1.1 In the adoption of the International Convention
for the Control and Management of Ships' Ballast Water and Sediments,
2004 (BWM Convention), Member States of the
International Maritime Organization (IMO) made a clear commitment
to minimizing the transfer of invasive aquatic species by shipping.
Studies have shown that biofouling can also be a significant vector
for the transfer of invasive aquatic species. Biofouling on ships
entering the waters of States may result in the establishment of invasive
aquatic species which may pose threats to human, animal and plant
life, economic and cultural activities and the aquatic environment.
1.2 While the International Convention on the
Control of Harmful Anti-Fouling Systems on Ships, 2001 (AFS
Convention) addresses anti-fouling systems on ships, its focus
is on the prevention of adverse impacts from the use of anti-fouling
systems and the biocides they may contain, rather than preventing
the transfer of invasive aquatic species.
1.3 The potential for invasive aquatic species
transferred through biofouling to cause harm has been recognized by
the IMO, the Convention on Biological Diversity (CBD), several UNEP
Regional Seas Conventions (e.g., Barcelona Convention for the Protection
of the Mediterranean Sea Against Pollution), the Asia Pacific Economic
Cooperation forum (APEC), and the Secretariat of the Pacific Region
Environmental Program (SPREP).
1.4 All ships have some degree of biofouling,
even those which may have been recently cleaned or had a new application
of an anti-fouling coating system. Studies have shown that the biofouling
process begins within the first few hours of a ship's immersion in
water. The biofouling that may be found on a ship is influenced by
a range of factors, such as follows:
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.1 design and construction, particularly the number,
location and design of niche areas;
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.2 specific operating profile, including factors
such as operating speeds, ratio of time underway compared with time
alongside, moored or at anchor, and where the ship is located when
not in use (e.g., open anchorage or estuarine port);
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.3 places visited and trading routes; and
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.4 maintenance history, including: the type, age
and condition of any anti-fouling coating system, installation and
operation of anti-fouling systems and dry-docking/slipping and hull
cleaning practices.
1.5 Implementing practices to control and manage
biofouling can greatly assist in reducing the risk of the transfer
of invasive aquatic species. Such management practices can also improve
a ship's hydrodynamic performance and can be effective tools in enhancing
energy efficiency and reducing air emissions from ships. This concept
has been identified by the IMO in the "Guidance for the development
of a ship energy efficiency management plan (SEEMP)" (MEPC.1/Circ.683).
1.6 These Guidelines for the control and management
of ships' biofouling to minimize the transfer of invasive aquatic
species (hereafter "the Guidelines") are intended to provide a globally
consistent approach to the management of biofouling. As scientific
and technological advances are made, the Guidelines will be refined
to enable the risk to be more adequately addressed. Port States, flag
States, coastal States and other parties that can assist in mitigating
the problems associated with biofouling should exercise due diligence
to implement the Guidelines to the maximum extent possible.