JP5281183B2 - Replacement method of membrane cartridge used in membrane treatment equipment for ballast water treatment - Google Patents

Abstract

<P>PROBLEM TO BE SOLVED: To provide an exchange method for a film cartridge used for a film processing equipment for ballast water processing, which controls the increase of cost with the number of detectors when detecting a trouble of the film cartridge, secures a work space when exchanging the film cartridge with trouble, reduces the cost of the entire equipment and exchanges the film cartridge in a short time. <P>SOLUTION: In the film processing equipment, 3 to 20 film cartridges are arranged in a manifold structure to structure a plurality of film units, and a film unit assembly in which the film units are assembled so that each of them is removable is structured. For every one or more film units, a detection means for detecting a trouble of the film cartridge is provided. The detection means detects the occurrence of a trouble in any one of the film cartridges structuring one or more film units, and then one or more film units including the film cartridge with the trouble are pulled out from the film unit assembly and one or more film units are exchanged at a time. <P>COPYRIGHT: (C)2013,JPO&amp;INPIT

Description

  The present invention relates to a method for replacing a membrane cartridge used in a membrane treatment facility for ballast water treatment.

  A cargo ship that transports crude oil or the like is provided with a ballast tank in order to maintain the stability of the hull during navigation. Usually, when crude oil or the like is not loaded, the inside of the ballast tank is filled with ballast water, and when the crude oil or the like is loaded, the ballast water is discharged to adjust the buoyancy of the hull and stabilize the hull.

  As described above, the ballast water is water necessary for the safe navigation of the ship, and normally, the ballast raw water of the port that performs cargo handling is used. The amount is said to exceed 10 billion tons per year worldwide.

  By the way, the ballast water contains microorganisms and eggs of small and large organisms that inhabit the port where the water was taken. It will be.

  Therefore, the destruction of ecosystems, such as the replacement of existing species with species that did not originally live in the sea, has become serious.

  Against this background, the duty to receive periodic inspections related to ballast water treatment equipment, etc. was adopted at a diplomatic meeting of the International Maritime Organization (IMO), which has been applied since 2009.

  In addition, according to the Convention for Regulation and Management of Ship Ballast Water and Sediment (hereinafter referred to as the Convention), the discharge standard of ballast water is up to about 1 / 100th of the number of microorganisms present in the open ocean when ballast water is discharged. It is required to be sterilized or sterilized.

  As a technique for sterilizing microorganisms in ballast water, an ozone sterilization technique (Patent Document 1) is known. Further, from the viewpoint of reducing the amount of ozone used, the present applicant has also proposed a membrane processing technique (Patent Document 2). A membrane used for membrane treatment is generally a microfiltration membrane or an ultrafiltration membrane in consideration of the size of microorganisms to be separated. As the type of film, a flat film (Patent Document 3), a spiral film (Patent Document 4), and the like are known.

  However, in order to process an enormous amount of ballast water in a short time, it is necessary to provide an enormous amount of membrane.

  Patent Document 5 discloses a configuration in which spiral membranes are arranged in series in the cartridge. However, if the membranes are arranged in series, high-speed membrane processing cannot be expected even if a large number of membrane cartridges are provided.

  In order to increase the processing speed, it is necessary to install a large number of membrane cartridges in parallel.

  As an example in which a plurality of membrane cartridges are installed in parallel, a configuration is known in which a plurality of membrane cartridges each provided with a monolithic filter are connected to a header pipe by pipes and installed in parallel (patent) Reference 6).

US2003 / 0015481 JP 2007-268379 A Japanese Patent No. 3160609 JP 2000-271454 A JP 2002-28453 A JP 2005-270810 A

  However, in the configuration in which each membrane cartridge is operated independently in parallel with the above-described piping, the raw water inflow piping, the concentrate liquid piping, the processing liquid piping, etc. are connected to each membrane cartridge, so the number of piping is This is necessary depending on the number of membrane cartridges.

  In the ballast processing, hundreds of membrane cartridges are required, and accordingly, the number of pipes is also required, resulting in an increase in installation space and equipment cost.

  When operating such a large number of membrane cartridges, if any membrane cartridge malfunctions, the configuration in which each membrane cartridge is operated independently as in Patent Document 6 detects the malfunction. Such a detector is required for each membrane cartridge, and there is a problem of enormous cost increase.

  Even if a defect can be detected, a work space for replacement is required to replace the defective membrane cartridge, and an enormous amount of space is required to secure a work space for every several hundred membrane cartridges. I need it. It is difficult to secure the above-described work space within a limited space in the ship.

  Furthermore, there is also a problem peculiar to ballast that it takes about a day to fill a ballast tank with a large amount of ballast water. This is because the time until the ship unloads and re-departs is limited.

  Therefore, the time that can be taken for detecting or replacing the membrane before the ballast water is flooded is extremely limited and must be able to be done in a short time.

  Therefore, the present inventor suppresses the increase in cost associated with the number of detectors when detecting a defect of the membrane cartridge, and secures a work space when replacing the defective membrane cartridge, while reducing the overall equipment cost. The present inventors have found that there is a limit to the conventional idea of operation for each membrane cartridge in order to solve all the problems of replacing the membrane cartridge in a short time, which can be suppressed.

  It is an object of the present invention to suppress an increase in cost due to the number of detectors when detecting a defect in a membrane cartridge, and to reduce the overall equipment cost while securing a work space when replacing a defective membrane cartridge Another object of the present invention is to provide a method for replacing a membrane cartridge used in a membrane treatment facility for ballast water treatment that can be replaced in a short time.

  Other problems of the present invention will become apparent from the following description.

  The inventor assembled a membrane unit by assembling membrane cartridges, introduced the idea of operating each membrane unit, and even if one of the membrane units had a problem, replace each membrane unit. Thus, it has been found that the problem of providing a method for replacing a membrane cartridge used in a membrane treatment facility for ballast water treatment, in which a defective membrane cartridge can be quickly replaced, and the equipment is low-cost and space-saving can be solved. In other words, a membrane cartridge that is not defective appears to be wasted by replacing the defective membrane cartridge together with the defective membrane cartridge. However, with this unconventional idea, a membrane cartridge replacement method used in a practical ballast water treatment facility It came to invent.

In view of this, the invention according to claim 1 is provided with the number of membrane cartridges in which membrane modules are loaded in the inside as many as necessary to fill the ballast tank with the treated water, and supplies the ballast raw water to the membrane cartridge for processing. A method of replacing a membrane cartridge used in a membrane treatment facility for ballast water treatment for obtaining water , wherein a common manifold is connected across a plurality of membrane cartridges, and each membrane cartridge is connected to the membrane cartridge via the manifold. A plurality of membrane units for supplying raw ballast water and taking out treated water from each of the membrane cartridges, and constituting a membrane unit assembly in which the membrane units are detachably assembled. A detection means for detecting a defect of the membrane cartridge is provided for each of the two or more membrane units, and the detection means has one or two or more front units. After failure in any of said membrane cartridge constituting the membrane unit has detected that it has generated, the Kimaku unit before including the membrane cartridge malfunction occurs, withdrawn from the membrane unit assemblies, each membrane unit A membrane cartridge exchange method used in a membrane treatment facility for ballast water treatment, characterized in that the membrane cartridge is exchanged.

  According to the present invention, an increase in cost due to the number of detectors when detecting a defect in the membrane cartridge is suppressed, and an overall facility cost is suppressed while securing a work space when replacing a defective membrane cartridge. In addition, it is possible to provide a method for replacing a membrane cartridge used in a membrane treatment facility for ballast water treatment that can replace the membrane cartridge in a short time.

Illustration of membrane treatment equipment for ballast water treatment Sectional drawing of the principal part of the membrane cartridge used for FIG. Schematic showing the mode of detection means The perspective view which shows the 1st aspect of a manifold structure Cross-sectional view of the main part showing the first aspect of the manifold structure Cross-sectional view of the main part showing the second aspect of the manifold structure Cross-sectional view of the principal part showing the third aspect of the manifold structure Explanatory drawing which shows the aspect of the membrane treatment equipment for ballast water treatment The perspective view which shows the 1st aspect of a membrane unit aggregate | assembly. The perspective view which shows the 2nd aspect of a membrane unit aggregate | assembly. The perspective view which shows the 3rd aspect of a membrane unit aggregate | assembly. Schematic showing an example of providing a detector for each header tube Schematic showing another example in which a detector is provided for each header tube

  Hereinafter, embodiments for carrying out the present invention will be described with reference to the drawings.

  FIG. 1 is an explanatory view of a membrane treatment facility for ballast water treatment, and FIG. 2 is a cross-sectional view of the main part of the membrane cartridge used in FIG.

  In FIG. 1, reference numeral 1 denotes a membrane cartridge. The membrane cartridge 1 includes a ballast-treated water collecting pipe 100 and a plurality of envelope-like films (spiral membranes) wound around the outer circumference of the collecting pipe 100 as shown in FIG. ) 101 is installed inside the spiral membrane module.

  The envelope-like membrane 101 is wound around the outer periphery of the water collecting pipe 100 with high density. For this reason, the processing amount per unit volume is larger than other membranes such as a flat membrane, and it is relatively space-saving. Moreover, since it is made into a cartridge, it is suitable for unitization regardless of the installation place, compared to a type of film that is used by being immersed in a tank.

  Inside each envelope of the two or more enveloped membranes 101 wound around the outer periphery of the water collecting tube 100, a membrane is stretched in an envelope shape, and treated water (permeated water) is supplied to the water collecting tube 100. A support 102 for transfer is provided.

  Even if a spacer 104 is inserted between the adjacent envelope membranes 101 to prevent the envelope membranes from coming into close contact with each other and to reduce the membrane area, and to form the ballast raw water flow channel 103. Good. The raw water channel 103 is formed on the inner surface of the water collecting pipe 100 and the membrane cartridge 1 outside the spiral membrane.

  In the present invention, the membrane cartridge 1 is provided with the number necessary for filling the ballast tank with the treated water, and preferably, the number necessary for filling the ballast tank with the treated water in one day is installed in parallel. To prepare.

The number n of membrane cartridges required to fill the ballast tank with the treated water during the treatment time T (Day) is determined by the capacity of the ballast tank Q (m ³ ), and the membrane area per membrane cartridge. When S (m ² ), initial flux (permeation flux) is F ₀ (m / Day), and processing time is T (Day), it can be expressed by the following equation.
n = α · Q / (S · F ₀ · T)
Accordingly, when the treated water is filled in one day, it can be expressed by the following formula.
n = α · Q / (S · F ₀ )
α is a coefficient for correcting a decrease in throughput during filtration and membrane cleaning, and is usually in the range of 1.05 to 1.30.

For example, the membrane area of one membrane cartridge is 38 m ² and the initial flux is 1.5 m / D. When the capacity of the ballast tank is 20000 m ³ , about 370 to 460 membrane cartridges are required when treated water is supplied in one day.

  This is an example, and in a ballast water treatment facility, it is necessary to process a large amount of ballast water at a high speed, and therefore, there may be hundreds to tens of thousands of membrane cartridges per one ballast water treatment facility.

  In FIG. 1, 4 is a membrane unit, and is constituted by arranging 3 to 20 membrane cartridges 1 side by side.

  Any method may be used as long as the membrane cartridges 1 are installed in parallel, and the membrane cartridge 1 may be arranged in parallel by a manifold structure constituted by a conventional pipe or the like. It is preferable to arrange them side by side with a manifold structure having

  The ballast raw water 10 is pumped up by the ballast pump 11 and supplied to the membrane unit 4 through the ballast raw water suction pipe 12. An open / close valve 13 is provided in the ballast raw water suction pipe 12. 14 is a ballast raw water discharge pipe (cleaning drainage discharge pipe), and 15 is an on-off valve provided in the ballast raw water discharge pipe 14. The cleaning drainage discharge pipe 14 discharges the cleaning drainage to the sea, for example.

  In the present invention, the raw ballast water may be water that has been conventionally used as ship ballast water, and seawater is mainly used.

  The ballast raw water supplied to the membrane unit 4 is introduced into the raw water flow paths 103 of the plurality of membrane cartridges 1 included in the unitized membrane unit 4 by the manifold structure, subjected to membrane treatment, and the generated treated water is used as the ballast tank 16. To be supplied.

  Reference numeral 17 denotes a treated water pipe, and 18 denotes an on-off valve provided in the treated water pipe 17.

  S1 and S2 are elements constituting one detection means for detecting a defect occurring in the membrane cartridge. For example, when detecting a pressure difference, it is possible to detect a pressure difference by taking a difference between measured values of the pressure gauge S1 and the pressure gauge S2.

  In the embodiment of FIG. 1, one detection means is provided for each membrane unit 4.

  In this aspect, when any of the detection means detects the occurrence of a defect in the membrane cartridge, the membrane unit monitored by the detection means is replaced.

  In the present invention, one detection means may be provided for every two or more membrane units 4.

  FIG. 3 is a schematic diagram showing an aspect of the detection means.

  In FIG. 3, one detection means composed of elements S 1 and S 2 is provided for every two membrane units 4.

  In this aspect, when any of the detection means detects the occurrence of a malfunction of the membrane cartridge, all the membrane units monitored by the detection means are replaced.

  Although various problems such as a decrease in flux and liquid leakage can be considered as problems occurring in the membrane cartridge, pinholes are particularly required to be dealt with promptly.

  When the film treatment of ballast water is performed using a film cartridge including a spiral film having pinholes, there is a possibility that microorganisms exceeding the reference value may be mixed in the ballast water submerged in the ballast tank.

  When such a situation occurs, it is difficult to re-pump ballast water even before the departure of the port, so it is difficult to re-pump the ballast water. Carrying in the cargo becomes impossible.

  For example, when a sensor capable of detecting the particle size in the treated water is provided to detect pinholes generated in the membrane, it would be expensive to attach a sensor to each membrane cartridge. If one is attached to the whole, the membrane cartridge in which the pinhole is generated cannot be specified, and all membrane treatments must be stopped and dealt with.

  On the other hand, in the present invention, by providing a sensor for each membrane unit, the cost can be reduced as compared with the case where the sensor is attached to each membrane cartridge. In addition, the membrane cartridge other than the membrane cartridge in which the malfunction has occurred is also removed and replaced. As described above, the replacement of the membrane cartridge in which the malfunction has occurred has the highest priority, and is further pulled out. Since the membrane cartridge is only a part of all the membrane cartridges constituting the membrane treatment facility, it is possible to cope with the exchange of the membrane cartridge while maintaining the membrane treatment capability. In other words, in a membrane treatment facility for ballast water treatment, this is an extremely rational replacement method.

  In the above aspect, the case where the detection means is composed of the elements S1 and S2 is shown. However, one or more elements may be combined to form one detection means. For example, only one S1 may be provided, and the malfunction of the membrane cartridge may be detected from the absolute value of the pressure instead of the pressure difference.

  Further, for example, the occurrence of pinholes may be detected by comparing with a pressure obtained from a reference membrane unit in which no pinholes have been generated in advance.

  In addition, monitoring of defects occurring in the membrane cartridge by the detection means can be performed constantly or periodically during membrane processing.

  It is also preferable that the ballast raw water introduced by the air introduction means is sent to the membrane unit before the membrane treatment is started to form a state in which the pressure is increased, and detection is performed with improved pinhole detection sensitivity. It is.

  Further, in the present invention, when the membrane cartridge 4 is arranged side by side to constitute the membrane unit 4, a further effect can be obtained by using a unique manifold structure.

  FIG. 4 is a perspective view showing a first aspect of the manifold structure, and FIG. 5 is a cross-sectional view of a main part showing the first aspect of the manifold structure.

  In the illustrated embodiment, a first manifold 2 is provided at one end (left side in the drawing) of six membrane cartridges arranged side by side, and a second manifold 3 is provided at the other end.

  The first manifold 2 has a ballast raw water chamber 201 in a rectangular parallelepiped manifold body 200, and the ballast raw water chamber 201 includes a ballast raw water introduction port 202 that is an opening for introducing the taken ballast raw water.

  Further, the first manifold 2 includes a ballast raw water inlet 203 through which the ballast raw water can be fed to the ballast raw water flow path 103 of the membrane cartridge 1.

  The connection method of the first manifold 2 and the membrane cartridge 1 is not particularly limited as long as it is detachable. For example, a screwing method or the like is adopted, and in the illustrated example, sealing by screwing and an O-ring is adopted. The screw may be directly screwed or may be screwed using an auxiliary member.

  The connection between the ballast raw water inlet 203 and the ballast raw water flow path 103 is not particularly limited, but a direct connection is preferable because pressure loss can be reduced. For example, when the ballast raw water inlet 203 as shown in the figure is an opening provided in the side wall of the ballast raw water chamber 201, a mode in which the ballast raw water flow path 103 communicates with the opening is preferable.

  The second manifold 3 includes a washing drain chamber 301 and a treated water chamber 302 in a rectangular parallelepiped manifold body 300. The cleaning liquid discharge chamber 301 and the treatment water chamber 302 are preferably provided side by side as shown in the figure. More preferably, the cleaning discharge liquid chamber 301 is disposed in contact with the membrane cartridge 1 and the treatment water chamber is located on the side far from the membrane cartridge 1. An embodiment in which 302 is arranged is given.

  The cleaning drainage chamber 301 includes a cleaning drainage inlet 303 into which the cleaning drainage sent from the ballast raw water flow path 103 of the membrane cartridge 1 can be introduced.

  The connection between the second manifold 3 and the membrane cartridge 1 is not particularly limited as long as it is detachable. For example, a screwing method or the like is employed, and in the illustrated example, sealing by screwing and O-ring is employed. The screw may be directly screwed or may be screwed using an auxiliary member.

  The cleaning drain chamber 301 includes a cleaning drain outlet 304 on the side wall for discharging the cleaning drain in the cleaning drain chamber 301 to the outside.

  The treated water chamber 302 has a treated water introduction port 305 through which treated water can be introduced from the ballast treated water collecting pipe 100 and treated water drainage for transferring treated water in the treated water chamber 302 to a ballast tank (not shown). An outlet 306 is provided.

  The treated water chamber 302 can be provided with a discharge port 307 for discharging the cleaning waste liquid to the outside. In this case, the cleaning drainage outlet 304 is provided with a cleaning drainage discharge pipe 308, and the cleaning drainage discharge pipe 308 is connected to the outlet 307 so that the cleaning drainage in the cleaning drainage chamber 301 is discharged to the outside. it can.

  In the illustrated example, the cleaning drainage outlet 304 is provided on the side wall of the cleaning drainage chamber 301. However, the cleaning drainage chamber 301 may be provided on the upper or lower wall of the cleaning drainage chamber 301. There is no need to provide 307.

  Although the aspect of the parallel arrangement of the membrane cartridges by the manifold is not particularly limited, preferably, an aspect in which the membrane cartridges are horizontally arranged is mentioned, but a plurality of membrane cartridges may be arranged in three dimensions.

  A plurality of membrane units having the above manifold structure can be arranged side by side to perform ballast water treatment.

  Further, the manifold structure of the present invention is not limited to the embodiment shown in FIGS. 4 and 5, and may be the embodiment shown in FIGS. 6 and 7.

  FIG. 6 is a cross-sectional view of a main part showing a second aspect of the manifold structure.

  In the second mode, the first manifold 2 includes a ballast raw water chamber 201 and a treated water chamber 204 in a rectangular parallelepiped manifold body 200. The ballast raw water chamber 201 and the treated water chamber 204 are preferably provided side by side as shown in the figure. More preferably, the ballast raw water chamber 201 is disposed in contact with the membrane cartridge 1 and the treated water chamber 204 is disposed on the side far from the membrane cartridge 1. The aspect to arrange | position is mentioned.

  The ballast raw water chamber 201 includes a ballast raw water introduction port 202 that is an opening for introducing the collected ballast raw water.

  The ballast raw water chamber 201 includes a ballast raw water inlet 203 through which the ballast raw water can be fed to the ballast raw water flow path 103 of the membrane cartridge 1.

  The connection method of the first manifold 2 and the membrane cartridge 1 is not particularly limited as long as it is detachable. For example, a screwing method or the like is adopted, and in the illustrated example, sealing by screwing and an O-ring is adopted. The screw may be directly screwed or may be screwed using an auxiliary member.

  The connection between the ballast raw water inlet 203 and the ballast raw water flow path 103 is not particularly limited, but a direct connection is preferable because pressure loss can be reduced. For example, when the ballast raw water inlet 203 as shown in the figure is an opening provided in the side wall of the ballast raw water chamber 201, a mode in which the ballast raw water flow path 103 communicates with the opening is preferable.

  The treated water chamber 204 includes a treated water inlet 205 through which treated water can be introduced from the ballast treated water collecting pipe 100, and treated water drainage for transferring treated water in the treated water chamber 204 to a ballast tank (not shown). An outlet 206 is provided.

  The treated water chamber 204 can be provided with an inlet 207 for introducing the ballast raw water into the ballast raw water chamber 201. In this case, the ballast raw water introduction pipe 208 is provided in the ballast raw water introduction port 202, and the ballast raw water introduction pipe 208 is connected to the introduction port 207, whereby the ballast raw water can be introduced into the ballast raw water chamber 201.

  In the illustrated example, the ballast raw water introduction port 202 is provided on the side wall of the ballast raw water chamber 201. However, the ballast raw water chamber 201 may be provided on the upper wall or the lower wall of the ballast raw water chamber 201. There is no need to provide it.

  The second manifold 3 includes a cleaning / draining chamber 301 in a rectangular parallelepiped manifold body 300.

  The cleaning drainage chamber 301 includes a cleaning drainage inlet 303 into which the cleaning drainage sent from the ballast raw water flow path 103 of the membrane cartridge 1 can be introduced.

  The connection between the second manifold 3 and the membrane cartridge 1 is not particularly limited as long as it is detachable. For example, a screwing method or the like is employed, and in the illustrated example, sealing by screwing and O-ring is employed. The screw may be directly screwed or may be screwed using an auxiliary member.

  The cleaning drain chamber 301 includes a cleaning drain outlet 304 on the side wall for discharging the cleaning drain in the cleaning drain chamber 301 to the outside.

  FIG. 7 is a cross-sectional view of a main part showing a third aspect of the manifold structure.

  In the third mode, the first manifold 2 includes a ballast raw water chamber 201 and a first treated water chamber 204 in a rectangular parallelepiped manifold body 200. The ballast raw water chamber 201 and the first treated water chamber 204 are preferably provided side by side as shown in the figure, and more preferably, the ballast raw water chamber 201 is disposed in contact with the membrane cartridge 1 and the first is located on the side far from the membrane cartridge 1. The aspect which arrange | positions the treated water chamber 204 of this is mentioned.

  The ballast raw water chamber 201 includes a ballast raw water introduction port 202 that is an opening for introducing the collected ballast raw water.

  The ballast raw water chamber 201 includes a ballast raw water inlet 203 through which the ballast raw water can be fed to the ballast raw water flow path 103 of the membrane cartridge 1.

  The connection method of the first manifold 2 and the membrane cartridge 1 is not particularly limited as long as it is detachable. For example, a screwing method or the like is adopted, and in the illustrated example, sealing by screwing and an O-ring is adopted. The screw may be directly screwed or may be screwed using an auxiliary member.

  The connection between the ballast raw water inlet 203 and the ballast raw water flow path 103 is not particularly limited, but a direct connection is preferable because pressure loss can be reduced. For example, when the ballast raw water inlet 203 as shown in the figure is an opening provided in the side wall of the ballast raw water chamber 201, a mode in which the ballast raw water flow path 103 communicates with the opening is preferable.

  The first treated water chamber 204 transfers the treated water introduction port 205 into which treated water can be introduced from the ballast treated water collecting pipe 100 and the treated water in the first treated water chamber 204 to a ballast tank (not shown). A treated water discharge port 206 is provided.

  The first treated water chamber 204 can be provided with an inlet 207 for introducing the ballast raw water into the ballast raw water chamber 201. In this case, the ballast raw water introduction pipe 208 is provided in the ballast raw water introduction port 202, and the ballast raw water introduction pipe 208 is connected to the introduction port 207, whereby the ballast raw water can be introduced into the ballast raw water chamber 201.

  In the illustrated example, the ballast raw water introduction port 202 is provided on the side wall of the ballast raw water chamber 201. However, the ballast raw water chamber 201 may be provided on the upper wall or the lower wall of the ballast raw water chamber 201. There is no need to provide it.

  The second manifold 3 includes a washing drain chamber 301 and a second treated water chamber 302 in a rectangular parallelepiped manifold body 300. The cleaning drain chamber 301 and the second treated water chamber 302 are preferably provided side by side as shown in the figure, and more preferably, the cleaning drain chamber 301 is disposed in contact with the membrane cartridge 1 and on the side far from the membrane cartridge 1. A mode in which the second treated water chamber 302 is disposed is exemplified.

  The cleaning drainage chamber 301 includes a cleaning drainage inlet 303 into which the cleaning drainage sent from the ballast raw water flow path 103 of the membrane cartridge 1 can be introduced.

  The connection between the second manifold 3 and the membrane cartridge 1 is not particularly limited as long as it is detachable. For example, a screwing method or the like is employed, and in the illustrated example, sealing by screwing and O-ring is employed. The screw may be directly screwed or may be screwed using an auxiliary member.

  The cleaning drain chamber 301 includes a cleaning drain outlet 304 on the side wall for discharging the cleaning drain in the cleaning drain chamber 301 to the outside.

  The second treated water chamber 302 transfers the treated water introduction port 305 into which treated water can be introduced from the ballast treated water collecting pipe 100 and the treated water in the second treated water chamber 302 to a ballast tank (not shown). A treated water discharge port 306 is provided.

  The second treated water chamber 302 can be provided with a discharge port 307 for discharging the cleaning waste liquid to the outside. In this case, the cleaning drainage outlet 304 is provided with a cleaning drainage discharge pipe 308, and the cleaning drainage discharge pipe 308 is connected to the outlet 307 so that the cleaning drainage in the cleaning drainage chamber 301 is discharged to the outside. it can.

  In the illustrated example, the cleaning drainage outlet 304 is provided on the side wall of the cleaning drainage chamber 301. However, the cleaning drainage chamber 301 may be provided on the upper or lower wall of the cleaning drainage chamber 301. There is no need to provide 307.

  According to the third aspect, the first manifold 2 and the second manifold 3 can be made the same component, and the device can be easily molded.

  By having the above manifold structure, the number of pipes is significantly larger than the case where a plurality of membrane cartridges are individually connected to the header pipes by pipes as disclosed in Patent Document 6. Reduced. For example, when six membrane cartridges are connected by the manifold structure of the present invention, the number of pipes is reduced to 1/6.

  Therefore, when the membrane cartridge is replaced, the number of pipes to be disconnected for extracting the membrane cartridge is greatly reduced, so that a quick replacement is possible. In addition, the cost required for installing the piping is greatly reduced.

  A membrane unit assembly is formed by detachably arranging the membrane units having the manifold structure according to the first to third aspects described above, thereby securing a working space when replacing the defective membrane cartridge. However, the overall equipment cost can be further suppressed, and the membrane cartridge can be replaced in a shorter time. This will be described with reference to FIG.

  FIG. 8 is an explanatory view showing an aspect of a membrane treatment facility for ballast water treatment.

  In FIG. 8, 4 is a membrane unit having the above manifold structure, and 5 is a membrane unit assembly in which the membrane units 4 are detachably arranged in parallel.

  Each membrane unit 4 is placed in a shelf shape with the lower walls of the first manifold 2 and the second manifold 3 formed in a rectangular parallelepiped shape contacting the membrane unit placement site. In each membrane unit 4, the membrane cartridge 1 is present with both ends supported by the manifold.

  Further, the raw ballast water introduction port 202, the treated water discharge port 306, and the (cleaning drainage) discharge port 307 included in each membrane unit 4 are the ballast raw water header pipe 12a, the treated water header pipe 17a, and the washing drain, respectively. The liquid header pipe 14a is detachably connected by a connecting portion. As an example of making it detachable, there is a configuration in which the connection is made by an extendable connection pipe.

  By housing the membrane unit 4 in the membrane unit assembly 5 so as to be removable, the membrane unit 4 can be pulled out of the membrane unit assembly 5.

  Sliding means such as a roller or a caster can be provided on the lower surface of each manifold portion formed in a rectangular parallelepiped shape, which facilitates drawing in the horizontal direction. A rail may be provided on the surface on which the membrane unit 4 is placed, and the sliding means may be engaged with the rail. The rail formation direction can be set as appropriate in accordance with the pulling direction.

  The membrane unit mounting portion may be a skeleton formed by an angle such as an L shape, or may be an upper wall of a manifold included in another membrane unit.

  The treated water pipe 17 is connected to a treated water discharge port 306 having a manifold structure, and the cleaning drainage discharge pipe 14 is connected to a discharge port 307 having a manifold structure.

  With the membrane unit assembly having the above-described configuration, even when a large number of membrane units are provided, the extraction work when extracting the membrane cartridge buried in the back is very efficient.

  In addition, when replacing the membrane unit containing the target membrane cartridge, the surrounding membrane units can be easily pulled out to secure a working space, so there is no need to secure the working space in advance, and the membrane cartridges are arranged side by side. It can save space.

  Next, FIG. 9 to FIG. 11 illustrate aspects of the membrane unit assembly.

  In FIG. 9, the membrane unit assembly 5 is formed by orienting the membrane units 4 so that the surfaces formed by the membrane cartridges 1 arranged in parallel are horizontal.

  In this aspect, it is preferable that the drawing direction of the membrane unit is the parallel direction (a1) of the membrane cartridges or the direction (a2) perpendicular to the surface formed by the parallel membrane cartridges 1 formed.

  In FIG. 10, the membrane unit assembly 5 is formed by orienting the membrane units 4 so that the parallel arrangement direction of the membrane cartridges 1 is vertical.

  In this embodiment, it is preferable that the drawing direction of the membrane unit is the direction in which the membrane cartridges are arranged (b1) or the direction perpendicular to the surface formed by the membrane cartridges 1 arranged in parallel (b2).

  In FIG. 11, the membrane unit assembly 5 is formed by orienting the membrane units 4 so that the longitudinal direction of the membrane cartridge 1 is in the vertical direction.

  In this aspect, it is preferable that the drawing direction of the membrane unit is the direction in which the membrane cartridges are arranged (c1) or the direction perpendicular to the surface formed by the membrane cartridges 1 arranged in parallel (c2).

  In any of the above-described embodiments, the membrane unit has a rectangular parallelepiped manifold at both ends thereof, so that the manifold can accurately arrange each membrane unit and can be easily arranged in a dense state. .

  With the above configuration, a plurality of membrane cartridges 1 are unitized to form a membrane unit 4, and further, the membrane unit assembly 5 is formed in multiple stages to further reduce the space. Figured. Further, since the plurality of membrane cartridges 1 are arranged in parallel by the manifold, it becomes possible to process a large amount of ballast water at the same time, and the processing speed is increased.

  Further, the ballast raw water introduction port 202, the treated water discharge port 306, and the (cleaning drainage) discharge port 307 included in each membrane unit are respectively connected to the ballast raw water header pipe 12, the treated water header pipe 17a, and the cleaning drainage liquid. By connecting the header pipe 14a with a connecting portion having an opening / closing valve, it is possible to close only the opening / closing valve of the membrane unit to be pulled out and continue the operation of the other membrane units.

  An installation example of the above-described detection means in the membrane unit assembly having the above configuration will be described with reference to FIGS.

  FIG. 12 is a schematic view showing an example in which a detector is provided for each header pipe connecting a plurality of membrane units.

  In FIG. 12, 12a is a raw ballast water header pipe, and 17a is a treated water header pipe, each connecting three membrane units 4 arranged in parallel in the horizontal direction.

  FIG. 13 is a schematic view showing another example in which a detector is provided for each header pipe connecting a plurality of membrane units.

  In FIG. 13, 12a is a ballast raw water header pipe, and 17a is a treated water header pipe, each connecting three membrane units 4 arranged in parallel in the vertical direction.

  In both figures, S1 and S2 are pressure gauges used as pinhole detectors, one for each of the header tubes 12a and 17a, and before and after the spiral membrane provided in the membrane cartridge arranged in parallel. It is configured to detect the occurrence of pinholes from the pressure difference.

  Only S1 may be provided, and the occurrence of pinholes may be detected from the absolute value of the pressure instead of the pressure difference.

  Further, the occurrence of pinholes may be detected by comparing with a pressure obtained from a reference membrane unit in which no pinholes have been generated in advance.

  With the above configuration, it is possible to constantly or periodically monitor defects occurring in the membrane cartridge during the membrane treatment.

  It is also preferable that the ballast raw water introduced by the air introduction means is sent to the membrane unit before the membrane treatment is started to form a state in which the pressure is increased, and detection is performed with improved pinhole detection sensitivity. It is.

  In the embodiment of FIG. 12, when the occurrence of a pinhole is confirmed in any header pipe, it is preferable to pull out all the membrane units connected to the header pipe in the drawing direction a1 shown in FIG.

  In addition, in the embodiment of FIG. 13, when the occurrence of a pinhole is confirmed in any header pipe, all the membrane units connected to the header pipe can be drawn in the drawing direction a2 shown in FIG. preferable.

  As a result, the membrane cartridge other than the membrane cartridge in which the malfunction has occurred is also removed and replaced. Since the membrane cartridge to be used is only a part of all the membrane cartridges constituting the membrane treatment facility, the membrane treatment facility for ballast water treatment is extremely suitable.

1: Membrane cartridge 100: Ballast-treated water collecting pipe 101: Envelope-like membrane (spiral membrane)
102: Support 103: Ballast raw water flow path 2: First manifold 201: Ballast raw water chamber 202: Ballast raw water inlet 203: Ballast raw water inlet 204: Treated water chamber 205: Treated water inlet 206: Treated water outlet 207: Introduction port 208: Raw ballast water introduction pipe 3: Second manifold 301: Cleaning drainage chamber 302: Treatment water chamber 303: Cleaning drainage introduction port 304: Cleaning drainage outlet 305: Treatment water introduction port 306: Treatment water discharge port 307 : Discharge port 4: Membrane unit 5: Membrane unit aggregate 10: Ballast raw water 11: Ballast pump 12: Ballast raw water suction pipe 13: On-off valve 14: Ballast raw water discharge pipe (cleaning drainage discharge pipe)
15: On-off valve 16: Ballast tank 17: Treated water pipe 18: On-off valve

Claims (1)

Membrane treatment for ballast water treatment is provided with the number of membrane cartridges in which membrane modules are loaded in the ballast tank as required to fill the ballast tank with treated water, and raw water is supplied to the membrane cartridge to obtain treated water. A method for replacing a membrane cartridge used in equipment,
A plurality of membrane units that connect a common manifold across the plurality of membrane cartridges and supply raw ballast water to each of the membrane cartridges and take out treated water from each of the membrane cartridges via the manifold. And comprises a membrane unit assembly in which each of the membrane units is detachably assembled, and provided with detection means for detecting a malfunction of the membrane cartridge for each of the one or more membrane units,
The detection means, after a malfunction in any of the film cartridge which constitutes one or more of the film unit has detected that it has generated, the Kimaku unit before including the membrane cartridge a problem occurs, the membrane A method for replacing a membrane cartridge used in a membrane treatment facility for ballast water treatment, wherein the membrane unit is pulled out from the unit assembly and exchanged together.

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