Section 4 - Environmental Compliance
Plan
4.1 The Environmental Compliance Plan (ECP) should
serve as the primary basis for evaluating the degree to which the
ship recycling facility:
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.1 understands the environmental risks associated
with ship recycling;
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.2 understands and implements the environmental
requirements imposed by national and international laws and regulations;
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.3 can manage and dispose of all the materials
used in the structure of the ship, its equipment and/or on board the
ship in an environmentally sound manner; and
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.4 implements controls to protect the environment,
which include handling and disposing of the hazardous materials.
4.2 The ECP should include information on the
recycler's ability to recycle ships and dispose of the resulting materials
in a manner that is compliant with applicable national and international
laws, regulations, and guidelines. Further, the ECP should reflect
the applicable national legislation and, where appropriate, the Basel
Convention "Technical Guidelines for the Environmentally Sound Management
of the Full and Partial Dismantling of Ships".
4.3 Elements of the ECP
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4.3.1 The ECP should provide a clear and concise
explanation of procedures for managing potentially hazardous materials,
including, but not limited to:
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.1 fuel, lubricants, and coolants; chemicals in
drums, buckets, pressurized bottles, stored solvents, and other chemicals
stocks, etc.;
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.2 cargo residue;
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.3 floatable materials (e.g. plastics, Styrofoam
insulation wood);
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.4 materials possibly containing PCBs, such as
wiring insulation (electrical cabling installed before 1975) (plastic
covering may contain PCBs)footnote;
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.5 waste water/sludges (generated aboard the vessel
during the scrapping process from rain water intrusion, fire fighting,
asbestos control activity, etc., as well as water that may be in compartments
of the vessel at the time of arrival); human waste in the form of
sewage or gray water; residues of ballast water;
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.6 harmful aquatic organisms, non-indigenous species
and marine growth in ballast water and on the hull, and sediments
in ballast tanks;
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.7 asbestos used in older ships as insulation
material and in accommodation panelling (includes bulkhead and pipe
insulation; bulkhead fire shields; electrical cable materials; brake
linings; floor tiles and deck underlay; steam, water and vent flange
gaskets; flexitalic gaskets; garlock seals; packing material; pipe
hanger inserts; and weld shop protectors and turn covers);
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.8 chromium (ballast water treatment, paint coatings,
gaskets, etc.);
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.9 TBT paints; and
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.10 environmental monitoring.
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4.3.2 Items on ships that may potentially contain
substances of concern include those identified in section 4.2 of the IMO Guidelines.
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4.3.3 In identifying potentially hazardous materials
on board ships the list of "Potentially hazardous materials which
may be on board ships delivered to recycling facilities" (appendix 2 of the IMO Guidelines)
should be considered for guidance.
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4.3.4 The ECP should identify all permits, certificates,
approvals, and licences required by international, national and local
environmental agencies and issued to the recycling facility to carry
out the work, including those required for the management of potentially
hazardous material.
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4.3.5 The ECP should identify all entities to
be involved with the process. This includes sub-contractors involved
with recycling operations at the site, and those who test, transport
and provide the disposal site/method. Copies of licences, approvals,
permits, and insurance, etc. should be included.
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4.3.6 The ECP should include a copy of the site's
spill prevention and/or spill response plan. Information related to
on-site water discharge requirements should be included.
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4.3.7 The ECP should describe whether the recycling
facility, any parent companies, subsidiaries or affiliates or any
proposed subcontractors, disposal facilities, within the past five
years has received any fines, notices, deficiencies, etc. from any
regulatory entities or third party environmental auditors.
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