Manaqement of Water Ballast in Marine vessels
This invention relates to the management of water ballast in marine
vessels, particularly for the purpose of limiting the transportation of viable bio-
matter between habitats.
It is now recognised that the discharge of water ballast from marine
vessels is a source of bio-contamination of marine and sometimes fresh water
habits by the introduction of species to foreign environments. This poses a substantial ecological threat, as introduced species can proliferate at the
expense of existing species, or produce vigorous hybrids with local similar species which disturb the balance of the ecology adversely.
This problem is being increasingly recognised, and is summarised in the UNDP and International Marine Organisation leaflet "Stopping the Ballast Water
Stowaway" (March 2001). The program will result in international agreements,
and national legislation which will regulate the discharge of water ballast with the
objective of effectively reducing or preventing the accidental introduction of
invasive species.
Accordingly, it is desirable to be able to provide an effective method and
apparatus for management of water ballast in marine vessels which can meet this objective, and which is not unduly burdensome on ship operators.
Marine organisms almost all have a life cycle stage where they form part
of the zoo-plankton, as larvae or eggs for example. Filtration, however, is not a
viable method of eliminating this material as the pressure drop across a filter
medium having a pore size sufficiently small to trap the smallest plankton, such
as eggs, leads to a significant slowing of the intake and/or discharge of water to
or from the ballast tanks, and in addition, the filter elements must be cleared by
removal of filtrate and are also vulnerable to bio-encrustation. It is thus necessary to consider non-mechanical methods of eliminating
viable marine organisms from ballast water and it is an object of the invention to
provide a method and apparatus for management of ballast water in marine
vessels which will effectively eliminate, or substantially reduce contamination of
ballast water discharges by viable marine organisms. Treatment with
hypochlorite is effective, but handling the material such as avoiding contact with
acids, whilst well understood, places a burden on operators and runs the risks of'
damage or casualties should there be any failure. An object of the invention is
to provide a safer alternative to the use hypochlorite.
In accordance with the invention, a method of management of ballast
water in marine vessels includes the steps of admitting ballast water to one or more ballast tanks, subjecting the ballast water during admission to the tank or
tanks to a concentration of metal ions in the water sufficient to render a
significant proportion of marine organisms non-viable, containing the water in
the tanks as required and discharging the ballast water with marine organisms
present in non-viable forms.
The invention also provides apparatus for management of ballast water in
marine vessels comprising one or more ballast tanks in a marine vessel, means
for admitting ballast water to each of the ballast tanks, means for subjecting the ballast water during admission to the tank or tanks to attain a concentration of
ions in the water sufficient to render a significant proportion of marine
organisms non-viable, and means for discharging the ballast water from the tank
or tanks with marine organisms present in non-viable forms.
The metal ions provided in the ballast water to render marine organisms
non-viable are preferably copper. The copper ions may be maintained at a
concentration in the water of from 2 micro grams per litre to 100 micro grams per
litre, preferably up to 45 micro grams per litre.
The copper ions may be released into the water in each ballast tank from
a copper device which is immersed in the ballast water.
The current impressed on the copper alloy anodes is preferably controlled
so as to attain a concentration of copper ions in the ballast water within the range of 2 micro grams per litre to 100 micro grams per litre, preferably up to 45
micro grams per litre. A control circuit may be provided to vary current applied
to the anodes to increase or reduce the output of copper ions in direct proportion
to the level of current applied.
The means for admitting ballast water to the ballast tanks, and for
discharging ballast water from the tanks may comprise inlet and outlet ports in
the hull of the vessel, which are preferably dual purpose , with a coarse screen
cover to prevent ingress of large particle size floating or swimming matter or
organisms, conduits connecting the inlet and outlet ports to the ballast tanks,
and pumps for impelling the ballast water to fill or empty the ballast tanks.
The copper ion concentration maintained in the ballast tanks is such that
whilst a significant proportion of marine organisms in the tanks are rendered
non-viable (that is either killed, or prevented from growing or reproducing) on
discharge of the ballast water, the concentration will be diluted well below
hazardous levels in the wider marine environment, and also the ions will be
quickly neutralised and thus reduced in effectiveness as a poison.
A preferred method and embodiment of apparatus according to the
invention for management of ballast water in marine vessels will now be
described by way of example, with reference to the accompanying, wherein:-
Figure 1. is a sectional view of a marine cargo vessel;
Figure 2. is a diagram showing the general arrangement of a ballast tank
equipped with means according to the invention.
As shown in Figure 1. , a marine cargo vessel 10 has a hull 11 divided by
internal bulkheads into spaces such as a cargo hold 12, propeller shaft tunnel
13, and ballast tanks 14 in the lower part of the hull. Ballast tanks 14 are
arranged to be filled and discharged by conduits 15 with pumps 16 opening to
the underwater environment at 17. These openings are closed by mesh grills in
the usual way to exclude large sized water borne matter and fish.
As shown in Figure 2., each ballast tank 14 has an inlet conduit 15, an
overflow conduit 18, and an inspection access 19. The top of the tank 14 is
closed by a cover 20, through which protrude an array of electrodes, in the form
of copper or copper-clad anodes 21. These are connected to a controller 23
which controls the current supplied to the electrodes in order to attain a
preferred optimum concentration of copper ions in the ballast water during
admission to the tank. A combination of CU+ or CU++ ions is preferably in the range of 2 micro
grams per litre to 100 micro grams per litre, for example about 45 micro grams
per litre. This is sufficient to render a significant proportion of marine organisms
such as algae, larvae, eggs, mirco organisms and other plankton non viable, in
the sense that they either killed or rendered incapable of further development -
ie. eggs will not hatch, nor larvae proceed to the adult stage, or adult organisms
are effectively sterilised. It is to be noted that it is unlikely that even the most
effective biocide will render 100% of all organisms non-viable in every trial.
Typical results in various circumstances range from about half, to well over 90%.
This copper ion concentration is attained at the time of admission of the
ballast water to the tank, to provide a once and for all dose to render bio matter
non viable. The ion concentration can then be allowed to decline, to render eventual discharge low enough in toxcity to meet environmental standards.
By use of this method, it is possible to meet current and expected future
requirements for preventing contamination of environments by accidental
introduction of invasive species from marine vessel ballast water.
The levels of copper ions in discharged ballast water is well below levels
considered to represent even a low level risk, so that the method can be used
repeatedly to prevent invasion by foreign species.
The method is applicable not only to use with sea water, but also with
fresh water such as might be taken in on the American great lakes, or inland
ship canals.
Details of the electrode materials are set out below: -
Anode Materials:
Copper: 99.9% pure electrolytic copper C101 as taken from BS2874 C101
ELECTRICALLY TOUGH PITCH HIGH CONDUCTIVITY COPPER.
Chemical Composition
COPPER (Sliver being counted as copper); Not less than 99.09%
Last 0.01% are called impurities. The British standard states the material must
not contain impurities in excess of the amounts stated for:
BISMUTH Not more than 0.0010%
LEAD Not more than 0.005%
TOTAL (Excluding Sliver SOxygen) Not more than 0.03%