Multistage reverse osmosis membrane treatment system

A two-stage reverse osmosis membrane system with high and low permeation flux membranes and pH adjustment effectively addresses the challenge of achieving high-quality treated water with reduced energy consumption by enhancing boron and silica removal and preventing scaling.

JP2026032608AInactive Publication Date: 2026-02-27KURITA WATER INDUSTRIES LTD
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Patent Information

Application Number
JP2024135253
Authority / Receiving Office
JP · JP
Patent Type
Applications
Current Assignee / Owner
Filing Date
2024-08-14
Publication Date
2026-02-27
Estimated Expiration
Not applicable · inactive patent

AI Technical Summary

Technical Problem

Existing reverse osmosis membrane treatment systems face challenges in achieving high-quality treated water while reducing operating energy consumption, particularly in removing weakly acidic ionic species like boron and silica, and there is a need for improved energy efficiency in multistage systems.

Method used

A two-stage reverse osmosis membrane system is employed, where the first membrane has a high permeation flux and the second membrane has a low permeation flux, with pH adjustment to the alkaline side for the second membrane, using an alkali addition means to enhance boron and silica removal, and potentially adding a scale inhibitor to prevent scaling.

Benefits of technology

The system achieves reduced operating energy consumption and improved water quality by maintaining high boron removal rates and minimizing the impact of membrane degradation, while also reducing power consumption through lower pressure operation of the first membrane.

✦ Generated by Eureka AI based on patent content.

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Abstract

To provide a multistage reverse osmosis membrane treatment system capable of obtaining treated water of high quality while suppressing operation energy.SOLUTION: A multistage reverse osmotic membrane treatment system 1 is equipped with a storage tank 2 for storing W0 to be treated and the water supply pipe 3 connected to the storage tank 2 and a liquid supply pump 4, a first reverse osmotic membrane 5 and a second reverse osmotic membrane 6 are successively provided to the water supply pipe 3. An aqueous NaOH soln. adding means 7 is connected to the front stage of the second reverse osmotic membrane 6 and the addition amt. of an aqueous NaOH soln. can be controlled so that the water to be treated of the second reverse osmotic membrane 6 becomes an alkali region corresponding to the flow amt. of the water passing pipe 3 and the pH of the W0 of the water to be treated. The first reverse-osmosis membrane 5 has a permeation flow rate of 2. 1MPa / (0m3·day) or more per membrane surface effective pressure m2 (water temperature 25 °C., pure water (RO permeate)), and the second reverse-osmosis membrane 6 has a permeation flow rate of 0. 1MPa / (8m3·day) or more and less than 2. m2 / (0m3·day) per membrane surface effective pressure m2 (water temperature 25 °C., pure water (RO permeate)).SELECTED DRAWING: Figure 1
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Description

[Technical Field]

[0001] The present invention relates to a multi-stage reverse osmosis membrane treatment system, and more particularly to a multi-stage reverse osmosis membrane treatment system that can obtain treated water of a predetermined level of quality while suppressing operating energy. [Background technology]

[0002] Conventionally, pure water such as ultrapure water, from which organic matter, ionic components, fine particles, bacteria, etc. have been highly removed, has been used as washing water in the manufacturing processes of semiconductor devices and liquid crystal display devices. To produce such pure water, a multistage reverse osmosis membrane treatment system, in which two or more stages of reverse osmosis membranes (RO membranes) are connected in series, is used because it is highly versatile and can easily produce a desired water quality. However, reverse osmosis membranes consume a lot of power, so they are not necessarily suitable for meeting recent demands for energy conservation.

[0003] These reverse osmosis membranes come in a variety of performances depending on the membrane surface effective pressure, permeation flux, etc., and attempts have been made to combine reverse osmosis membranes with different performances. For example, Patent Document 1 discloses a system comprising a first reverse osmosis membrane treatment means for passing water to be treated through a first reverse osmosis membrane to obtain a first permeate and a first concentrate, and at least a second reverse osmosis membrane treatment means for passing the first permeate through a second reverse osmosis membrane to obtain a second permeate and a second concentrate, wherein the permeation flux per 1 MPa of the effective pressure of the second reverse osmosis membrane is lower than the permeation flux per 1 MPa of the effective pressure of the first reverse osmosis membrane, and the permeation flux per 1 MPa of the second reverse osmosis membrane is 0.5 m 3 / m 2 A reverse osmosis membrane treatment system with a filtration rate of 1000 kJ / d or less has been proposed.

[0004] 3, Patent Document 2 discloses a pure water production system 11 including a storage tank 12 for storing raw water to be treated W0, and a water supply pipe 13 connected to the storage tank 12, the water supply pipe 13 being provided with a liquid supply pump 14, a first reverse osmosis membrane 15, a second reverse osmosis membrane 16, and an ion exchange device 17 in that order. In Patent Document 2, the first reverse osmosis membrane 15 has a permeation flux of 0.8 m per 1 MPa of effective membrane surface pressure (water temperature 25°C, pure water (RO permeate)). 3 / (m 2 A reverse osmosis membrane of 2.0 m permeation flux per membrane effective pressure of 1 MPa (water temperature 25°C, pure water (RO permeate)) is used as the second reverse osmosis membrane 16. 3 / (m 2 By using a reverse osmosis membrane of 1000 kJ / s or more, it is possible to reduce operating energy while maintaining water quality. [Prior art documents] [Patent documents]

[0005] [Patent Document 1] Japanese Patent Application Publication No. 2018-79451 [Patent Document 2] Japanese Patent Application Publication No. 2023-70396 Summary of the Invention [Problem to be solved by the invention]

[0006] However, the reverse osmosis membrane treatment system described in Patent Document 1 aims to improve water quality by removing IPA from the permeate water, and has the problem of being less effective in reducing operating energy. Therefore, it is conceivable to combine the system with a reverse osmosis membrane, which requires less operating energy, but this creates the problem of making it difficult to obtain treated water from which weakly acidic ionic species such as boron and silica have been sufficiently removed.

[0007] Furthermore, the multi-stage reverse osmosis membrane treatment system described in Patent Document 2 is capable of removing weakly acidic ion species such as boron and silica while reducing operating energy, but there is still room for improvement in terms of water quality.

[0008] The present invention has been made in view of the above-mentioned problems, and has an object to provide a multi-stage reverse osmosis membrane treatment system that can obtain high-quality treated water while reducing operating energy. [Means for solving the problem]

[0009] In view of the above object, the present invention provides a multistage reverse osmosis membrane treatment system in which reverse osmosis membranes are arranged in series in two stages, and of the two stages of reverse osmosis membranes, the first reverse osmosis membrane in the first stage has a permeation flux of 2.0 m per membrane effective pressure of 1 MPa (water temperature 25°C, pure water (RO permeate)). 3 / (m 2 The second reverse osmosis membrane in the latter stage has a permeation flux of 0.8 m per membrane effective pressure of 1 MPa (water temperature 25°C, pure water (RO permeate)). 3 / (m 2 · days) or more, 2.0m 3 / (m 2 The present invention provides a multi-stage reverse osmosis membrane treatment system having a reverse osmosis membrane with a pH of less than 1 / 2 days, and an alkali addition means for adjusting the pH of the water to be treated by the first reverse osmosis membrane to the alkaline side.

[0010] According to this invention (Invention 1), by using a reverse osmosis membrane (first reverse osmosis membrane) with a high permeation flux per 1 MPa of effective membrane surface pressure (low effective membrane surface pressure at the same permeation flux), it is possible to significantly reduce operating energy compared to a multi-stage reverse osmosis membrane treatment system configured solely with reverse osmosis membranes with lower permeation fluxes. Furthermore, by adjusting the pH of the feedwater (water to be treated) to the alkaline side for the subsequent reverse osmosis membrane (second reverse osmosis membrane) with a low permeation flux per 1 MPa of effective membrane surface pressure (high effective membrane surface pressure at the same permeation flux), boron and TOC can be maintained at or above predetermined levels. This allows for both reduced operating energy and water quality. In particular, the boron removal rate can be improved compared to when the order of the first and second reverse osmosis membranes is reversed. Furthermore, it is generally known that upstream reverse osmosis membranes have a higher water supply load and are more susceptible to membrane degradation than downstream reverse osmosis membranes. However, when multiple membranes with significantly different low-molecular-weight TOC rejection rates are installed, as in Invention 1, the final water quality depends on the membrane with the higher rejection rate. Therefore, if the upstream reverse osmosis membrane is an ultra-low-pressure reverse osmosis membrane, its degradation leads to a deterioration in the water quality of the entire system. However, if the upstream reverse osmosis membrane is an ultra-low-pressure reverse osmosis membrane, as in Invention 1, the impact on the TOC rejection rate of the entire system can be reduced as long as the downstream ultra-low-pressure membrane is in good condition. Furthermore, the upstream reverse osmosis membrane, which has a larger water volume, is operated at a lower pressure, which also reduces power consumption.

[0011] In the above invention (Invention 1), it is preferable that the first reverse osmosis membrane has a Ca and Mg removal rate of 99% or more and a SiO2 removal rate of 95% or more. (Invention 2).

[0012] According to this invention (Invention 2), by using such a first reverse osmosis membrane, scaling in the second reverse osmosis membrane can be suppressed when treatment is performed at a high pH in the subsequent second reverse osmosis membrane.

[0013] In the above invention (Invention 1), it is preferable to have a means for adding a scale inhibitor to the treated water of the second reverse osmosis membrane (Invention 3).

[0014] According to this invention (Invention 3), scaling in the second reverse osmosis membrane can be prevented when treatment is carried out at a high pH in the second reverse osmosis membrane in the subsequent stage.

[0015] Furthermore, in the above inventions (Inventions 1 to 3), it is preferable that the water quality of the water to be treated in the multistage reverse osmosis membrane treatment system has a boron concentration of 1 to 500 μg / L (Invention 4).

[0016] According to this invention (Invention 4), by treating water having the above boron concentration with a multistage reverse osmosis membrane treatment system, it is possible to remove boron from the treated water at a high level of 95% or more. [Effects of the Invention]

[0017] The multi-stage reverse osmosis membrane treatment system of the present invention uses a reverse osmosis membrane with a permeation flux per 1 MPa of effective membrane surface pressure greater than a predetermined value in the first stage and a reverse osmosis membrane with a permeation flux per 1 MPa of effective membrane surface pressure less than a predetermined value in the second stage, thereby adjusting the pH of the feedwater (water to be treated) to the alkaline side for treatment, thereby achieving both reduced operating energy consumption and good water quality. Furthermore, the impact of a decrease in the TOC removal rate of the entire system can be reduced. [Brief explanation of the drawings]

[0018] [Figure 1] FIG. 1 is a flow diagram showing a multistage reverse osmosis membrane treatment system according to an embodiment of the present invention. [Figure 2] FIG. 1 is a flow diagram showing a multistage reverse osmosis membrane treatment system of Comparative Example 1. [Figure 3] FIG. 1 is a flow diagram showing a pure water production apparatus using a conventional multistage reverse osmosis membrane treatment system. DETAILED DESCRIPTION OF THE INVENTION

[0019] Hereinafter, a multistage reverse osmosis membrane treatment system of the present invention will be described with reference to the accompanying drawings.

[0020] [Multi-stage reverse osmosis membrane treatment system] Figure 1 shows a multistage reverse osmosis membrane treatment system according to one embodiment of the present invention. In Figure 1, the multistage reverse osmosis membrane treatment system (two-stage reverse osmosis membrane treatment system) 1 includes a storage tank 2 for storing water to be treated WO as raw water to be treated, and a water supply pipe 3 connected to the storage tank 2. The water supply pipe 3 is sequentially provided with a liquid supply pump 4, a first reverse osmosis membrane 5, and a second reverse osmosis membrane 6. An NaOH aqueous solution supplying means 7, which serves as an alkali supplying mechanism, is connected upstream of the second reverse osmosis membrane 6. A control mechanism (not shown) can control the amount of NaOH solution supplied to the second reverse osmosis membrane 6 so that the water to be treated reaches an alkaline range, depending on the flow rate of the water supply pipe 3 and the pH of the water to be treated WO.

[0021] (reverse osmosis membrane) In this specification, the first reverse osmosis membrane and the second reverse osmosis membrane are defined as having the following performance: Note that although there are reverse osmosis membranes that have a smaller permeation flux per 1 MPa of effective membrane surface pressure than the first reverse osmosis membrane and the second reverse osmosis membrane, these are very general-purpose reverse osmosis membranes.

[0022] <First reverse osmosis membrane> - Permeation flux of 0.6m under the condition of membrane surface effective pressure of 0.3MPa (water temperature 25℃, pure water (RO permeate)) 3 / (m 2 permeation flux of 2.0 m per membrane effective pressure of 1 MPa (water temperature 25°C, pure water (RO permeate)) 3 / (m 2 (days) or more Salt rejection rate: 95% or more (membrane surface effective pressure 0.3 MPa (water temperature 25°C, feed water 500 mg / L at NaCl) IPA removal rate: 60% or more (membrane surface effective pressure 0.3 MPa (water temperature 25°C, feed water 500 mg / L at IPA)

[0023] In particular, it is preferable that the first reverse osmosis membrane has an effective membrane surface pressure of 0.3 MPa, a Ca and Mg removal rate of 99% or more, and an SiO2 removal rate of 95% or more.

[0024] <Second reverse osmosis membrane> - Permeation flux of 0.6m under the condition of membrane surface effective pressure of 0.75MPa (water temperature 25℃, pure water (RO permeate)) 3 / (m 2 permeation flux per membrane surface effective pressure of 1 MPa (water temperature 25°C, pure water (RO permeate)) of 0.8 to 2.0 m 3 / (m 2 ·day) Salt rejection rate: 98% or more (membrane surface effective pressure 0.75 MPa (water temperature 25°C, feed water 500 mg / L at NaCl) IPA removal rate: 80% or more (membrane surface effective pressure 0.75 MPa (water temperature 25°C, feed water 500 mg / L at IPA)

[0025] (Operation method of multi-stage reverse osmosis membrane treatment system) The operation method of the above-described multi-stage reverse osmosis membrane treatment system will now be described. First, the liquid feed pump 4 is driven to supply the water to be treated W0 stored in the storage tank 2 to the first reverse osmosis membrane 5. For the treatment of this embodiment, the water to be treated W0 preferably has a boron concentration of 1 to 500 μg / L. Ionic impurities are removed to a certain extent by the first reverse osmosis membrane 5 to obtain primary treated water W1. The water supply pressure of the water to be treated W0 from the liquid feed pump 4 at this time may be set based on the configuration of the reverse osmosis membrane and the desired permeation flux.

[0026] Specifically, the first reverse osmosis membrane 5 has a permeation flux of 2.53 m per membrane surface effective pressure of 1 MPa (water temperature 25°C, pure water (RO permeate)). 3 / (m 2 A reverse osmosis membrane (1.00 m 2 / 1.00 m 3 / 1.00 m 4 / 1.00 m 5 / 1.00 m 6) was used as the second reverse osmosis membrane 6, and the effective membrane surface pressure was 1 MPa (water temperature 25°C, pure water (RO permeate)). 3 / (m 2 When a reverse osmosis membrane of 1.00 m / s is used, the first reverse osmosis membrane 5 and the second reverse osmosis membrane 6 each have a permeation flux (flux) of 1.00 m / s. 3 / (m 2When water is passed through the first reverse osmosis membrane 5 at a permeation flux of 1.00 m / s, the water supply pressure from the liquid feed pump 4 may be set to approximate the sum of the effective pressures on the membrane surfaces at that flux. 3 / (m 2 Since the effective membrane surface pressure of the second reverse osmosis membrane 6 at 20°C (days) is 0.39 MPa and the effective membrane surface pressure of the second reverse osmosis membrane 6 is 1.0 MPa, the pressure should be set to 1.4 (≒0.39 + 1.0) MPa.

[0027] Next, an NaOH aqueous solution is added to the primary treated water W1 using an NaOH aqueous solution adding means 7 to adjust the pH of the primary treated water W1 to the alkaline side before being treated by the second reverse osmosis membrane 6. Specifically, the pH of the primary treated water W1 is preferably adjusted to 8 to 11. Adjusting the pH of the primary treated water W1 to 8 to 11 improves the removal rate of weakly acidic ionic species, such as boron and silica, remaining in the primary treated water W1. A scale inhibitor may also be added to the primary treated water W1. The scale inhibitor is not particularly limited and can be selected appropriately depending on the quality of the primary treated water W1. For example, phosphonic acids such as 2-phosphonobutane-1,2,4-tricarboxylic acid, copolymers of acrylic acid and 2-acrylamido-2-methylpropanesulfonic acid, polyacrylic acid, phosphonic acids such as 2-phosphonobutane-1,2,4-tricarboxylic acid, polyacrylic acid, etc., can be used. The amount of these scale inhibitors added is approximately 10 to 1000 mg / L. Then, by treating with this second reverse osmosis membrane 6, remaining ionic impurities, particularly boron and silica, are removed to obtain secondary treated water W2.

[0028] The residence time of the water to be treated W0 in the treatment with the first reverse osmosis membrane 5 and the second reverse osmosis membrane 6 as described above is preferably 10 seconds or more, particularly 30 seconds or more. A residence time of less than 30 seconds, particularly less than 10 seconds, is undesirable because it becomes impossible to maintain a sufficiently high removal rate of boron, as well as Ca, Mg, and SiO.

[0029] Furthermore, this secondary treated water W2 can be treated with an ion exchange device or the like as needed to further remove remaining ionic impurities, thereby producing pure water.

[0030] According to the multistage reverse osmosis membrane treatment system 1 of this embodiment, the permeation flux per membrane surface effective pressure of 1 MPa (water temperature 25°C, pure water (RO permeate)) is 2.0 m 3 / (m 2 The multistage reverse osmosis membrane treatment system 1 uses a first reverse osmosis membrane 5 with a flow rate of at least 1.0 MPa (approximately 1.0 MPa / day) and adjusts the pH of the primary treated water W1 treated by the second reverse osmosis membrane 6 to the alkaline side. This allows the boron removal rate of the resulting secondary treated water W2 to be maintained at a high level (e.g., 95% or higher). Furthermore, the operating energy of the multistage reverse osmosis membrane treatment system 1 is roughly proportional to the feed pressure of the water W0 from the feed pump 4, i.e., the output of the feed pump 4, which can be used to compare the magnitude of operating energy. For example, under the same conditions as the feed pressure from the feed pump 4 described above, if two second reverse osmosis membranes 6 are installed in series, the feed pressure of the feed pump 4 is theoretically 2.0 (≒ 1.0 × 2) MPa, resulting in an operating energy reduction rate of approximately 30% ((2.0 - 1.4) / 2.0 × 100 ≒ 30).

[0031] While the present invention has been described above based on the above embodiment, the present invention is not limited to the above embodiment and can be implemented in various modified forms. For example, in the above embodiment, a case has been described in which a first reverse osmosis membrane and a second reverse osmosis membrane are connected in two stages in series. However, in the present invention, in a multi-stage reverse osmosis membrane treatment system in which reverse osmosis membranes are connected in series in multiple stages, it is sufficient to use a first reverse osmosis membrane as the reverse osmosis membrane in the preceding stage and adjust the pH of the liquid to the alkaline side in the subsequent stage, and the system may be configured with three or more stages of reverse osmosis membranes. [Example]

[0032] The present invention will be described in more detail below based on specific examples, but the present invention is not limited to the following examples.

[0033] [Confirmation of performance of the first reverse osmosis membrane 5 and the second reverse osmosis membrane 6] In this example, the first reverse osmosis membrane 5 and the second reverse osmosis membrane 6 were reverse osmosis membranes having a permeation flow rate (flux) per membrane surface effective pressure of 1 MPa (water temperature 25°C, pure water (RO permeate)) as shown in Table 1. As shown in FIG. 1, these reverse osmosis membranes were configured as an extremely low-pressure reverse osmosis membrane (first reverse osmosis membrane 5) in the first stage and an ultra-low-pressure reverse osmosis membrane (second reverse osmosis membrane 6) in the second stage. Pure water to which 500 μg / L of boron had been added was used to treat treated water, the pH of which had been adjusted by the second-stage reverse osmosis membrane treatment. The boron concentration was measured, and the boron removal rate was calculated. The results are shown in Table 2. As shown in Figure 2, the first stage is an ultra-low pressure reverse osmosis membrane (second reverse osmosis membrane 6) and the second stage is an extremely low pressure reverse osmosis membrane (first reverse osmosis membrane 5). Pure water with 500 μg / L of boron added is used to treat the treated water, which has had its pH adjusted by the second stage reverse osmosis membrane treatment. The boron concentration was measured and the boron removal rate was calculated. The results are also shown in Table 2.

[0034] As shown in Figure 2, in a multi-stage reverse osmosis membrane treatment system 1 with a first-stage ultra-low pressure reverse osmosis membrane (second reverse osmosis membrane 6) and a second-stage extremely low pressure reverse osmosis membrane (first reverse osmosis membrane 5), the boron concentration was measured when pure water was treated with 500 μg / L of boron added and the pH was adjusted, and the boron removal rate was calculated. The results are shown in Table 2.

[0035] [Table 1]

[0036] [Table 2]

[0037] Examples 1 to 4 As shown in Figure 1, a multi-stage reverse osmosis membrane treatment system 1 uses an extremely low-pressure reverse osmosis membrane (first reverse osmosis membrane 5) as the first stage and an ultra-low-pressure reverse osmosis membrane (second reverse osmosis membrane 6) as the second stage. The feedwater was pure water doped with 20 μg / L of boron (B), and the pH was adjusted to 7, 9, 10, or 11 by adding an aqueous NaOH solution via an aqueous NaOH solution dosing means 7. The boron concentrations of the treated water from the first and second reverse osmosis membranes were measured when the first reverse osmosis membrane was operated at a recovery rate of 85% and a recovery rate of 90%. The results are shown in Table 3, along with the boron concentration in the feedwater and the pH of the treated water from the second reverse osmosis membrane. The treatment performance of the extremely low-pressure reverse osmosis membrane (first reverse osmosis membrane 5) used for the treatment of various components is shown in Table 4.

[0038] Comparative Examples 1 to 4 As shown in Figure 2, in a multi-stage reverse osmosis membrane treatment system 1 with a first-stage ultra-low-pressure reverse osmosis membrane (second reverse osmosis membrane 6) and a second-stage extremely low-pressure reverse osmosis membrane (first reverse osmosis membrane 5), pure water with 20 μg / L of boron (B) added was used as feedwater W0, and an aqueous NaOH solution was added via an aqueous NaOH solution adding means 7 to adjust the pH to 7, 9, 10, or 11, respectively. The boron concentrations of the water treated by the first-stage reverse osmosis membrane and the second-stage reverse osmosis membrane were measured when the first-stage reverse osmosis membrane recovery rate was 85% and the second-stage reverse osmosis membrane recovery rate was 90%. The results are shown in Table 1, along with the boron concentration in the feedwater and the pH of the water treated by the second-stage reverse osmosis membrane.

[0039] [Table 3]

[0040] [Table 4]

[0041] As is clear from Table 3, Example 1, in which the pH was not adjusted, had a higher boron concentration than Comparative Example 1, but Examples 2 to 4, in which the pH was adjusted, had lower boron concentrations than Comparative Examples 2 to 4, and it can be seen that the effect of reducing boron concentration was greater as the pH increased, especially within the pH range of 9 to 11. Furthermore, Table 4 also shows that the extremely low-pressure reverse osmosis membrane (first reverse osmosis membrane 5) used in this example did not have a high boron removal performance, but achieved high removal rates of Ca, Mg, and SiO2, and is expected to have an effect of suppressing scaling relative to the second-stage ultra-low-pressure reverse osmosis membrane. This effect cannot be achieved with NF membranes. [Explanation of symbols]

[0042] 1. Multi-stage reverse osmosis membrane treatment system (two-stage reverse osmosis membrane treatment system) 2 storage tank 3 Water supply piping 4. Liquid transfer pump 5. First reverse osmosis membrane 6. Second reverse osmosis membrane 7 NaOH aqueous solution addition means (alkali addition mechanism) W0 Water to be treated (raw water to be treated) W1 Primary treated water W2 Secondary treated water

Claims

1. A multi-stage reverse osmosis membrane treatment system in which reverse osmosis membranes are arranged in series in two stages, Of the two reverse osmosis membranes, the first reverse osmosis membrane in the front stage has a permeation flux of 2.0 m per membrane surface effective pressure of 1 MPa (water temperature 25°C, pure water (RO permeate)). 3 / (m 2 - It is a reverse osmosis membrane of 100% or more, The second reverse osmosis membrane in the latter stage has a permeation flux of 0.8 m per membrane surface effective pressure of 1 MPa (water temperature 25°C, pure water (RO permeate)). 3 / (m 2 ・Day) or more, 2.0m 3 / (m 2 - It is a reverse osmosis membrane of less than 1000kJ / day, a multi-stage reverse osmosis membrane treatment system having an alkali addition means for adjusting the pH of the water to be treated by the first reverse osmosis membrane to the alkaline side;

2. The first reverse osmosis membrane has a Ca and Mg removal rate of 99% or more, and 2 2. The multi-stage reverse osmosis membrane treatment system according to claim 1, wherein the removal rate of 95% or more is 95% or more.

3. 2. The multi-stage reverse osmosis membrane treatment system according to claim 1, further comprising means for adding a scale inhibitor to the treated water from the second reverse osmosis membrane.

4. The multistage reverse osmosis membrane treatment system according to any one of claims 1 to 3, wherein the water quality of the water to be treated in the multistage reverse osmosis membrane treatment system has a boron concentration of 1 to 500 μg / L.

Citation Information

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