JPH0221904A - High-temperature adsorption treatment device - Google Patents
High-temperature adsorption treatment deviceInfo
- Publication number
- JPH0221904A JPH0221904A JP63169025A JP16902588A JPH0221904A JP H0221904 A JPH0221904 A JP H0221904A JP 63169025 A JP63169025 A JP 63169025A JP 16902588 A JP16902588 A JP 16902588A JP H0221904 A JPH0221904 A JP H0221904A
- Authority
- JP
- Japan
- Prior art keywords
- temperature
- manganese dioxide
- sulfate
- adsorption treatment
- electrolytic manganese
- 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.)
- Pending
Links
Classifications
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M8/00—Fuel cells; Manufacture thereof
- H01M8/04—Auxiliary arrangements, e.g. for control of pressure or for circulation of fluids
- H01M8/04007—Auxiliary arrangements, e.g. for control of pressure or for circulation of fluids related to heat exchange
- H01M8/04029—Heat exchange using liquids
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/50—Fuel cells
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Manufacturing & Machinery (AREA)
- Sustainable Development (AREA)
- Sustainable Energy (AREA)
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Treatment Of Liquids With Adsorbents In General (AREA)
- Fuel Cell (AREA)
Abstract
(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
【発明の詳細な説明】
〔発明の目的〕
(産業上の利用分野)
本発明は、燃料電池の高温の冷却水中等に含まれる、配
管系統や熱交換器等から溶出した銅、鉄などの重金属腐
食生成物を捕獲する高温吸着処理装置に関する。[Detailed Description of the Invention] [Objective of the Invention] (Industrial Application Field) The present invention is directed to the treatment of copper, iron, etc. eluted from piping systems, heat exchangers, etc. contained in high-temperature cooling water of fuel cells. This invention relates to a high temperature adsorption treatment device for capturing heavy metal corrosion products.
(従来の技術)
燃料電池は水素と酸素とを反応器内で触媒を使って緩か
に反応させ、これによって電気を発生させるものであり
、燃料となる水素と酸素の化学エネルギが直接電気エネ
ルギに変換されるので、他の発電方式より高効率である
。(Prior art) A fuel cell generates electricity by causing hydrogen and oxygen to slowly react in a reactor using a catalyst, and the chemical energy of the hydrogen and oxygen used as fuel is directly converted into electrical energy. It is more efficient than other power generation methods.
この場合、水素と酸素との反応によって水を生成しなが
ら発電が行なわれるが、同時に熱も発生するので高い発
電効率を維持するためには反応容器内の温度を160〜
230℃に保つ必要があり、常時冷却水を反応器中に流
している。この冷却水は反応器内の温度より5〜10℃
低いものを使用する。In this case, electricity is generated while producing water through the reaction between hydrogen and oxygen, but at the same time heat is also generated, so in order to maintain high power generation efficiency, the temperature inside the reaction vessel must be kept at 160-160℃.
It is necessary to maintain the temperature at 230°C, and cooling water is constantly flowing into the reactor. This cooling water is 5 to 10 degrees Celsius higher than the temperature inside the reactor.
Use a low one.
すなわち、150〜225℃という高温である。冷却水
中には冷却管および他の配管の内壁、継手、タンク、熱
交換器等から銅または鉄等の重金属腐食生成物が溶出す
る。また、冷却管およびその継手部分には燃料電池の構
造上、電位が加わっており、腐食を促進するうえに、重
金属腐食生成物をイ・」着または堆積させやすい。この
冷却水は循環流路を流れており、長時間処理を継続する
と付着や堆積が進行して冷却管やその継手の一部が閉塞
し、反応器内の温度分布が不均一となり、発電効率を低
下させ、電池の寿命を短かくする。That is, it is a high temperature of 150 to 225°C. Corrosion products of heavy metals such as copper or iron are leached into the cooling water from the inner walls of cooling pipes and other piping, joints, tanks, heat exchangers, etc. Further, due to the structure of the fuel cell, a potential is applied to the cooling pipes and their joints, which not only accelerates corrosion but also tends to cause heavy metal corrosion products to attach or accumulate. This cooling water flows through a circulation channel, and if the treatment continues for a long time, adhesion and deposition will progress, clogging some of the cooling pipes and their joints, making the temperature distribution inside the reactor uneven, and reducing the power generation efficiency. and shorten battery life.
この冷却管と継手への重金属腐食生成物の付着と堆積を
抑制するためには冷却水水質を高純度に維持する必要が
ある。従来はこの冷却水の一部を循環系から取り出し、
熱交換器(冷却器)で40〜60℃に降温した後にイオ
ン交換樹脂で低温浄化していた。In order to suppress the adhesion and accumulation of heavy metal corrosion products to the cooling pipes and joints, it is necessary to maintain the quality of the cooling water at a high purity. Conventionally, some of this cooling water was taken out of the circulation system,
After the temperature was lowered to 40 to 60°C using a heat exchanger (cooler), low-temperature purification was performed using an ion exchange resin.
しかし、イオン交換樹脂による低温浄化はエネルギロス
が大きいため、この量を、循環している冷却水量の10
%以上とするのは実用的ではなく、十分な浄化ができな
かった。従って、高温状態の冷却水中の重金属腐食生成
物を除去できることが要望されている。However, low-temperature purification using ion exchange resin causes a large energy loss, so this amount is reduced to 10% of the amount of circulating cooling water.
% or more was not practical and could not achieve sufficient purification. Therefore, it is desired to be able to remove heavy metal corrosion products from cooling water at high temperatures.
本発明者らは、この処理に適用できる高温吸着ろ材とし
て、二酸化マンガンが最適であることを実験により確認
している。この二酸化マンガン吸着ろ材としては電解で
生成させた電解二酸化マンガンが適していることも確認
した。The present inventors have confirmed through experiments that manganese dioxide is optimal as a high-temperature adsorption filter material that can be applied to this treatment. It was also confirmed that electrolytic manganese dioxide produced by electrolysis is suitable as this manganese dioxide adsorption filter material.
(発明が解決しようとする課題)
しかし、この電解二酸化マンガンは硫酸マンガンの電解
で生成するため、 そのブロック中に1.5%以下(平
均1%)の硫酸塩を含有している。この電解二酸化マン
ガン中の硫酸塩は、燃料電池の冷却水のような高温水(
150〜225℃)中では溶出し硫酸H2SO4となる
。硫酸が冷却水に溶出すると配管、継手、タンク等を腐
食するため、硫酸塩を完全に除去して使用しなければな
らない。(Problem to be Solved by the Invention) However, since this electrolytic manganese dioxide is produced by electrolysis of manganese sulfate, the block contains 1.5% or less (average 1%) of sulfate. The sulfate in this electrolytic manganese dioxide is absorbed by high-temperature water (such as fuel cell cooling water).
(150-225°C), it is eluted to become sulfuric acid H2SO4. If sulfuric acid is eluted into cooling water, it will corrode piping, fittings, tanks, etc., so sulfate must be completely removed before use.
本発明の目的は硫酸塩を完全に除去した後に電解二酸化
マンガンを高温吸着ろ材として使用して溶出硫酸塩によ
る腐食を防止した高温吸着装置を提供することにある。An object of the present invention is to provide a high-temperature adsorption device that uses electrolytic manganese dioxide as a high-temperature adsorption filter material after completely removing sulfates to prevent corrosion caused by eluted sulfates.
(課題を解決するための手段)
本発明による高温吸着処理装置は、吸着ろ材として、高
温純水を流通させて硫酸塩を溶出させた電解二酸化マン
ガンを用いている。(Means for Solving the Problems) The high-temperature adsorption treatment apparatus according to the present invention uses electrolytic manganese dioxide in which sulfate is eluted by flowing high-temperature pure water as an adsorption filter medium.
(作用)
本発明では、吸着ろ材として硫酸塩を除去した電解二酸
化マンガンを用いたので、高温の被処理水中に硫酸塩が
溶出し、硫酸となって各部を腐食することはなく、被処
理水中に含まれる重金属を吸着処理することができる。(Function) In the present invention, electrolytic manganese dioxide from which sulfates have been removed is used as an adsorption filter material, so sulfates do not elute into the high-temperature water to be treated, become sulfuric acid, and corrode various parts. It is possible to adsorb and treat heavy metals contained in
(実施例)
始めに、電解二酸化マンガンからの硫酸塩の除去につい
て検討した結果を説明する。実験では100℃、150
°C,200°Cの各純水に対する硫酸の溶出を検証し
た。その結果を第2図に示す。第2図から、100℃純
水に対して電解二酸化マンガン中の硫酸塩は溶出する。(Example) First, the results of a study on the removal of sulfate from electrolytic manganese dioxide will be explained. In the experiment, the temperature was 100℃ and 150℃.
The elution of sulfuric acid with respect to each type of pure water at °C and 200 °C was verified. The results are shown in FIG. From FIG. 2, sulfate in electrolytic manganese dioxide is eluted in pure water at 100°C.
この溶出量は時間の経過とともに減少し、遂には溶出し
なくなることを確認した。次に、100℃で処理済の電
解二酸化マンガンを150℃の純水中に浸漬したところ
、硫酸塩の溶出は起こらなかった。 しかし、200℃
の純水に対しては硫酸塩が再び溶出することが確認され
た。It was confirmed that this elution amount decreased over time and finally stopped elution. Next, when the electrolytic manganese dioxide treated at 100°C was immersed in pure water at 150°C, no sulfate elution occurred. However, 200℃
It was confirmed that sulfate was eluted again in pure water.
このことは、電解二酸化マンガン中の硫酸塩は100℃
の純水で溶出するが、全量は溶出せず、残りの硫酸塩は
200℃程度の純水で溶出することを表わす。This means that the sulfate in electrolytic manganese dioxide is
However, the entire amount is not eluted, and the remaining sulfate is eluted with pure water at about 200°C.
以上の結果を検討した結果、本発明者らは電解二酸化マ
ンガンからの硫酸塩を除去するための好ましい例として
、100℃の純水中で硫酸塩を可能なだけ溶出させた後
に200℃以上の純水中で残りを溶出させることを提供
する。なお、最初から最後まで200℃以上の純水中で
溶出させることもできるが、高温、高圧である等、設備
にかかるコストも大幅に上昇し、100℃の純水での処
理に比較するとエネルギロスが大きく得策ではない。As a result of studying the above results, the present inventors found that as a preferable example for removing sulfate from electrolytic manganese dioxide, after eluting as much of the sulfate as possible in pure water at 100°C, the Provide for elution of the remainder in pure water. Although elution can be carried out in pure water at 200°C or higher from start to finish, the high temperature and pressure required will significantly increase equipment costs and require less energy compared to treatment with 100°C pure water. Loss is not a great idea.
以下本発明の一実施例を第1図に示す。1は反応器で、
内蔵された冷却管2の出口側は気液分離器3に接続され
る。この気液分離器3からの冷却水出口配管4は循環ポ
ンプ5に接続し、さらに、開閉弁6を介して高温吸着処
理塔7に接続する。An embodiment of the present invention is shown in FIG. 1 below. 1 is a reactor,
The outlet side of the built-in cooling pipe 2 is connected to a gas-liquid separator 3. A cooling water outlet pipe 4 from the gas-liquid separator 3 is connected to a circulation pump 5 and further connected to a high-temperature adsorption treatment tower 7 via an on-off valve 6.
この高温吸着処理塔7内は、電解二酸化マンガンを高温
吸着ろ材として収容している。高温吸着処理塔7の出口
配管8は開閉弁9を介して冷却4W2人口に接続してお
り、これによって冷却水の循環系を形成する。また前記
冷却水出口配管4は分岐してあり、分岐例は開閉弁lO
を介して冷却器11に接続した後、イオン交換樹脂等か
らなる低温浄化器12に接続する。低温浄化器12の出
口配管13はボンプ14とヒーター15を経て気液分離
器3に接続する。また、高温吸着塔7の出口配管8も分
岐しており、分岐側は開閉弁16を介して冷却器17に
接続する。この冷却器17の出口配管18はイオン交換
樹脂等からる浄化器19に接続し、さらにその出口配管
20はポンプ24.ヒーター21.開閉弁22を経て高
温吸着塔7の入口配管23に接続する。This high-temperature adsorption treatment tower 7 contains electrolytic manganese dioxide as a high-temperature adsorption filter material. The outlet pipe 8 of the high-temperature adsorption treatment tower 7 is connected to the cooling 4W2 population via an on-off valve 9, thereby forming a cooling water circulation system. Further, the cooling water outlet pipe 4 is branched, and an example of the branch is an on-off valve lO.
After connecting to a cooler 11 via a cooler 11, it is connected to a low temperature purifier 12 made of ion exchange resin or the like. An outlet pipe 13 of the low temperature purifier 12 is connected to the gas-liquid separator 3 via a pump 14 and a heater 15. Further, the outlet pipe 8 of the high temperature adsorption tower 7 is also branched, and the branch side is connected to a cooler 17 via an on-off valve 16. The outlet pipe 18 of this cooler 17 is connected to a purifier 19 made of ion exchange resin or the like, and the outlet pipe 20 is connected to a pump 24. Heater 21. It is connected to the inlet pipe 23 of the high temperature adsorption tower 7 via the on-off valve 22.
上記構成において、運転時は開閉弁6,9.10を開き
、開閉弁16.22を閉じる。反応器1内の冷却管2を
通り、気液分離器3および各種配管を通り、それらから
発生した重金属腐食生成物を含む冷却水は、循環ポンプ
5により高温吸着処理塔7に送りこまれる。高温吸着処
理塔7内には、これらの重金属腐食生成物を吸着処理す
る電解二酸化マンガンを収容している。この電解二酸化
マンガンは燃料電池の冷却水のような高温熱中の重金属
を極めて効率よく吸着することを確認している。In the above configuration, during operation, the on-off valves 6, 9.10 are opened and the on-off valve 16.22 is closed. Cooling water containing heavy metal corrosion products generated therefrom passes through the cooling pipe 2 in the reactor 1, the gas-liquid separator 3, and various piping, and is sent to the high-temperature adsorption treatment tower 7 by the circulation pump 5. The high temperature adsorption treatment tower 7 contains electrolytic manganese dioxide for adsorption treatment of these heavy metal corrosion products. It has been confirmed that this electrolytic manganese dioxide adsorbs heavy metals in high-temperature heat such as fuel cell cooling water extremely efficiently.
なお、この電解二酸化マンガンは重金属以外のもの、例
えばcQ−,5ob−等の陰イオンは吸着できないため
、低温浄化も必要となる。すなわち、循環系内の冷却水
の一部を開閉弁10から取出して冷却器11へ送り、4
0〜60℃に降温した後、イオン交換樹脂等の低温浄化
器12により処理する。この処理液はポンプ14で加圧
され、ヒーター15で昇温された後に気液分離器3に戻
される。Note that this electrolytic manganese dioxide cannot adsorb anything other than heavy metals, for example, anions such as cQ-, 5ob-, etc., so low-temperature purification is also required. That is, a part of the cooling water in the circulation system is taken out from the on-off valve 10 and sent to the cooler 11.
After the temperature is lowered to 0 to 60°C, treatment is performed using a low-temperature purifier 12 such as an ion exchange resin. This treated liquid is pressurized by a pump 14 and heated by a heater 15, and then returned to the gas-liquid separator 3.
ここで、電解二酸化マンガンは硫酸塩を含有しているた
め、上述した冷却水中の重金属腐食生成物の高温吸着処
理を行なう前処理として、以下に示す硫酸塩の除去を行
なう。開閉弁6,9.10を閉じ、開閉弁16.22を
開き、浄化器19でイオン交換処理した純水をポンプ2
4で加圧し、さらにヒーター21で100℃に昇温した
後、開閉弁22を通し入口配管23から高温吸着処理塔
7に供給する(第1ステツプ)。高温吸着処理塔7では
純水に対し電解二酸化マンガンから硫酸塩が溶出する。Here, since electrolytic manganese dioxide contains sulfate, the following sulfate removal is performed as a pretreatment for performing the high-temperature adsorption treatment of heavy metal corrosion products in the cooling water. The on-off valves 6 and 9.10 are closed, the on-off valve 16.22 is opened, and the purified water that has been ion-exchanged in the purifier 19 is pumped into the pump 2.
After pressurizing at step 4 and further raising the temperature to 100° C. using heater 21, it is supplied to high-temperature adsorption treatment tower 7 through inlet pipe 23 through on-off valve 22 (first step). In the high-temperature adsorption treatment tower 7, sulfate is eluted from electrolytic manganese dioxide with respect to pure water.
ただし、純水を通すため電解二酸化マンガンの吸着容量
を減少させることはない。硫酸が溶出した純水は出口配
管8.開閉弁16を通り、冷却器17に流れ、ここで4
0〜60℃に降温された後、浄化器19で浄化される。However, since pure water passes through it, the adsorption capacity of electrolytic manganese dioxide is not reduced. The pure water from which sulfuric acid has been eluted is sent to the outlet pipe 8. It passes through the on-off valve 16 and flows to the cooler 17, where 4
After the temperature is lowered to 0 to 60°C, it is purified in a purifier 19.
このような循環系で処理を続け、100℃の純水への
硫酸の溶出がなくなった時点で、純粋をヒーター21に
より200℃まで昇温する(第2ステツプ)。この20
0℃の純水を高温吸着処理塔7に流すと、100℃の純
水中には溶出しなかった硫酸塩が、再び電解二酸化マン
ガンから溶出する。The treatment is continued in such a circulation system, and when sulfuric acid is no longer eluted into the 100°C pure water, the temperature of the pure water is raised to 200°C using the heater 21 (second step). These 20
When pure water at 0°C is passed through the high-temperature adsorption treatment tower 7, the sulfate that was not eluted into the pure water at 100°C is eluted from the electrolytic manganese dioxide again.
このように前処理により硫酸塩を除去した電解二酸化マ
ンガンを高温吸着ろ材として使用するため、硫酸溶出に
よる配管、タンク、継手等の腐食を抑制できる。また、
硫酸塩の除去を、第1ステツプとして100℃で行ない
、第2ステツプとして200℃で行なうため、200℃
で一貫して実施するよりも昇温、降温によるエネルギロ
スを少なくできる。Since electrolytic manganese dioxide from which sulfates have been removed through pretreatment is used as a high-temperature adsorption filter material, corrosion of piping, tanks, joints, etc. due to sulfuric acid elution can be suppressed. Also,
Since the sulfate removal was carried out at 100°C as a first step and at 200°C as a second step,
Energy loss due to temperature rise and fall can be reduced compared to consistent implementation.
上記の実施例では冷却水中の重金属腐食生成物の除去を
行なう高温処理装置部と、電解二酸化マンガン中の硫酸
塩の除去を行なう前処理装置部とを一体としているが、
両者を分離し、前処理装置で硫酸塩を除去した電解二酸
化マンガンを高温吸着処理装置に充填してもよい。この
場合は前処理に伴なう装置の休止時間が短くなる。In the above embodiment, the high temperature treatment unit that removes heavy metal corrosion products in cooling water and the pretreatment unit that removes sulfate from electrolytic manganese dioxide are integrated.
The two may be separated and the electrolytic manganese dioxide from which sulfate has been removed in a pretreatment device may be charged into a high-temperature adsorption treatment device. In this case, the down time of the apparatus associated with pre-processing is shortened.
また、上記のように前処理装置と高温吸着処理装置に分
離し、更に前処理装置を100℃での前処理装置と20
0℃での前処理装置とに別けてもよい。In addition, as mentioned above, the pretreatment device and the high temperature adsorption treatment device are separated, and the pretreatment device is further divided into the pretreatment device at 100°C and the high temperature adsorption treatment device.
It may be separated into a pretreatment device at 0°C.
100℃の装置は常圧のため装置がシンプルなうえに操
作性にも優れている。200℃の処理は高温。The 100°C device uses normal pressure, so it is simple and has excellent operability. Processing at 200℃ is a high temperature.
高圧に耐える装置が必要なため、多量の電解二酸化マン
ガンを前処理するには、100℃と200℃の処理装置
を別けるのが価格、処理時間、操作性から優れている。Since equipment that can withstand high pressure is required, in order to pre-treat a large amount of electrolytic manganese dioxide, it is better to use separate processing equipment for 100°C and 200°C in terms of cost, processing time, and operability.
前記の実施例では第1ステツプを100℃の純水で行な
うとしたが、100℃以下の純水でもよい。In the above embodiment, the first step was performed using pure water at 100°C, but pure water at 100°C or lower may be used.
ただし、常温(最大40℃程度)の純水では硫酸塩が溶
出しないので、60℃程度以上には昇温する必要がある
。もちろん純水の温度が低ければ、その全処理に長時間
を必要とする。また、第2ステツプも200℃の純水に
限定されず、160〜300℃でもよい。すなわち、第
1ステツプ経過後の二酸化マンガンに150℃以下の純
水を供給しても硫酸塩の溶出はほとんど生じないが、1
60℃〜190℃程度の純水に対しては硫酸塩の溶出が
急激に増大する。However, since sulfate does not elute with pure water at room temperature (up to about 40°C), it is necessary to raise the temperature to about 60°C or higher. Of course, if the temperature of the pure water is low, the entire process will take a long time. Furthermore, the second step is not limited to pure water at 200°C, but may also be from 160 to 300°C. In other words, even if pure water of 150°C or lower is supplied to manganese dioxide after the first step, almost no sulfate elution occurs;
For pure water at about 60°C to 190°C, the elution of sulfate increases rapidly.
もちろん純水温度が高いほど硫酸塩の溶出は活発になる
が、300°C以上になると二酸化マンガン自体が変質
する可能性があり、上記範囲に定めた。Of course, the higher the pure water temperature, the more active the sulfate elution becomes, but if the temperature exceeds 300°C, there is a possibility that the manganese dioxide itself will change in quality, so the temperature was set within the above range.
これらの値は発明者が実験により確認している。These values have been confirmed by the inventor through experiments.
上記温度範囲のいずれを採用するかは処理時間と効率を
検討し決定すべきである。Which of the above temperature ranges to adopt should be determined by considering processing time and efficiency.
前記実施例では高温吸着処理塔を一塔としたが、これを
二基にして一塔で冷却水の高温吸着処理を行ない、他の
一塔では電解二酸化マンガンの前処理を行なうようにし
てもよい。この場合、高温処理性能が低下した場合は前
処理を終で待機していた塔と切換えることで常に連続的
に処理できる。In the above example, one high-temperature adsorption treatment tower was used, but it is also possible to use two towers, one tower performing high-temperature adsorption treatment of cooling water, and the other tower performing pretreatment of electrolytic manganese dioxide. good. In this case, if the high-temperature treatment performance deteriorates, continuous treatment can always be achieved by switching to the column that was on standby at the end of the pretreatment.
以上説明したように、本発明によれば、前処理として電
解二酸化マンガンに含有されている硫酸塩を除去したの
で、溶出した硫酸による配管、継手、タンク等の腐食を
防止することができる。4゜As explained above, according to the present invention, since the sulfate contained in the electrolytic manganese dioxide is removed as a pretreatment, it is possible to prevent corrosion of pipes, joints, tanks, etc. due to eluted sulfuric acid. 4゜
【図面の簡単な説明】
第1図は本発明による高温吸着処理装置の一実施例を示
す系統図、第2図は電解二酸化マンガンに含有される硫
酸塩の処理時間と溶出濃度の関係の一例を示す説明図で
ある。
1・・・反応器 2・・・冷却管3・気液分離
器 4・・・冷却水出口配管5・・・循環ポンプ
6 、9.10,16.22・・開閉弁7・・・高温
吸着処理塔 8・・・出口配管11.17・・冷却器
12・・・低温浄化器13・・・出口配管
14.24・・・ポンプ15.21・・ヒータ
18・・・出口配管19・・・浄化器 20・
・・出口配管23・・・入口配管
代理人 弁理士 則 近 憲 佑
同 第子丸 健
C−dJ〕9gイ迦ポ犀言([Brief Description of the Drawings] Figure 1 is a system diagram showing an embodiment of the high temperature adsorption treatment apparatus according to the present invention, and Figure 2 is an example of the relationship between treatment time and elution concentration of sulfate contained in electrolytic manganese dioxide. FIG. 1... Reactor 2... Cooling pipe 3, gas-liquid separator 4... Cooling water outlet piping 5... Circulation pump
6, 9.10, 16.22...Opening/closing valve 7...High temperature adsorption treatment tower 8...Outlet piping 11.17...Cooler
12...Low temperature purifier 13...Outlet piping
14.24...Pump 15.21...Heater
18... Outlet piping 19... Purifier 20.
...Outlet piping 23...Inlet piping agent Patent attorney Nori Ken Yudo Daishimaru Ken C-dJ〕9g Ikapo Saiko (
Claims (1)
処理塔を設け、被処理水中の銅、鉄などの重金属腐食生
成物を除去する高温吸着処理装置において、 前記吸着ろ材として、高温純水を流通させて硫酸塩を溶
出させた電解二酸化マンガンを用いたことを特徴とする
高温吸着処理装置。[Claims] In a high-temperature adsorption treatment device that removes heavy metal corrosion products such as copper and iron from the water to be treated, a high-temperature adsorption treatment tower containing an adsorption filter medium is provided in a flow path of high-temperature water to be treated, A high-temperature adsorption treatment apparatus characterized in that the adsorption filter medium is electrolytic manganese dioxide in which sulfate is eluted by flowing high-temperature pure water.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63169025A JPH0221904A (en) | 1988-07-08 | 1988-07-08 | High-temperature adsorption treatment device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63169025A JPH0221904A (en) | 1988-07-08 | 1988-07-08 | High-temperature adsorption treatment device |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0221904A true JPH0221904A (en) | 1990-01-24 |
Family
ID=15878930
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP63169025A Pending JPH0221904A (en) | 1988-07-08 | 1988-07-08 | High-temperature adsorption treatment device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0221904A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2008135271A (en) * | 2006-11-28 | 2008-06-12 | Kyocera Corp | Fuel cell device |
| JP2021094521A (en) * | 2019-12-17 | 2021-06-24 | 株式会社東芝 | High temperature water purification device and high temperature water purification method |
-
1988
- 1988-07-08 JP JP63169025A patent/JPH0221904A/en active Pending
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2008135271A (en) * | 2006-11-28 | 2008-06-12 | Kyocera Corp | Fuel cell device |
| JP2021094521A (en) * | 2019-12-17 | 2021-06-24 | 株式会社東芝 | High temperature water purification device and high temperature water purification method |
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