The present invention relates to ballast water utilization systems, and more particularly to a utilization system of ballast water that can be used as various types of utility water.
A cargo ship transporting crude oil or the like has a ballast tank in order to keep the stability of a hull during navigation.
Usually, when the ship is not loaded with crude oil or the like, the ballast tank is filled with ballast water, and the ballast water is discharged when crude oil or the like is loaded into the ship.
The ballast water is water required for safe navigation of the ship, and seawater at a port where cargo handling is carried out is usually used. The amount thereof is estimated to be 3 to 4 billion tons per year on the worldwide basis.
In the ballast water, aquatic organisms living in a port from which the water was taken are mixed, and the aquatic organisms are also transported to foreign countries with the movement of the ship. Therefore, the destruction of an ecological system caused as a result of an organism species which do not originally live in a sea area replacing an existing organism species is getting serious.
Against this background, at a diplomatic conference of the International Maritime Organization (IMO), the Convention for the Control and Management of Ships' Ballast Water and Sediments has been adopted, and an obligation to manage ballast water by using a ballast water treatment apparatus is scheduled to be applied to a ship constructed in 2009 and after.
Also, a ballast-water discharge standard is specified by the above Convention as shown in the table below:
Escherichia coli
cholerae (01, 0189)
Enterococcus
It is against this background that the need to develop a ballast water sterilization/bacterial eradication technology that can solve the above problem has become urgent.
As the ballast water sterilization/bacterial eradication technology, an ozone-based chemical method (Patent Document 1), filtration treatment (Patent Document 2), membrane treatment (Patent Document 3), a buffer tank that brings a pump into operation (Patent Document 4), and the like, are conventionally known.
Patent Document 1 proposes a technology for performing sterilization by injecting ozone into ballast water in conjunction with an injection of steam while reducing ozone usage by turning the ozone into microscopic bubbles and thereby promoting the generation of hydroxyl radicals. However, the reduction of ozone usage has its limit.
The filtration treatment and membrane treatment described in Patent Documents 2 and 3 require cleaning of an apparatus to continue operation for long periods.
However, the problem is that, to maintain the safety of navigation of a ship, the ballast water such as seawater or freshwater introduced into the ballast tank cannot be used for other uses.
Therefore, an object of the present invention is to provide a utilization system of ballast water that can secure cleaning water for cleaning an apparatus and be used for various uses.
Other objects of the present invention will become apparent from the following description.
The invention according to claim 1 is a ballast water utilization system including: a ballast water treatment apparatus which is an apparatus for treating microorganisms or bacteria in seawater or freshwater and requires cleaning at least once a day while treatment is continuously performed; and a ballast tank storing ballast water treated by the ballast water treatment apparatus, wherein a service tank storing ballast treated water treated by the ballast water treatment apparatus is provided, and the ballast treated water in the service tank is made available for cleaning of the ballast water treatment apparatus.
The invention according to claim 2 is the ballast water utilization system according to claim 1, wherein the ballast water treatment apparatus is a filtering apparatus separating and removing microorganisms and bacteria or a treatment apparatus using mechanical shear.
The invention according to claim 3 is the ballast water utilization system according to claim 1, wherein the ballast water treatment apparatus includes a filtering apparatus separating and removing microorganisms and bacteria and a sterilizing apparatus placed in the following stage of the filtering apparatus and performing sterilization by using a bactericide or ultraviolet light.
The invention according to claim 4 is the ballast water utilization system according to claim 1, wherein the ballast water treatment apparatus includes a treatment apparatus using mechanical shear and a sterilizing apparatus placed in the following stage of the treatment apparatus and performing sterilization by using a bactericide or ultraviolet light.
The invention according to claim 5 is the ballast water utilization system according to claim 3 or 4, wherein the ballast treated water in the service tank is used as water to dilute a bactericide used in the sterilizing apparatus performing sterilization by using a bactericide.
The invention according to claim 6 is the ballast water utilization system according to any one of claims 1 to 5, wherein the ballast treated water in the service tank is introduced into a reverse osmosis membrane treatment apparatus to produce drinking water or reclaimed water.
According to the present invention, it is possible to provide a utilization system of ballast water that can secure cleaning water for cleaning an apparatus and be used for various uses.
Hereinafter, an embodiment of the present invention will be explained by using the drawings.
3 denotes a ballast water treatment apparatus which is an apparatus for treating microorganisms or bacteria in seawater or freshwater and requires cleaning at least once a day while treatment is continuously performed.
4 denotes a ballast tank for storing ballast treated water treated by the ballast water treatment apparatus 3.
5 denotes a service tank for storing ballast water treated by the ballast water treatment apparatus 3. It is preferable that the service tank 5 be filled with water by conveying the ballast treated water to the service tank 5 after the ballast tank 4 is filled with the ballast water or in the course of filling the ballast tank therewith.
One service tank 5 may be provided when it is large in capacity, or a plurality of service tanks 5 may be provided when they are small in capacity.
Moreover, the service tank 5 may be formed into any one of a cylindrical shape and a rectangular shape by using normal resin or an anticorrosion steel plate (such as SUS). When a certain space cannot be secured on the ship, a container formed of a flexible material is also preferable. Examples of the service tank formed of a flexible material include, for example, a resin film, a cloth sack or reinforced fiber cloth sack lined with rubber.
6 denotes a pipe for supplying cleaning water to the ballast water treatment apparatus 3. In the present invention, as mentioned above, the ballast water treatment apparatus 3 requires cleaning at least once a day while treatment is continuously performed.
Therefore, the ballast treated water in the service tank 5 is supplied to the ballast water treatment apparatus 3 as the cleaning water.
The ballast water such as seawater or freshwater introduced into the ballast tank cannot be used for uses other than for the safety of navigation of a ship. That is, if such ballast water is used, the ship is at risk of losing a balance and capsizing. For this reason, the need for the service tank 5 in accordance with the present invention arises, and the service tank 5 fulfills an important function. In the past, there was no concept of such a service tank.
In the present invention, it is preferable that the ballast water treatment apparatus 3 be a filtering apparatus 30 separating and removing microorganisms and bacteria as shown in (A) of
Examples of the filtering apparatus 30 separating and removing microorganisms and bacteria include a filtering apparatus using a filtering medium and a membrane filtering apparatus.
With such a membrane treatment apparatus, it is possible to separate and remove microorganisms and bacteria having a size equal to or greater than a pore size of the membrane.
Examples of the membrane filtering apparatus include membrane treatment apparatuses using a filtration membrane (for example, a microfiltration membrane). These membrane treatment apparatuses require membrane cleaning after performing filtration for a predetermined time period because the membrane gets clogged as the treatment continues.
Furthermore, as another preferred embodiment of the present invention, it is preferable that the ballast water treatment apparatus 3 be composed of, as shown in (C) of
Examples of the sterilizing apparatus 32 performing sterilization by using a bactericide or ultraviolet light include a sterilizing apparatus using a bactericide such as chlorine or hypochlorous acid or a photooxidation treatment apparatus using an ultraviolet lamp.
It is also preferable that a bactericide and ultraviolet light be used in combination.
The sterilizing apparatus using a bactericide needs dilution water for adjusting the concentration of a bactericide to a predetermined concentration. In the present invention, it is preferable to use the ballast treated water in the service tank as such dilution water. Also in this case, the ballast water in the ballast tank cannot be used for the reason described above.
Incidentally, when an ultraviolet lamp is used, it is also preferable to use the ballast treated water in the service tank for cleaning the ultraviolet lamp.
The shear treatment apparatus 31 using mechanical shear is formed as a tubular body 310, as shown in
In the invention, it is preferable that the ballast water treatment apparatus 3 be composed of, as shown in (D) of
Incidentally, it is also preferable to place a membrane treatment apparatus using a filtration membrane in the following stage of the treatment apparatus 31 using mechanical shear.
The above-mentioned shear treatment apparatus 31 also requires removal of microorganisms or the like lodged in the pores 311 by cleaning after a lapse of a predetermined time period. Therefore, in the present invention, it is important to use the ballast treated water in the service tank as cleaning water for that purpose as described above. This is a nonconventional idea.
Up to this point, the preferred ballast water treatment apparatuses of the present invention have been explained. In addition to those described above, the preferred embodiments include electrolytic treatment and ion-exchange membrane treatment. These embodiments can be adopted alone or in combination with membrane treatment or shear treatment.
Furthermore, in the present invention, though not illustrated, introducing the ballast treated water in the service tank 5 into a reverse osmosis membrane treatment apparatus and treating the ballast treated water to produce drinking water or reclaimed water is also a preferred embodiment.
Incidentally, in
Other various uses include securing of reclaimed water in the ship, securing of deck cleaning water, and the use of the ballast treated water as water to produce hypochlorous acid.
This embodiment includes a pipe 8 for transferring the ballast water stored in the ballast tank 4 to the service tank 5 with a transfer pump 9.
Therefore, it is possible to transfer the ballast water in the ballast tank 4 which is no longer required at the time of loading of a new cargo, for example, to the service tank 5 via the pipe 8. The ballast water in the ballast tank 4 is clean ballast treated water treated by the ballast water treatment apparatus 3.
As a result, at the time of discharge of ballast water or after discharge thereof, even when ballast treated water is needed for making it available for various uses when the ballast treated water in the service tank 5 is used and is getting low or the service tank is emptied, transferring the ballast water in the ballast tank 4 to the service tank 5 via the pipe 8 eliminates the need to pump new ballast water with the ballast pump 2 and treat it by the ballast water treatment apparatus 3. This makes it possible to make the ballast treated water in the service tank 5 available for use promptly.
Moreover, as also shown in
Filing Document | Filing Date | Country | Kind | 371c Date |
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PCT/JP2007/059534 | 5/8/2007 | WO | 00 | 10/13/2009 |