RESOLUTION MEPC.279(70)
(Adopted on 28 October 2016)
2016
GUIDELINES FOR APPROVAL OF BALLAST WATER MANAGEMENT SYSTEMS (G8)
THE MARINE ENVIRONMENT PROTECTION COMMITTEE,
RECALLING Article 38(a) of the Convention on the International
Maritime Organization concerning the functions of the Marine Environment
Protection Committee conferred upon it by the international conventions for the
prevention and control of marine pollution from ships,
RECALLING ALSO that the International Conference on Ballast Water
Management for Ships held in February 2004 adopted the International Convention
for the Control and Management of Ships' Ballast Water and Sediments, 2004 (the
Ballast Water Management Convention) together with four conference resolutions,
NOTING that regulation D-3 of the annex to the Ballast Water
Management Convention provides that ballast water management systems used to
comply with the Convention must be approved by the Administration, taking into
account the guidelines developed by the Organization,
NOTING ALSO resolution MEPC.125(53) by which the Committee adopted
the Guidelines for approval of ballast water management systems (the
Guidelines (G8)), and resolution MEPC.174(58), by which the Committee adopted a
revision to the Guidelines (G8),
NOTING FURTHER that, by resolution MEPC.174(58), the Committee
resolved to keep Guidelines (G8) under review in the light of experience
gained,
RECALLING the provisions for non-penalization of early movers
contained in the Roadmap for the implementation of the BWM Convention,
agreed at its sixty-eighth session (MEPC 68/WP.8, annex 2),
NOTING the Organization's established practice with regard to the
validity of type approval certification for marine products (MSC.1/Circ.1221)
that the Type Approval Certificate itself has no influence on the operational
validity of existing ballast water management systems accepted and installed on
board a ship and manufactured during the period of validity of the relevant
Type Approval Certificate, meaning that the system need not be renewed or
replaced due to expiration of such Certificate,
HAVING CONSIDERED, at its seventieth session, the outcome of the
Intersessional Working Group on the Review of Guidelines (G8),
1 ADOPTS the 2016
Guidelines for approval of ballast water management systems (G8), as set
out in the annex to this resolution (the 2016 Guidelines (G8));
2 AGREES to keep the
2016 Guidelines (G8) under review in the light of experience gained with their
application;
3 RECOMMENDS that
Administrations apply the 2016 Guidelines (G8) when approving ballast
water management systems as soon as possible, but not later than 28 October
2018; 4 AGREES that ballast water management systems installed on ships on or
after 28 October 2020 should be approved taking into account the 2016
Guidelines (G8);
5 AGREES that
ballast water management systems installed on board ships prior to 28 October
2020 should be approved taking into account either the Guidelines (G8) as
adopted by resolution MEPC.174(58), or preferably the 2016 Guidelines (G8) set
out in the annex to this resolution;
6 AGREES that, for
the purpose of operative paragraphs 4 and 5 of this resolution, the word
"installed" means the contractual date of delivery of the ballast
water management system to the ship. In the absence of such a date, the word
"installed" means the actual date of delivery of the ballast water
management system to the ship;
7 AGREES that the
dates referenced in this resolution will be considered in the reviews carried
out in accordance with regulation D-5 of the Ballast Water Management
Convention, to determine whether a sufficient number of appropriate
technologies are approved and available, taking into account the 2016
Guidelines (G8);
8 SUPERSEDES the Guidelines
for approval of ballast water management systems (G8) adopted by resolution
MEPC.174(58).
ANNEX
2016 GUIDELINES FOR APPROVAL OF BALLAST WATER MANAGEMENT SYSTEMS
(G8)
Contents
1 INTRODUCTION
General
Goal and purpose
Applicability
2 BACKGROUND
3 DEFINITIONS
4 TECHNICAL
SPECIFICATIONS
General principles for
operation
Ballast water management
systems
Control and monitoring equipment
5 TYPE APPROVAL PROCESS
6 APPROVAL AND CERTIFICATION PROCEDURES
7 INSTALLATION REQUIREMENTS FOLLOWING TYPE
APPROVAL
8 INSTALLATION SURVEY AND COMMISSIONING
PROCEDURES FOLLOWING TYPE APPROVAL
ANNEX
PART
1 SPECIFICATIONS FOR PRE-TEST EVALUATION OF SYSTEM DOCUMENTATION
PART
2 TEST AND PERFORMANCE SPECIFICATIONS FOR APPROVAL OF BALLAST WATER
MANAGEMENT SYSTEMS
PART
3 SPECIFICATION FOR ENVIRONMENTAL TESTING FOR APPROVAL OF BALLAST WATER
MANAGEMENT SYSTEMS
PART
4 SAMPLE ANALYSIS METHODS FOR THE DETERMINATION OF BIOLOGICAL CONSTITUENTS IN
BALLAST WATER
PART
5 SELF-MONITORING
PART
6 VALIDATION OF SYSTEM DESIGN LIMITATIONS
PART
7 TYPE APPROVAL CERTIFICATE AND TYPE APPROVAL REPORT
Appendix
TYPE APPROVAL CERTIFICATE OF BALLAST WATER MANAGEMENT SYSTEM
2016 GUIDELINES FOR APPROVAL OF BALLAST WATER MANAGEMENT SYSTEMS
(G8)
1 INTRODUCTION
General
1.1 The 2016 Guidelines
for approval of ballast water management systems (G8) are aimed primarily at
Administrations, or their designated bodies, in order to assess whether ballast
water management systems meet the standard as set out in regulation D-2 of the
"International Convention for the Control and Management of Ships' Ballast
Water and Sediments," hereafter referred to as "the Convention".
In addition, these guidelines can be used as guidance for manufacturers and
shipowners on the evaluation procedure that equipment will undergo and the
requirements placed on ballast water management systems. These Guidelines
should be applied in an objective, consistent and transparent way and their
application should be evaluated periodically by the Organization.
1.2 Articles and
regulations referred to in these Guidelines are those contained in the
Convention.
1.3 The Guidelines
include general requirements concerning design and construction, technical
procedures for evaluation, the procedure for issuance of the Type Approval
Certificate of the ballast water management system, and reporting to the
Organization.
1.4 These Guidelines
are intended to fit within an overall framework for evaluating the performance
of systems that includes the experimental shipboard evaluation of prototype
systems under the provisions of regulation D-4, approval of ballast water
management systems and associated systems that comply fully with the
requirements of the Convention, and port State control sampling for compliance
under the provisions of article 9 of the Convention.
1.5 The requirements of
regulation D-3 stipulate that ballast water management systems used to comply
with the Convention must be approved by the Administration, taking into account
these Guidelines. In addition to such ballast water management system approval,
as set forth in regulation A-2 and regulation B-3, the Convention requires that
discharges of ballast water from ships must meet the regulation D-2 performance
standard on an on-going basis. Approval of a system is intended to screen-out
management systems that would fail to meet the standards prescribed in
regulation D-2 of the Convention. Approval of a system, however, does not
ensure that a given system will work on all ships or in all situations. To
satisfy the Convention, a discharge must comply with the D-2 standard
throughout the life of the ship.
1.6 The operation of
ballast water management systems should not impair the health and safety of the
ship or personnel, nor should it present any unacceptable harm to the
environment or to public health.
1.7 Ballast water
management systems are required to meet the standards of regulation D-2 and the
conditions established in regulation D-3 of the Convention. These Guidelines
serve to evaluate the safety, environmental acceptability, practicability and
biological effectiveness of the systems designed to meet these standards and
conditions. The cost effectiveness of type-approved equipment will be used in
determining the need for revisions of these Guidelines.
1.8 These Guidelines
contain recommendations regarding the design, installation, performance,
testing, environmental acceptability and approval of ballast water management
systems.
1.9 To achieve
consistency in its application, the approval procedure requires that a uniform
manner of testing, analysis of samples, and evaluation of results is developed
and applied. These Guidelines should be applied in an objective, consistent,
and transparent way; and their suitability should be periodically evaluated and
revised as appropriate by the Organization. New versions of these Guidelines
should be duly circulated by the Organization. Due consideration should be
given to the practicability of the ballast water management systems.
Goal and purpose
1.10 The goal of these
Guidelines is to ensure uniform and proper application of the standards
contained in the Convention. As such the Guidelines are to be updated as the
state of knowledge and technology may require.
1.11 The purpose of these
Guidelines is to provide a uniform interpretation and application of the
requirements of regulation D-3 and to:
.1 define test and
performance requirements for the approval of ballast water management systems;
.2 assist
Administrations in determining appropriate design, construction and operational
parameters necessary for the approval of ballast water management systems;
.4 provide guidance to
Administrations, equipment manufacturers and shipowners in determining the
suitability of equipment to meet the requirements of the Convention and of the
environmental acceptability of treated water; and
.5 assure that ballast
water management systems approved by Administrations are capable of achieving
the standard of regulation D-2 in land-based and shipboard evaluations and do
not cause unacceptable harm to the ship, crew, the environment or public
health.
Applicability
1.12 These Guidelines
apply to the approval of ballast water management systems in accordance with
the Convention.
1.13 These Guidelines
apply to ballast water management systems intended for installation on board
all ships required to comply with regulation D-2.
2 BACKGROUND
2.1 The requirements of
the Convention relating to approval of ballast water management systems used by
ships are set out in regulation D-3.
2.2 Regulation D-2 stipulates
that ships meeting the requirements of the Convention by meeting the ballast
water performance standard must discharge:
.1 less than 10 viable
organisms per cubic metre greater than or equal to 50 micrometres in minimum
dimension;
.2 less than 10 viable
organisms per millilitre less than 50 micrometres in minimum dimension and
greater than or equal to 10 micrometres in minimum dimension; and
.3 less than the
following concentrations of indicator microbes, as a human health standard:
.1 Toxicogenic Vibrio
cholerae (serotypes O1 and O139) with less than 1 Colony Forming Unit (cfu)
per 100 millilitres or less than 1 cfu per 1 gramme (wet weight) of zooplankton
samples;
.2 Escherichia coli
less than 250 cfu per 100 millilitres; and
.3 Intestinal
Enterococci less than 100 cfu per 100 millilitres.
3 DEFINITIONS
For the purpose of these Guidelines:
3.1 Active Substance
means a substance or organism, including a virus or a fungus, that has a
general or specific action on or against harmful aquatic organisms and
pathogens.
3.2 Ballast water
management system (BWMS) means any system which processes ballast water
such that it meets or exceeds the ballast water performance standard in
regulation D-2. The BWMS includes ballast water treatment equipment, all
associated control equipment, piping arrangements as specified by the
manufacturer, control and monitoring equipment and sampling facilities. For the
purpose of these guidelines, BWMS does not include the ship's ballast water fittings,
which may include piping, valves, pumps, etc., that would be required if the
BWMS was not fitted.
3.3 Ballast water
management plan means the document referred to in regulation B-1 of the
Convention describing the ballast water management process and procedures
implemented on board individual ships.
3.4 Control and
monitoring equipment means the equipment installed for the effective
operation and control of the BWMS and the assessment of its effective
operation.
3.5 The Convention
means the International Convention for the Control and Management of Ships'
Ballast Water and Sediments, 2004.
3.6 Failed test
cycle is a valid test cycle in which the performance of the BWMS resulted
in treated water that is determined to be non-compliant with the standard set
within regulation D-2. A failed test cycle interrupts the required consecutive
test cycles and terminates the test.
3.7 Invalid test
cycle is a test cycle in which, due to circumstances outside the control of
the BWMS, the requirements for a valid test cycle are not met. When a test
cycle is invalid, it does not count as one of the required consecutive test
cycles in a test and the test can be continued.
3.8 Land-based
testing means a test of the BWMS carried out in a laboratory, equipment
factory or pilot plant including a moored test barge or test ship, according to
Parts 2 and 3 of the annex to these Guidelines, to confirm that the BWMS meets
the standard described in regulation D-2 of the Convention.
3.9 Major components
means those components that directly affect the ability of the system to meet
the ballast water performance standard described in regulation D-2.
3.10 Representative
sampling means sampling that reflects the relative concentrations
(chemicals) and numbers and composition of the populations (organisms) in the
volume of interest. Samples should be taken in a time-integrated manner and the
sampling facility should be installed in accordance with the annex, Part 1 of
the Guidelines on ballast water sampling (G2).
3.11 Sampling
facilities refers to the means provided for sampling treated or untreated
ballast water as needed in these Guidelines and in the Guidelines for
ballast water sampling (G2) developed by the Organization.
3.12 Shipboard testing
means a full-scale test of a complete BWMS carried out on board a ship
according to Part 2 of the annex to these Guidelines, to confirm that the
system meets the standards set by regulation D-2 of the Convention.
3.13 Successful test
cycle means a valid test cycle where the BWMS functions to its
specifications and treated water is determined to meet the performance standard
described in regulation D-2.
3.14 System Design
Limitations of a BWMS means the water quality and operational parameters,
determined in addition to the required type approval testing parameters, that
are important to its operation, and, for each such parameter, a low and/or a
high value for which the BWMS is designed to achieve the performance standard
of regulation D-2. The System Design Limitations should be specific to the
processes being employed by the BWMS and should not be limited to parameters
otherwise assessed as part of the type approval process. The System Design
Limitations should be identified by the manufacturer and validated under the
supervision of the Administration in accordance with these Guidelines.
3.15 Test cycle
refers to one testing iteration (to include uptake, treatment, holding and
discharge as appropriate) under a given set of requirements used to establish
the ability of a BWMS to meet the set standards.
3.16 Test means the set of required test
cycles.
3.17 Treatment Rated
Capacity (TRC) means the maximum continuous capacity expressed in cubic
metres per hour for which the BWMS is type approved. It states the amount of
ballast water that can be treated per unit time by the BWMS to meet the
standard in regulation D-2 of the Convention. The TRC is measured at the inlet
of the BWMS.
3.18 Valid test cycle
means a test cycle in which all the required test conditions and arrangements,
including challenge conditions, test control, and monitoring arrangements
(including piping, mechanical and electrical provisions) and test analytical
procedures were achieved by the testing organisation
3.19 Viable organisms
mean organisms that have the ability to successfully generate new individuals
in order to reproduce the species.
4 TECHNICAL
SPECIFICATIONS
4.1 This section
details the general technical requirements which a BWMS should meet in order to
obtain type approval.
General principles for
operation
4.2 A BWMS should be
effective in meeting the D-2 standard on short voyages and long voyages (i.e.
short and long intervals between treatment and discharge), regardless of
temperature, unless the system is intentionally constructed for use in specific
waters.
4.3 Ballast water
discharged following treatment should be safe for the environment on short
voyages and long voyages (i.e. short and long intervals between treatment and
discharge), regardless of temperature.
4.4 The design of the
BWMS should account for the fact that, regardless of the BWMS technology
employed, viable organisms remaining after treatment may reproduce in the
interval between treatment and discharge.
Ballast water management
systems
4.5 The BWMS should be designed and
constructed:
.1 for robust and
suitable operation in the shipboard environment;
.2 for the service for
which it is intended;
.3 to mitigate any
danger to persons on board when installed. Equipment that could emit dangerous
gases/liquids shall have at least two independent means of detection and
shutdown of the BWMS (i.e. hazardous gas level reaching lower explosive limits
(LEL) or level of toxic concentrations that can result in severe effects on
human health); and
.4 with materials
compatible for the substances used, purpose which it is intended, the working
conditions to which it will be subjected and the environmental conditions on
board.
4.6 The BWMS should not
contain or use any substance of a dangerous nature, unless adequate risk
mitigation measures are incorporated for storage, application, installation,
and safe handling, acceptable to the Administration.
4.7 In case of any
failure compromising the proper operation of the BWMS, audible and visual alarm
signals should be given in all stations from which ballast water operations are
controlled.
4.8 All working parts
of the BWMS that are liable to wear or to be damaged should be easily
accessible for maintenance. The routine maintenance of the BWMS and
troubleshooting procedures should be clearly defined by the manufacturer in the
operation, maintenance and safety manual. All maintenance and repairs should be
recorded.
4.9 To avoid interference with the BWMS, the
following items should be included:
.1 every access of the
BWMS beyond the essential requirements of paragraph 4.8, should require the
breaking of a seal;
.2 if applicable, the
BWMS should be so constructed that a visual indication is always activated
whenever the BWMS is in operation for purposes of cleaning, calibration, or
repair, and these events should be recorded by the control and monitoring
equipment; and
.3 the BWMS should be
provided with the necessary connections to ensure that any bypass of the BWMS
will activate an alarm, and that the bypass event is recorded by the control
and monitoring equipment.
4.10 Facilities should be
provided for checking, at the renewal surveys and according to the
manufacturer's instructions, the performance of the BWMS components that take
measurements. A calibration certificate certifying the date of the last
calibration check, should be retained on board for inspection purposes. Only
the manufacturer or persons authorized by the manufacturer should perform the accuracy
checks.
4.11 The BWMS should be
provided with simple and effective means for its operation and control. It
should be provided with a control system that should be such that the services
needed for the proper operation of the BWMS are ensured through the necessary
arrangements.
4.12 The BWMS should, if
intended to be fitted in hazardous area locations, comply with the relevant
safety regulations for such spaces. Any electrical equipment that is part of
the BWMS should be based in a non-hazardous area, or should be certified by the
Administration as safe for use in a hazardous area. Any moving parts, which are
fitted in hazardous areas, should be arranged so as to avoid the formation of
static electricity.
4.13 The BWMS should not
endanger the health and safety of the crew, interact negatively with the ship's
systems and cargo or produce any adverse environmental effects. The BWMS should
not create long term impacts on the safety of the ship and crew through
corrosive effects in the ballast system and other spaces.
4.14 It should be
demonstrated by using mathematical modelling and/or calculations, that any up
or down scaling of the BWMS will not affect the functioning and effectiveness
on board a ship of the type and size for which the equipment will be certified.
In doing so, the manufacturer of the equipment should take into account the
relevant guidance developed by the Organization.
4.15
Scaling information should allow the
Administration to verify that any scaled model is at least as robust as the
land-based-tested model. It is the responsibility of the Administration to
verify that the scaling used is appropriate for the operational design of the
BWMS.
4.16 At a minimum, the shipboard test unit should be of a capacity
that allows for further validation of the mathematical modelling and/or
calculations for scaling, and preferably selected at the upper limit of the
rated capacity of the BWMS, unless otherwise approved by the Administration.
Control and monitoring
equipment
4.17 Administrations
should ensure that type approved BWMS have a suitable control and monitoring
system that will automatically monitor and record sufficient data to verify
correct operation of the system. The control and monitoring equipment should
record the proper functioning or failure of the BWMS. Where practical, system
design limitation parameters should be monitored and recorded by the BWMS to
ensure proper operation.
4.18 The BWMS should
incorporate control equipment that automatically monitors and adjusts necessary
treatment dosages or intensities or other aspects of the BWMS of the ship,
which while not directly affecting treatment, are nonetheless required for
proper administration of the necessary treatment.
4.19 The equipment should
be able to produce (e.g. display, print or export) a report of the applicable
self-monitoring parameters in accordance with Part 5 of the annex for official
inspections or maintenance, as required.
4.20 To facilitate
compliance with regulation B-2, the control and monitoring equipment should
also be able to store data for at least 24 months, In the event the control and
monitoring equipment is replaced, means should be provided to ensure the data
recorded prior to replacement remains available on board for 24 months.
4.21 For BWMS that could
emit dangerous gases, a means of gas detection by redundant safety systems is
to be fitted in the space of the BWMS, and an audible and visual alarm is to be
activated at a local area and at a manned BWMS control station in case of
leakage. The gas detection device is to be designed and tested in accordance
with IEC 60079-29-1, or other recognized standards acceptable to the
Administration. Monitoring measures for dangerous gases with independent
shutdown is to be provided on the BWMS.
4.22 All software changes
introduced to the system after the pre-test evaluation shall be done according
to a change handling procedure ensuring traceability.
5 TYPE APPROVAL
PROCESS
5.1 The type approval requirements for BWMS
are as described below.
5.2 The manufacturer of
the equipment should submit information regarding the design, construction,
operation and functioning of the BWMS in accordance with Part 1 of the annex
including information regarding the water quality and operational parameters
that are important to the operation of the system. This information should be
the basis for a first evaluation of suitability by the Administration.
5.3 Following the
Administration's pre-test evaluation, the BWMS should undergo landbased,
shipboard, and other tests in accordance with the procedures described in Parts
2 and 3 of the annex. The BWMS tested for type approval should be a final and
complete product that meets the requirements of section 4 and it should be constructed
using the same materials and procedures that will be used to construct
production units.
5.4 Successful
fulfilment of the requirements and procedures outlined in Parts 2 and 3 of the
annex, as well as all other requirements of these guidelines, should lead to
the issuance of a Type Approval Certificate by the Administration in accordance
with section 6.
5.5 The limitations of
the BWMS, in addition to the required type approval testing parameters
identified in paragraphs 2.4.20 and 2.5.1 of the annex, as submitted by its
manufacturer and validated by the Administration, should be documented on the
Type Approval Certificate. These design limitations do not determine if the
equipment may be type approved or not, but provide information on the conditions
beyond the type approval testing parameters under which proper functioning of
the equipment can be expected.
5.6 When a type
approved BWMS is installed on board, an installation survey according to
section 8 should be carried out.
5.7 The documentation submitted for approval
should include at least the following:
.1 a description and diagrammatic drawings of the BWMS;
.2 operation, maintenance and safety manual;
.4 hazard identification;