4 Identification of the region to be covered
by a RRFP – For the purposes of an RRFP, a region should
include the participating States and the ports that will be covered
by the plan. A map should be provided, clearly showing the participating
States and all ports within the region. The majority of States participating
in an RRFP should be Small Island Developing States (SIDS). Although
non-SIDS may participate, they should do so only so far as their ports
may be Regional Waste Reception Centres. The obligations of non-SIDS
to provide adequate reception facilities in all ports and terminals
will not be satisfied by RA.
5
Identification of the nature of the unique
circumstances that impact on the ability to provide adequate port
reception facilities – A clear understanding of such
unique circumstances will lead to a logical approach to designing
RA that most efficiently address those circumstances. Generally, such
circumstances will include practical difficulties on the part of a
State to manage its own domestic waste, or a disproportionate additional
burden from ships to the domestic waste stream. Distances between
ports and suitable waste processing facilities may result in unacceptable
costs for transport which may increase the risk of inappropriate treatment.
A State's small geographical size may limit the space available to
process or dispose of ship generated wastes and cargo residues, as
may geomorphology (for example high water table or unstable land areas
on low lying islands). A small population may limit the ability to
provide staff to receive and process ship generated wastes and cargo
residues at times convenient to ships. In addition to these examples,
other unique circumstances may be present and should be fully described
in the RRFP.
6 In demonstrating a compelling need for RA, alternatives
should be explored, costed and assessed in terms of their environmental
risk. For example, it may be relatively efficient to receive ship
generated wastes and cargo residues in every port, temporarily store
it and transport it to a central treatment plant for processing, while
being sure to comply with applicable international law on the transboundary
movement of hazardous wastes. The cost of such storage, transport
and central processing may be less than providing comprehensive processing
of ship generated wastes and cargo residues in the vicinity of every
port, and may be more easily funded and/or recovered from port users.
However, in some regions, the cost of transport may still be prohibitive
and the environmental risk associated with the transport of the ship
generated wastes and cargo residues may be unacceptable.
7 Note that RA are not intended as a quick solution
for short-term problems (e.g. where an individual port has a temporary
inability to provide adequate port reception facilities due to equipment
breakdown, industrial action, severe weather etc.). RA is intended
for ports where the practicality of providing port reception facilities
is likely to be challenging for the foreseeable future. A clear understanding
of the unique circumstances will also help to identify the areas or
issues that may be able to be tackled in the long term to enhance
the provision of port reception facilities throughout the region.
8
Context for RA within a broader approach
to waste management and implementation of MARPOL – RA
should be designed to complement other strategies to improving management
of ship generated wastes and cargo residues within a region. It should
be clearly understood and documented how RA will contribute to efforts
to improve the ability of a State to effectively fulfil its obligations
under MARPOL, or to accede to MARPOL where a State is not already
a Party. Parties proposing RA should ensure that such arrangements
would be suited to the vessels calling at ports within the region
and would not encourage any illegal discharge into the sea.
9
International and domestic shipping and
the needs of ships operating in the region to discharge ship generated
wastes and cargo residues – Understanding shipping patterns
is important to assessing the demand for port reception facilities
in a region and in individual ports. The ships calling at each port
within a region should be quantified, as well as the existing number
of requests for reception of various types of ship generated wastes
and cargo residues. Advice on how to approach this task is given in
several IMO documents and publications.footnote
10 The types of ships operating in a region should
be carefully identified as certain ship types generate particular
waste streams and/or are subject to specific ship generated wastes
and cargo residues management requirements. For example:
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oil and chemical tankers – cargo slops from tankers
can reach large volumes with high water content compared to other
types of ships' generated wastes which is generally more concentrated;
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oil tankers of less than 150 gross tonnage – in most
cases these ships are required to retain all oil on board;
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fishing vessels – damaged or otherwise decommissioned
fishing gear can be bulky and contaminated with target and non-target
species, including invasive aquatic species and fouling organisms;
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passenger vessels – these generally have larger volumes
of garbage and sewage compared to the general merchant fleet; and
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recreational vessels – may lack or have limited pollution
prevention equipment, for example smaller holding tanks and garbage
storage areas, basic or no sewage treatment, no bilge water treatment.
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11 For a successful regional approach, it is also
important to understand the overall voyage pattern of ships calling
at ports in the region. Therefore, an RRFP should take account of
routes and ports of call, including origin and destination outside
the region. A ship should not need to deviate from its route for the
sole purpose of accessing port reception facilities. Aspects of routing
and voyage planning that might affect the amount of ship generated
wastes and cargo residues on board ships arriving in a particular
region or port, and/or the need to clear ship generated wastes and
cargo residues storage spaces prior to the onward journey, include:
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voyage through a Special Area where certain ship generated
wastes and cargo residues may not be allowed to be discharged into
the sea;
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voyage through a Particularly Sensitive Sea Area where
associated protective measures include additional discharge restrictions;
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periods of anchorage prior to entering a port, during which
ship generated wastes and cargo residues may accumulate on board;
and
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average times spent in each port, which may provide greater
or lesser opportunities to discharge ship generated wastes and cargo
residues.
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12
Additional considerations –
There may be other factors that influence the demand for port reception
facilities in a region or a particular port. For example, quarantine
requirements within a region, in a particular port, or at the onward
destination, may necessitate particular means of waste handling on
board and/or in port (e.g. compulsory discharge to shore, incineration
requirements, cleaning or disinfection, fumigation). Increased shipboard
collection and segregation of recyclable and reusable materials may
also influence demand for port reception facilities.
13
All ports in the region, including type
and available facilities – The RRFP should contain a
thorough assessment of the port reception facilities at all ports
and terminals within the region. Several IMO documents and publications
provide detailed information on what constitutes adequate facilities
and how adequacy can be assessed. An assessment should also be made
of any opportunities to provide adequate port reception facilities
where such facilities are not already available.
14
Identification of the selected Regional
Ships Waste Reception Centres (RSWRC) – Based on the
foregoing assessments and considerations, an RRFP should identify
which ports would be Regional Ships Waste Reception Centres (RSWRC).
In general, these should be the ports where facilities are adequate
to receive all types of ship generated wastes and cargo residues,
including any ship generated wastes and cargo residues remaining on
board a ship that has visited a port within the region where ship
generated wastes and cargo residues cannot be delivered. RSWRCs should
be located so as to be convenient according to the prevailing shipping
patterns. This means that ships should not be forced to deviate from
their voyage for the sole purpose of delivering ship generated wastes
and cargo residues to shore. RSWRCs should be located so that ships
can deliver ship generated wastes and cargo residues during normal
port visits – that is, where the ship would otherwise have visited
for the purposes of unloading, loading, provisioning or lay-up.
15
Identification of ports with limited
facilities (PLF) – Based on the foregoing assessments,
an RRFP should identify which ports have limited facilities (PLF).
16
Identification of a central point of
contact – A central point of contact should be identified
in an RRFP whose role should include:
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maintaining a current version of the RRFP;
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receiving and, where appropriate responding to or redirecting,
inquiries about an RRFP;
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facilitating discussions between government, shipping and
waste industry stakeholders regarding an RRFP;
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providing consistent information to government, shipping
and waste industry stakeholders regarding an RRFP; and
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instigating periodic reviews of an RRFP.
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17 Other functions could also be assigned to the
central point of contact, depending on the size and complexity of
an RRFP.
18 It is suggested that a government agency or
authority, rather than an individual person, is nominated as the central
point of contact to encourage continuity through any staff changes.
The central point of contact should also be able to respond to enquiries
in a timely manner. Hours of contact should be at least the business
hours of the agency or authority.
19
Identification of stakeholder roles and
responsibilities – this should list stakeholders and
describe their roles and responsibilities in implementing or operating
in a region covered by an RRFP. A generic example is provided below,
but should be modified and/or expanded upon to address specific arrangements
within a region.
Stakeholder
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Examples of roles/responsibilities
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Regulators
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- Enforcing legislation related to
the prevention of pollution from ships, management of ship generated wastes
and cargo residues.
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(e.g. environment
protection agencies, quarantine authorities, maritime authorities)
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- Licensing waste service
providers.
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- Providing current information to the
Organization, including updating GISIS, with respect to port reception
facilities.
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Port users
|
- Maintaining an awareness of how to
access information on RSWRCs, PLFs and individual port reception facilities
in ports.
|
(e.g. ships agents, masters)
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- Providing timely advance
notification of the need to access port reception facilities.
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- Submitting formal reports of alleged
inadequacies of port reception facilities where appropriate.
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Waste service providers
|
- Operating in accordance with
relevant legislation.
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- Collecting ship generated wastes
and cargo residues from vessels and transporting it to storage or disposal
point.
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- Treating, reusing, recycling,
destroying or otherwise managing ship generated wastes and cargo residues
collected by waste transporters.
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- Providing current
contact details to RRFP point of contact and other stakeholders as
necessary.
|
20
Period of review – an RRFP
should include a schedule for regular review by the participating
States to take into account changing shipping patterns, types of ship
generated wastes and cargo residues, local waste infrastructure and
capacity improvements and other relevant circumstances. The aim of
such a review process is to ensure that the objectives of the Convention
and the needs of ships using ports covered by a RRFP continue to be
met.
21
Description of consultations undertaken
with stakeholders in developing an RRFP – this will assist
in demonstrating to MEPC and stakeholders that the full range of stakeholder
needs, roles and points of view have been thoroughly considered in
developing an RRFP.