WO2016076409A1

WO2016076409A1 - Method for operating regenerative ion exchange device

Info

Publication number: WO2016076409A1
Application number: PCT/JP2015/081934
Authority: WO
Inventors: 洋一宮▲崎▼
Original assignee: 栗田工業株式会社
Priority date: 2014-11-13
Filing date: 2015-11-13
Publication date: 2016-05-19
Also published as: JP2016093779A; JP6015737B2

Abstract

Provided is a method for operating a regenerative ion exchange device in which raw water is used for cleaning after regeneration of an ion exchange resin, and excellent post-regeneration water quality is obtained. In the ion exchange device, a cation exchange resin 31 is contained in one of a first chamber 30 and a second chamber 20, and an anion exchange resin 21 is contained in the other of the first chamber 30 and the second chamber 20. The first chamber 30 and the second chamber 20 are made to communicate with each other by communication means 5, 8, 11. This method for operating an ion exchange device is provided with: a water collection step for sequentially passing raw water through the first chamber 30, the communication means, and the second chamber 20; a regeneration step for regenerating the cation exchange resin 31 and the anion exchange resin 21; a first cleaning step for passing raw water as an upward flow through the second chamber 20 and cleaning the resin in the second chamber 20 after the regeneration step; and a second cleaning step for passing raw water as an upward flow through the first chamber 30 and cleaning the resin in the first chamber 30 after the first cleaning step, feeding the cleaning waste water from the first chamber 30 though the communication means to the second chamber 20 and passing the cleaning waste water as an upward flow, and cleaning the resin in the second chamber 20.

Description

Operation method of regenerative ion exchanger

TECHNICAL FIELD The present invention relates to a method for operating a regenerative ion exchange apparatus including an anion exchange resin and a cation exchange resin, and in particular, an ion exchange apparatus in which ion exchange resin cleaning after regeneration of the ion exchange apparatus is performed with raw water. It relates to the driving method.

Ion exchange devices are widely used in pure water and ultrapure water production facilities in the electronics industry. As this ion exchange device, Japanese Patent Application Laid-Open No. 2011-72927 and Japanese Patent Application Laid-Open No. 2012-205993 divide the inside of the tower into two upper and lower chambers by a water-shielding partition plate, and one chamber is filled with an anion exchange resin. The other chamber is filled with a cation exchange resin, and the upper chamber and the lower chamber are communicated with each other by a communication means routed outside the tower (Double Bed Polisher, hereinafter abbreviated as DBP). Is described).

In this DBP, an acid solution or an alkali solution is separately supplied to each chamber during the regeneration of the ion exchange resin. Therefore, the cation exchange resin and the anion exchange resin are not mixed, and the partition plate that partitions both chambers is water-blocking, and the acid or alkali supplied to one chamber passes through the partition plate and the other The reverse regeneration is prevented without flowing into the chamber. After completion of the regeneration, pure water is passed through each chamber instead of the acid solution and the alkali solution, and each path and resin are washed. Regenerated chemicals are accumulated between the inert resins packed in the upper part of the tower, and in order to stir and wash them, washing is performed in a downward flow.

Conventionally, pure water having a higher purity than DBP-treated water, for example, UF brine water of a subsystem, has been used as the pure water passed through each chamber in the cleaning process. This is to prevent contamination of the upper ion exchange resin on the treated water side during sampling when the washing is performed in a downward flow. When DBP raw water is used as the wash water in the downflow, the ion exchange resin on the treated water side is contaminated by ions contained in the raw water, resulting in a decrease in the quality of the reached water and deterioration of the water quality at the beginning of water collection after regeneration. Occur. For this reason, DBP uses high-purity water as cleaning water, and it is necessary to provide a water tank for storing the high-purity cleaning water.

On the other hand, in a mixed bed type ion exchange apparatus having a mixed ion exchange resin layer in which a strongly acidic cation exchange resin and a strongly basic anion exchange resin are mixed, regeneration is often performed using water in a raw water tank. Therefore, in DBP, the necessity of a water tank for storing high-purity cleaning water has led to an increase in cost, which is disadvantageous for the expansion of DBP application.

JP 2011-72927 A JP 2012-205993 A

The present invention has been made in view of the above-described conventional situation, and uses a raw water for washing after regeneration of an anion exchange resin and a cation exchange resin, and a regenerative ion exchange apparatus in which the water quality after regeneration is good. It is an object to provide a driving method.

The operation method of the regenerative ion exchange apparatus according to the present invention includes a first chamber and a second chamber each containing an ion exchange resin, the cation exchange resin being stored in one of the first chamber and the second chamber, An operation method of a regenerative ion exchange apparatus in which an anion exchange resin is accommodated and the first chamber and the second chamber are communicated with each other by a communicating means, in the order of the first chamber, the communicating means, and the second chamber A regenerative ion exchange apparatus comprising: a water collection step for passing raw water; a regeneration step for regenerating the cation exchange resin and the anion exchange resin; and a washing step for washing the cation exchange resin and the anion exchange resin. In the operation method, in the water sampling step, raw water is passed through the first chamber and the second chamber in an upward flow, and in the washing step, raw water is passed through the first chamber in an upward flow, The resin in the first chamber is washed, and the washing waste water is discharged from the first chamber. A first cleaning step, and after the first cleaning step, raw water is passed through the first chamber in an upward flow to clean the resin in the first chamber, and the waste water in the first chamber is discharged to the communication means. A second cleaning step of supplying the second chamber to the second chamber and passing the cleaning wastewater through the second chamber in an upward flow to clean the resin in the second chamber.

In the present invention, the supply of raw water to the first chamber is continued between the first cleaning step and the second cleaning step, and the cleaning waste water flowing out from the first chamber is guided to the second chamber. It is preferable to shift to the second cleaning step by switching the communication means.

In the present invention, after the second cleaning step, it is preferable to return to the water sampling step while continuously passing raw water through the first chamber.

In the regeneration step, it is preferable to pass the regeneration solution in a downward flow in the first chamber and the second chamber.

In the present invention, in the second cleaning step, at least a part of the cleaning waste water in the second chamber may be discharged from an extraction pipe provided at the top.

According to the present invention, raw water is used for washing after regeneration of the anion exchange resin and the cation exchange resin. In the present invention, at the beginning of the cleaning process (first cleaning process), raw water is circulated upward into the first chamber, and this cleaning wastewater is discharged out of the system. If the regenerative chemical component in the cleaning wastewater from the first cleaning step is reduced, the process proceeds to the second cleaning step, and the cleaning wastewater from the first chamber is circulated upwardly into the second chamber for cleaning. Drain the waste water from the system.

The regenerative drug component adhering to the ion exchange resin in the first chamber is removed in the first cleaning step and discharged out of the system, so that the regenerative drug component flows from the first chamber into the upper chamber in the second cleaning step. There is no.

When the first chamber is filled with a cation exchange resin, cations in the wash water (raw water) are adsorbed on the lower cation exchange resin in the first chamber in the first and second cleaning steps. Since the cation exchange capacity of the entire cation exchange resin is large, the adsorption does not proceed to the upper cation exchange resin in the first chamber. Therefore, the cation concentration in the first chamber effluent after resuming water sampling is sufficiently low. Similarly, when the anion exchange resin is filled in the first chamber, the anion concentration in the first chamber effluent after resuming the sampling is sufficiently low.

In the second washing step, the first chamber effluent is circulated upward into the second chamber, and the regenerated chemical component adhering to the ion exchange resin in the second chamber is removed. When the first chamber is filled with the cation exchange resin and the second chamber is filled with the anion exchange resin, the anion in the first chamber effluent is adsorbed to the lower anion exchange resin in the second chamber. Since the anion exchange capacity of the whole anion exchange resin is large, the adsorption does not proceed to the upper anion exchange resin. Therefore, the anion concentration in the second chamber effluent (treated water) after resuming water sampling is sufficiently low. Similarly, when the first chamber is filled with an anion exchange resin and the second chamber is filled with a cation exchange resin, the cation concentration in the second chamber effluent (treated water) after resuming water sampling is sufficiently low. It will be a thing.

Thus, even when raw water is used as the washing water in the washing step after regeneration, the quality of the treated water is improved immediately after resuming the sampling.

Also, since raw water is used for cleaning after regeneration, there is no need to provide a water tank for storing cleaning water made of high-purity pure water or the like, and costs can be reduced.

In the present invention, when the cleaning water flows upward in the first and second cleaning steps, the ion exchange resin floats in the first chamber and the second chamber to form a fixed bed made of a floating layer. Therefore, when shifting from the first cleaning step to the second cleaning step, the flow of the raw water to the first chamber is continued without stopping, and the first chamber effluent is caused to flow into the second chamber by the communication means. It is preferable to start the second cleaning step. As described above, when the upward flow of raw water is continued and the process proceeds from the first cleaning step to the second cleaning step, the fixed bed (floating layer) of the ion exchange resin formed in the first chamber in the first cleaning step collapses. Without being performed, the second cleaning step is also maintained.

Furthermore, when the sampling process is shifted from the second washing process to the sampling process, if the sampling of the raw water is started without stopping, the fixed bed (floating layer) of the ion exchange resin collapses. And maintain the flying state. Thus, if the ion exchange resin fixed bed formed in the washing process continues as it is to the water sampling process, the adsorption zone is not disturbed, and treated water with good water quality can be collected.

In addition, when the upward circulating water is stopped in a state where the fixed bed floating in the room is formed by the upward circulating water, the ion exchange resin settles down sequentially from the lower part of the fixed bed. At this time, the ion exchange resin is agitated, and a part of the cation exchange resin (or anion exchange resin having a large cation adsorption amount) located relatively lower moves to the upper part of the ion exchange resin bed. Therefore, the treated water chamber may be deteriorated early in the water sampling process after resuming water sampling.

As described above, by continuing the upward circulation water of the raw water without stopping in the first washing process, the second washing process, and the water sampling process, there is no collapse of the fixed bed during this period, and the processing of the water sampling process Water quality will be good over a long period of time.

When the upward circulation water is used in the water sampling process and the washing process, it is preferable that the regenerative medicine is distributed downward in the regeneration process. When the regenerative drug is flowed downward, the upper part of the ion exchange resin bed is sufficiently regenerated, so at the start of the water sampling process with the upward flow of water, the ion exchange resin has a higher ion exchange capacity as the upper part of the ion exchange resin bed. Will exist. In the water sampling step, when raw water is circulated upward in the ion exchange resin bed, the quality of the treated water is improved and the amount of water that can be collected increases.

FIG. 1a shows a water sampling process of the ion exchange apparatus according to the embodiment, and FIG. 1b is a schematic cross-sectional view showing a regeneration process. 2a and 2b are schematic sectional views showing a cleaning process of the ion exchange apparatus according to the embodiment. It is a schematic sectional drawing which shows the ion exchange apparatus which concerns on another embodiment. 4a and 4b are explanatory diagrams of Experimental Examples 1 to 3. FIG. 6 is a graph showing the results of Experimental Examples 1 to 3. It is a graph which shows the result of an Example and a comparative example. 7a and 7b are explanatory diagrams of comparative examples 1 and 2. FIG.

Hereinafter, embodiments will be described with reference to FIGS. 1 and 2.

The tower 1 of the ion exchange apparatus has an outer shell made up of a cylindrical portion 1a whose vertical direction is the cylinder axis direction, a top end plate portion 1b, and a bottom end plate portion 1c. The end plate portion 1b is convexly curved upward, and the end plate portion 1c is convexly curved downward.

The inside of the tower body 1 is divided into two chambers, an upper chamber 20 and a lower chamber 30, by a water shielding partition plate 2. In this embodiment, the partition plate 2 is made of metal or synthetic resin that does not allow water to pass through at all, and is curved downward and convex like the end plate portion 1c. The peripheral edge of the partition plate 2 is watertightly coupled to the inner peripheral surface of the cylindrical portion 1a by welding or the like.

The first water collection / distribution member 4 is disposed in the upper part of the upper chamber 20, and the upper water supply / discharge pipe 3 is connected to the first water collection / distribution member 4. A second water collection / distribution member 6 is installed in the lower part of the upper chamber 20, and the first communication pipe 5 is connected to the water collection / distribution member 6. A third water collection / distribution member 9 is installed in the upper part of the lower chamber 30, and the second communication pipe 8 is connected to the water collection / distribution member 9. The

communication pipes

5 and 8 are connected by a third communication pipe 11, and a valve 12 is installed in the communication pipe 11.

Valves

7 and 10 are provided at the end portions of the

communication pipes

5 and 8 as means for supplying and discharging the regenerated liquid. A fourth water collection / distribution member 14 is installed in the lower part of the lower chamber 30, and the lower water supply / discharge pipe 13 is connected to the water collection / distribution member 14.

Most of the inside of the upper chamber 20 is filled with an anion exchange resin 21, and a granular inert resin 22 is filled above the anion exchange resin 21. The first water collection / distribution member 4 is embedded in the inert resin 22.

Most of the inside of the lower chamber 30 is filled with a cation exchange resin 31, and a granular inert resin 32 is filled above the cation exchange resin 31. The third water collecting and distributing member 9 is embedded in the inert resin 32. As the inert resin, a polyacrylonitrile resin having a specific gravity smaller than that of the ion exchange resin is used. The particle size of the inert resin is preferably about the same as that of the ion exchange resin.

Although not shown, the lower portion of the upper chamber 20 and the lower portion of the lower chamber 30 are filled with particles having a specific gravity greater than that of an ion exchange resin such as glass beads, and the water collecting and distributing

members

6 and 14 are placed in the high specific gravity particle packed layer. It may be embedded in In this way, the water that flows out from the water collection and

distribution members

6 and 14 is uniformly distributed and supplied into the anion exchange resin 21 and the cation exchange resin 31.

The water collecting and distributing

members

4, 6, 9, and 14 pass water, but block the passage of the ion exchange resin, and the water collecting plates used in the conventional ion exchange apparatus and radially extended. A strainer provided with many slits in the pipe can be used. For example, when the size of the ion exchange resin is about 0.4 mm, it is preferable to use a strainer having a slit width of about 0.2 mm. The water collecting and distributing

members

4, 6, 9, and 14 have shapes along the end plate portion 1b, the partition plate 2, and the end plate portion 1c, and have a small dead space along the end plate portion 1b, the partition plate 2, and the end plate portion 1c. It has become.

[Water sampling process]
The flow at the time of production (water sampling) of deionized water using this ion exchange device is shown in FIG. 1a. In this case, the valve 12 is opened, the

valves

7 and 10 are closed, and raw water (treated water) is supplied from the lower supply / discharge pipe 13. This raw water is a water collection / distribution member 14, a cation exchange resin 31, an inert resin 32, a water collection / distribution member 9, a

communication pipe

8, 11, 5, a water collection / distribution member 6, an anion exchange resin 21, an inert resin 22, and a water collection / distribution member 4. Then, it flows in the order of the upper supply / discharge pipe 3 and is taken out as treated water (deionized water).

[Regeneration process]
When the cation exchange resin 31 and the anion exchange resin 21 are regenerated, the valve 12 is closed and the

valves

7 and 10 are opened as shown in FIG. 1b, and an alkaline solution such as NaOH is supplied from the upper supply / discharge pipe 3 to the upper chamber 20. Then, an acid solution such as HCl and H ₂ SO ₄ is supplied to the lower chamber 30 from the third communication pipe 8. The alkaline solution flows in the order of the water collection / distribution member 4, the inert resin 22, the anion exchange resin 21, the water collection / distribution member 6, and the communication pipe 5, and flows out as recycled wastewater (alkali), whereby the anion exchange resin 21 is regenerated. . The acid solution flows in the order of the water collection / distribution member 9, the inert resin 32, the cation exchange resin 31, the water collection / distribution member 14, and the lower supply / discharge pipe 13, and flows out as recycled wastewater (acid). Played.

[First cleaning step]
After the regeneration, the first cleaning process is performed as shown in FIG. 2a. That is, the

valves

7 and 12 are closed, the valve 10 is opened, and raw water is supplied from the lower supply / discharge pipe 13. The raw water flows in the order of the lower supply / discharge pipe 13, the water collection / distribution member 14, the cation exchange resin 31, the inert resin 32, the water collection / distribution member 9, and the third communication pipe 8, and flows out as washing waste water. Washing wastewater is sent to a wastewater treatment facility. Thus, the 1st washing | cleaning process which rinses the cation exchange resin 31 and the inert resin 32 of the lower chamber 30 is implemented. In the first cleaning process, the liquid flow to the upper chamber 20 is stopped.

The first cleaning step is performed until the electrical conductivity or acid concentration of the cleaning wastewater in the lower chamber 30 discharged from the third communication pipe 8 becomes a predetermined value or less.

[Second cleaning step]
When the acid concentration of the washing waste water in the lower chamber 30 becomes a predetermined value or less, the supply of raw water from the lower supply / discharge pipe 13 is continued, the

valves

7 and 10 are closed and the valve 12 is opened as shown in FIG. Two cleaning steps are performed. The raw water supplied from the lower supply / discharge pipe 13 includes a water collection / distribution member 14, a cation exchange resin 31, an inert resin 32, a water collection / distribution member 9,

communication pipes

8, 11, 5, a water collection / distribution member 6, an anion exchange resin 21, It flows in the order of the inert resin 22, the water collection and distribution member 4, and the upper water supply / discharge pipe 3, and flows out as washing waste water. In this way, the second cleaning step of rinsing the cation exchange resin 31 and the inert resin 32 in the lower chamber 30 and the anion exchange resin 21 and the inert resin 22 in the upper chamber 20 is performed.

The second cleaning step is performed until the specific resistance value of the cleaning drainage of the upper chamber 20 discharged from the upper supply / discharge pipe 3 becomes a predetermined value or more, for example, 18 MΩ · cm or more.

When the specific resistance value of the washing waste water in the upper chamber 20 becomes a predetermined value or more, the supply of raw water from the lower supply / discharge pipe 13 is continued, and the process returns to the water sampling process as shown in FIG.

In this embodiment, the anion exchange resin 21 and the cation exchange resin 31 are not mixed at all in the regeneration step shown in FIG. 1b. Further, the regeneration alkaline solution does not flow into the lower chamber 30 and the acid solution is not mixed into the upper chamber 20, and reverse regeneration is completely prevented. In addition, the anion exchange resin 21 and the cation exchange resin 31 can be regenerated at the same time, and the regenerating time is remarkably short. In addition, the regenerant is passed in a downward flow, and the fully regenerated ion exchange resin is fixed to the top of each ion exchange resin by filling with the inert resin, and the outlet of the water to be treated at the time of sampling Since this ion exchange resin is located on the side, high-quality treated water can be obtained. Further, the flow of the regenerant in the downward flow does not flow the resin, so that the flow rate can be increased compared with the flow of the regenerant in the upward flow, and the regeneration efficiency is good.

In this embodiment, since raw water is used for cleaning in the cleaning process shown in FIGS. 2a and 2b, it is not necessary to provide a regenerating water tank for storing high-purity pure water, and the cost can be reduced. Further, in the first cleaning step (FIG. 2a), after sufficiently washing the resin in the lower chamber 30 using raw water, the upper chamber 20 and the lower chamber 30 are communicated to move to the second cleaning step. The cleaning waste water of the lower chamber 30 containing acid does not enter the upper chamber 20 and reverse regeneration does not occur.

In the first cleaning step and the second cleaning step, cations in the cleaning water (raw water) are adsorbed on the lower cation exchange resin 31 in the lower chamber 30, but the upper cation exchange resin 31 in the lower chamber 30 is not absorbed. Adsorption does not progress. Therefore, the cation concentration in the outflow water of the lower chamber 30 after resuming the sampling is sufficiently low.

In the second cleaning step, the lower chamber 30 effluent is circulated upward into the upper chamber 20, and anions in the lower chamber 30 effluent (mainly anions contained in the raw water) are anion exchanged in the lower portion of the upper chamber 20. Although it adsorbs to the resin 21, the adsorption does not proceed to the upper anion exchange resin 21 in the upper chamber 20. Therefore, the anion concentration in the upper chamber 20 effluent (treated water) after resuming water sampling is sufficiently low.

When starting the flow of raw water in the upward flow in the washing process, the ion exchange resin rises and forms a fixed bed. If the flow of raw water is stopped before the water sampling process, the ion exchange resin flows and settles and the adsorption zone is disturbed, and in the subsequent upstream water sampling process, the quality of the treated water may deteriorate. . According to the present embodiment, the flow of the raw water in the upward flow is continued until the cleaning process returns to the water sampling process. Maintain and prevent degradation of treated water quality.

This ion-exchange apparatus is one in which one tower body 1 is partitioned into two upper and lower chambers by one partition plate 2, and the height of the tower body is low and the installation space is also small. Also, the

pipes

5, 11, and 8 communicating the upper chamber 20 and the lower chamber 30 can be shortened.

In this ion exchange apparatus, the water collecting and distributing

members

4, 6, 9, and 14 are provided along the end plate portion 1b, the partition plate 2, and the end plate portion 1c, so that local retention of water is prevented.

In this ion exchange apparatus, the upper chamber 20 and the lower chamber 30 are filled with

inert resins

22 and 32, and the flow of the anion exchange resin 21 and the cation exchange resin 31 is prevented. Are evenly in contact with the anion exchange resin 21 and the cation exchange resin 31, so that high-quality deionized water can be obtained and sufficient regeneration can be performed.

In the above embodiment, the anion exchange resin is accommodated in the upper chamber 20 and the cation exchange resin is accommodated in the lower chamber 30, but the reverse may be possible. In the above embodiment, the upper chamber 20 and the lower chamber 30 communicate with each other via the

pipes

5, 11, and 8, but the present invention is not limited to this as long as the outside of the tower body 1 is routed. In this embodiment, the three

valves

7, 10, 12 are used, but the flow path may be switched using two three-way valves.

In the present invention, as shown in FIG. 3, an extraction pipe 42 as a means for extracting washing wastewater may be connected to the top of the tower 1. The extraction pipe 42 is provided with a valve 41. A particle outflow prevention member (not shown) such as a mesh or a strainer is installed at the opening to the upper chamber 20 of the extraction pipe 42.

In the water sampling process, the regeneration process, and the first cleaning process of the ion exchange apparatus of FIG. 3, the valve 41 is closed, and the flow of the liquid is the same as in FIGS. 1a, 1b, and 2a. In the second cleaning step, the valve 41 is opened, and a part of the cleaning waste water in the upper chamber 20 is discharged from the extraction pipe 42. Since washing waste water is also discharged from the extraction pipe 42, regeneration liquid discharge (rinsing) at the top of the tower is promoted.

In the present invention, raw water may be used as dilution water for the regenerant. When the cation exchange resin 31 is regenerated with an HCl solution having a concentration of several percent, in the regeneration step, the atmosphere in the tower is in a state where HCl of% order, that is, H ⁺ ions are present. Since cations (Na, Ca, etc.) contained in the raw water as dilution water are at the mg / L level, cations in the raw water for dilution are hardly adsorbed on the cation exchange resin in the regeneration step. By using raw water as dilution water, the cost of regeneration treatment can be reduced.

In the present invention, the above ion exchange apparatus may be installed in a plurality of towers, for example, two towers in parallel, and water may be collected in one apparatus and the other apparatus may be used as a spare. As one apparatus moves to the regeneration / washing process, the other (preliminary) apparatus starts the water sampling process, so that water sampling can be continued. The ion exchange apparatus that has completed the regeneration / washing process waits until the other ion exchange apparatus moves to the regeneration process.

In the above embodiment, the ion exchange device partitions the inside of the tower body 1 into the two chambers of the upper chamber 20 and the lower chamber 30 by the partition plate 2, and accommodates the cation exchange resin in one of the upper chamber 20 and the lower chamber 30. In the other, the structure (2 beds and 1 tower) containing the anion exchange resin is used, but the tower containing the cation exchange resin, the tower containing the anion exchange resin, and the communication pipe connecting these two towers ( 2 beds, 2 towers, 2 beds, 3 towers, etc.).

Hereinafter, the present invention will be described more specifically with reference to experimental examples, examples, and comparative examples. The present invention is not limited to these.

<Experimental example 1>
The ion exchange apparatus shown in FIG. 1 was used. The specifications are as follows.

Tower diameter: 500mm
Tower height: 5000 mm
Upper chamber volume: 200L
Lower chamber volume: 200L
Anion exchange resin: (Kurita Industry Co., Ltd. EX-AG)
Cation exchange resin: (Kurita Industry Co., Ltd. EX-CG)
Filling amount of anion exchange resin: 100L
Filling amount of cation exchange resin: 100L
Filling amount of inert resin (LANXESS IN-42) 22: 80L
Filling quantity of inert resin (LANXESS IN-42) 32: 80L

As the raw water, a solution obtained by dissolving NaCl in ultrapure water so as to have a concentration of 1 ppm was used for the following water sampling process, regeneration process, washing process and test water sampling.

[Water sampling process]
As shown in FIG. 1a, the raw water was passed through the ion exchange apparatus at SV = 50h ^{−1 for} 120 hours.

[Regeneration process]
Next, the following acid solution and alkali solution were used as a regenerant, and water was passed as shown in FIG. 1b to regenerate the anion exchange resin and the cation exchange resin simultaneously.

Regeneration conditions HCl: 4% SV = 5 h ⁻¹ , 30 minutes NaOH: 4% SV = 5 h ⁻¹ , 30 minutes

[Washing process]
Next, as shown in FIG. 4a, the valve 12 is closed, the

valves

7 and 10 are opened, and the raw water is passed through the anion exchange resin and the cation exchange resin for 5 minutes at SV = 100 h ^{−1 for} 5 minutes. And washed.

[Test sampling]
After this cleaning, as shown in FIG. 4 b, the

valves

7 and 10 are closed, the valve 12 is opened, the ultrapure water is supplied from the lower supply / discharge pipe 13, and the specific resistance value of the outflow water taken out from the upper supply / discharge pipe 3 Was measured over time. The results are shown in FIG.

<Experimental example 2>
In Experimental Example 1, water was collected, regenerated and cleaned under the same conditions as in Experimental Example 1 except that the NaCl concentration of the raw water used in the cleaning process was 1.5 ppm. The change over time in the specific resistance value was measured. The results are shown in FIG.

<Experimental example 3>
In Experimental Example 1, sampling, regeneration, and cleaning were performed under the same conditions as in Experimental Example 1 except that the NaCl concentration of the raw water used in the cleaning process was 2 ppm, and the specific resistance of the effluent of the upper supply / discharge pipe 3 The change in value over time was measured. The results are shown in FIG.

As shown in FIG. 5, in Experimental Example 1 where the NaCl concentration of the cleaning raw water was 1 ppm, the specific resistance value of the effluent of the upper supply / discharge pipe 3 quickly became 18 MΩ · cm or more. In contrast, in Experimental Examples 2 and 3 in which the NaCl concentration of the cleaning raw water was 1.5 ppm and 2 ppm, the rise of the specific resistance value was delayed, and the specific resistance value did not reach 18 MΩ · cm or more. As the ion load of the raw water of the ion exchanger, it is considered that the NaCl concentration is 1.5 ppm or more, and it has been confirmed that it is not preferable to pass the raw water in a downward flow in the cleaning process after the regeneration process. It was.

From these experimental examples 1 to 3, it was confirmed that the cleaning process needs to be an upflow instead of a downflow. However, the fact that the cleaning is performed by upflow means that the ion exchange resin in the tower is once floated. Once the ion-exchange resin is floated and a fixed bed is formed, if it is stopped after that, the ion-exchange resin settles while flowing, so the adsorption zone is disturbed and the water quality is changed even if the up-flow sampling is performed again. A decline is inevitable. Therefore, when washing is performed by upflow, it is necessary to shift to the water sampling step without stopping upflow water flow.

In Experimental Examples 1 to 3, since both the cation exchange resin and the anion exchange resin have not been completely regenerated in the tower until the extrusion process before the washing process, the washing water is supplied from the initial washing stage to the cation exchange resin → anion. It was inappropriate to wash the replacement resin in series.

<Example 1>
Raw water (NaCl dissolved in ultrapure water to a NaCl concentration of 2.5 ppm, conductivity 0.55 mS / m) in the same ion exchanger as in Experimental Examples 1 to 3 was the same as in Experimental Examples 1 to 3. The water sampling process was carried out.
Next, regeneration was performed in the same manner as in Experimental Examples 1 to 3.
Then, according to the procedure of FIG. 2a, 2b, the 1st and 2nd washing | cleaning process was performed with this raw | natural water. The water flow SV in the first and second cleaning steps was set to 100 h- ¹ .

After the washing drainage of the lower chamber 30 discharged from the third communication pipe 8 becomes pH 4.5, the supply of raw water is continued, the

valves

7 and 10 are closed, the valve 12 is opened, and the second washing step Went. In Example 1, as shown in FIG. 7b, the outflow water of the upper chamber 20 discharged from the upper supply / discharge pipe 3 is returned to the raw water side and circulated. The change over time in the specific resistance value of the effluent of the upper supply / discharge pipe 3 after the circulation water flow was started was measured. The results are shown in FIG.

<Comparative Example 1>
After water collection and regeneration under the same conditions as in Example 1, the valve 12 was closed as shown in FIG. 7a, and ultrapure water having a specific resistance of 18 MΩ · cm or more was applied to each of the anion exchange resin and the cation exchange resin. Washing was performed by passing water in a downward flow for 5 minutes at a water flow rate of 10 m ³ / h. Next, as shown in FIG. 7 b, the

valves

7 and 10 are closed, the valve 12 is opened, raw water is passed upward from the lower supply / discharge pipe 13, and the upper chamber 20 discharged from the upper supply / discharge pipe 3 is discharged. The treated water was returned to the simulated raw water side and circulated. After this circulation water flow was started, the change with time of the specific resistance value of the treated water discharged from the upper supply / discharge pipe 3 was measured. The results are shown in FIG.

<Comparative example 2>
In the comparative example 1, each process was performed on the same conditions as the comparative example 1 except having used raw water (NaCl density | concentration 2.5 ppm) instead of the ultrapure water for the washing | cleaning process of FIG. After the circulation water flow was started, the change with time of the specific resistance value of the treated water discharged from the upper supply / discharge pipe 3 was measured. The results are shown in FIG.

As shown in FIG. 6, in the case of Comparative Example 2 in which the cleaning treatment after regeneration was performed by passing the raw water in a downward flow, the rise of the specific resistance value was delayed, and the specific resistance value did not reach 18 MΩ · cm. . Example 1 in which the washing treatment after regeneration was performed by passing simulated raw water through the lower chamber in an upward flow, and then continuously flowing upward from the lower chamber to the upper chamber, In Comparative Example 1 in which ultrapure water was passed through each of the lower chambers in a downward flow, the rise in specific resistance value and the water quality of the treated water were comparable.

Although the present invention has been described in detail using specific embodiments, it will be apparent to those skilled in the art that various modifications can be made without departing from the spirit and scope of the invention.
This application is based on Japanese Patent Application No. 2014-230827 filed on Nov. 13, 2014, which is incorporated by reference in its entirety.

DESCRIPTION OF SYMBOLS 1

Tower body

1b, 1c End plate 2 Partition plate 3 Upper supply / discharge piping 4, 6, 9, 14 Water collection /

distribution member

5, 8, 11 Communication piping 13 Lower supply / discharge piping 20 Upper chamber 30 Lower chamber

Claims

Each has a first chamber and a second chamber for containing an ion exchange resin, the cation exchange resin is contained in one of the first chamber and the second chamber, and the anion exchange resin is contained in the other. A method of operating a regenerative ion exchange apparatus in which the two chambers are communicated by a communication means,
A water sampling step of passing raw water in the order of the first chamber, the communication means, and the second chamber;
A regeneration step of regenerating the cation exchange resin and the anion exchange resin;
A washing step of washing the cation exchange resin and the anion exchange resin;
In the operation method of the regenerative ion exchange apparatus having
In the water sampling step, raw water is passed through the first chamber and the second chamber in an upward flow,
The washing step includes
A first cleaning step of passing raw water through the first chamber in an upward flow to clean the resin in the first chamber and discharging cleaning wastewater from the first chamber;
After the first cleaning step, raw water is passed through the first chamber in an upward flow to clean the resin in the first chamber, and the cleaning waste water in the first chamber is supplied to the second chamber by the communication means. And a second cleaning step of cleaning the resin in the second chamber by passing the cleaning wastewater upward through the second chamber;
A method for operating a regenerative ion exchange apparatus, comprising:
In Claim 1, between the said 1st washing | cleaning process and the said 2nd washing | cleaning process, supply of the raw | natural water to the said 1st chamber is continued, and the washing waste_water | drain which flows out from a 1st chamber is guide | induced to a 2nd chamber. A method of operating a regenerative ion exchange apparatus, wherein the second cleaning step is performed by switching the communication means.
3. The operation method of a regenerative ion exchange apparatus according to claim 1, wherein after the second cleaning step, the raw water is continuously returned to the water sampling step while passing through the first chamber.
4. The method of operating a regenerative ion exchange apparatus according to any one of claims 1 to 3, wherein in the regeneration step, the regeneration liquid is passed in a downward flow in the first chamber and the second chamber.
5. The regenerative ion exchange according to claim 1, wherein in the second cleaning step, at least a part of the cleaning waste water in the second chamber is discharged from an extraction pipe provided at the top. How to operate the device.