water production equipment | |
| JP2677468B2 (en) | Method and apparatus for producing pure water | |
| US6464867B1 (en) | Apparatus for producing water containing dissolved ozone | |
| JPH0790219B2 (en) | Pure water production apparatus and production method | |
| US20050121398A1 (en) | System and method for removing organic compounds from waste water by oxidation | |
| JPS62204892A (en) | Desalting method | |
| JPH0649190B2 (en) | High-purity water manufacturing equipment | |
| JPS62110795A (en) | High purity water production equipment | |
| JP3057890B2 (en) | Method and apparatus for producing pure water | |
| JP3238745B2 (en) | Method of treating ammonium fluoride-containing water | |
| JPS62204893A (en) | Water treatment method using granular activated carbon tower and reverse osmosis membrane apparatus | |
| JPH01284385A (en) | Pure water and ultrapure water production method and its production equipment | |
| JPH1024286A (en) | Decarbonation equipment | |
| JPH0632821B2 (en) | Method for suppressing the growth of microorganisms in pure water | |
| JP2001205297A (en) | Apparatus for producing pure water | |
| JPH07328693A (en) | Ultrapure water producing device | |
| JPH0639366A (en) | Method and equipment for producing ultrapure water | |
| JPH0938669A (en) | Method and apparatus for producing ultrapure water | |
| JP3794040B2 (en) | Purification method of hydrogen peroxide | |
| JPH0839059A (en) | Recovery method of semiconductor cleaning wastewater containing organic alkali | |
| JPS6336899A (en) | Apparatus for producing pure water | |
| JPH0780473A (en) | Method for treating acidic water containing hydrogen peroxide and surfactant | |
| JPH11290870A (en) | Treatment apparatus of ammonia-hydroperoxide mixed waste solution and treatment method using the same | |
| JPH05293494A (en) | Apparatus for producing pure water | |
| JPH0716580A (en) | Ultrapure water production method |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| S533 | Written request for registration of change of name |
Free format text: JAPANESE INTERMEDIATE CODE: R313533 |
|
| R350 | Written notification of registration of transfer |
Free format text: JAPANESE INTERMEDIATE CODE: R350 |
|
| LAPS | Cancellation because of no payment of annual fees |