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IMO
Resolution
A.868(20)
Adopted on 27
November 1997 (Agenda item 11)
GUIDELINES FOR THE CONTROL AND MANAGEMENT OF SHIPS'
BALLAST WATER TO MINIMIZE THE TRANSFER OF HARMFUL AQUATIC ORGANISMS AND
PATHOGENS
THE
ASSEMBLY,
RECALLING Article 15(j) of the Convention on the
International Maritime Organization concerning the functions of the
Assembly in relation to regulations and guidelines concerning prevention
and control of marine pollution from ships,
RECALLING ALSO
resolution A.774(18) by which it recognized that the uncontrolled
discharge of ballast water and sediment from ships has led to the transfer
of harmful aquatic organisms and pathogens, causing injury to public
health and damage to property and the environment, and accordingly adopted
Guidelines for Preventing the Introduction of Unwanted Aquatic Organisms
and Pathogens from Ships' Ballast Water and Sediment Discharges, and
further that the Marine Environment Protection Committee (MEPC) and the
Maritime Safety Committee (MSC) shall keep the ballast water issue and the
application of the Guidelines under review with a view to further
developing the Guidelines as a basis for a new Annex to MARPOL
73/78,
RECALLING FURTHER that the 1992 United Nations Conference on
Environment and Development (UNCED), in its Agenda 21 requests IMO to
consider the adoption of appropriate rules on ballast water discharge to
prevent the spread of non-indigenous organisms, and further proclaims in
its Declaration on Environment and Development that States shall widely
apply the precautionary approach according to their
capabilities,
BEARING IN MIND that MEPC/Circ.288 recognized that
the existing Guidelines do not provide a complete solution towards the
total prevention of the introduction of harmful aquatic organisms and
pathogens, but urged that focus should be directed on measures aimed at
minimizing the risks, emphasizing further that in applying the existing
Guidelines, the ship's safety was of paramount importance,
NOTING
the objectives of the Convention on Biological Diversity, 1992, and that
the transfer and introduction of alien aquatic species with ballast water
threatens the conservation and sustainable use of biological
diversity,
NOTING FURTHER the status of work carried out by MEPC as
requested by resolution A.774(18) concerning the development of legally
binding provisions on ballast water management together with guidelines
for their effective implementation, as well as the Guidance on Safety
Aspects of Ballast Water Exchange at Sea prepared by the Sub-Committee on
Ship Design and Equipment, and distributed as MEPC/Circ.329 and
MSC/Circ.806, both of 30 June 1997,
RECOGNIZING that several States
have taken unilateral action by adopting legally binding provisions for
local, regional or national application with a view to minimizing the
risks of introducing harmful aquatic organisms and pathogens through ships
entering their ports, and also that this issue, being of worldwide
concern, demands action based on globally applicable regulation together
with guidelines for their effective implementation and uniform
interpretation,
HAVING CONSIDERED the recommendation of the MEPC at
its fortieth session on this issue,
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ADOPTS the
Guidelines for the Control and Management of Ships' Ballast Water to
Minimize the Transfer of Harmful Aquatic Organisms and Pathogens set out
in the Annex to the present resolution;
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REQUESTS
Governments to take urgent action in applying these Guidelines,
including the dissemination thereof to the shipping industry, to use
them as a basis for any measures they adopt with a view to minimizing
the risks of introducing harmful aquatic organisms and pathogens, and to
report to the MEPC on any experience gained in their
implementation;
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REQUESTS ALSO the
MEPC to work towards completion of legally binding provisions on ballast
water management in the form of a new Annex to MARPOL 73/78, together
with guidelines for their uniform and effective implementation with a
view to their consideration and adoption in the year
2000;
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REQUESTS FURTHER
the MSC to include in its workplan the evaluation of information
received from interested parties, particularly that relevant to 12.2 of
the Guidelines adopted herewith, with a view to determining the hazards
and potential consequences for various existing ship types and
operations. The MSC is also requested to consider any other relevant
issues concerning ballast water management as well as design objectives
for new ships, with a view to minimizing to the extent possible risks of
introducing harmful aquatic organisms and pathogens with ships' ballast
water and sediments;
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REVOKES
resolution A.774(18).
ANNEX -
GUIDELINES FOR THE CONTROL AND MANAGEMENT OF SHIPS' BALLAST WATER TO
MINIMIZE THE TRANSFER OF HARMFUL AQUATIC ORGANISMS AND
PATHOGENS
Contents
CHAPTER 1 - INTRODUCTION
CHAPTER 2 -
DEFINITIONS
CHAPTER 3 - APPLICATION
CHAPTER 4 - GUIDELINE
OBJECTIVES AND BACKGROUND
CHAPTER 5 - DISSEMINATION OF
INFORMATION
CHAPTER 6 - TRAINING AND EDUCATION
CHAPTER 7 -
PROCEDURES FOR SHIPS AND PORT STATES 7.1 Procedures for ships 7.2
Procedures for port States
CHAPTER 8 - RECORDING AND REPORTING
PROCEDURES 8.1 Procedures for ships 8.2 Procedures for port
States
CHAPTER 9 - SHIPS' OPERATIONAL PROCEDURES 9.1
Precautionary practices .1 Minimizing uptake of harmful aquatic
organisms, pathogens and sediments .2 Removing ballast sediment on a
timely basis .3 Avoiding unnecessary discharge of ballast
water
9.2 Ballast water management options .1 Ballast water
exchange .2 Non-release or minimal release of ballast water .3
Discharge to reception facilities .4 Emergent and new technologies and
treatments
CHAPTER 10 - PORT STATE CONSIDERATIONS 10.1 Highly
disparate conditions between uptake and discharge ports 10.2 Ballast
water age 10.3 Presence of target organisms
CHAPTER 11 -
ENFORCEMENT AND MONITORING BY PORT STATES
CHAPTER 12 - FUTURE
CONSIDERATIONS IN RELATION TO BALLAST WATER EXCHANGE 12.1 Research
needs 12.2 Long-term evaluation of safety aspects in relation to
ballast water exchange
CHAPTER 13 - BALLAST SYSTEM
DESIGN
Appendix 1 - Ballast water reporting form
Appendix 2
- Guidance on safety aspects of ballast water exchange at
sea
1
Introduction
1.1 Studies carried
out in several countries have shown that many species of bacteria, plants,
and animals can survive in a viable form in the ballast water and sediment
carried in ships, even after journeys of several months' duration.
Subsequent discharge of ballast water or sediment into the waters of port
States may result in the establishment of harmful aquatic organisms and
pathogens which may pose threats to indigenous human, animal and plant
life, and the marine environment. Although other media have been
identified as being responsible for transferring organisms between
geographically separated water bodies, ballast water discharge from ships
appears to have been among the most prominent.
1.2 The potential
for ballast water discharge to cause harm has been recognised not only by
the International Maritime Organization but also by the World Health
Organization, which is concerned about the role of ballast water as a
medium for the spreading of epidemic disease bacteria.
1.3 These
Guidelines are not to be regarded as a certain solution to the problem.
Rather, each part of them should be viewed as a tool which, if correctly
applied, will help to minimize the risks associated with ballast water
discharge. As scientific and technological advances are made, the
Guidelines will be refined to enable the risk to be more adequately
addressed. In the interim, port States, flag States and other parties that
can assist in mitigating this problem should exercise due care and
diligence in an effort to conform to the maximum extent possible with the
Guidelines.
1.4 The selection of appropriate methods of risk
minimization will depend upon several factors, including the type or types
of organisms being targeted, the level of risk involved, its environmental
acceptability, the economic and ecological costs involved and the safety
of ships.
2
Definitions
For the purposes of
these Guidelines, the following definitions apply: 'Administration'
means the Government of the State under whose authority the ship is
operating.
'Convention' means MARPOL 73/78 (International
Convention for the Prevention of Pollution from Ships, 1973, and the
Protocol of 1978 related thereto).
'Member States' means States
that are Members of the International Maritime
Organization.
'Organization means' the International Maritime
Organization (IMO).
'Port State authority' means any official or
organization authorized by the Government of a port State to administer
guidelines or enforce standards and regulations relevant to the
implementation of national and international shipping control
measures.
'Treatment' means a process or mechanical, physical,
chemical or biological method to kill, remove or render infertile, harmful
or potentially harmful organisms within ballast water.
3 Application
The Guidelines are directed to Member States and can apply
to all ships; however, a port State authority shall determine the extent
to which they do apply.
4
Guideline objectives and background
4.1 The objectives of these Guidelines, developed under
technical and scientific guidance, are to assist Governments and
appropriate authorities, ship masters, operators and owners, and port
authorities, as well as other interested parties, in minimizing the risk
of introducing harmful aquatic organisms and pathogens from ships' ballast
water and associated sediments while protecting ships' safety.
4.2
The Guidelines allow port States to exempt ships within the area under
their jurisdiction from part or all of the relevant provisions.
Notwithstanding, any administration wishing to apply restrictions to
ballast water operations should still follow these Guidelines, when
developing legislation or procedures.
4.3 In order that the
Guidelines may be implemented in a standard and uniform manner, all Member
State Governments, ship operators, other appropriate authorities and
interested parties are requested to apply these
Guidelines.
5 Dissemination of
information
5.1 Administrations
are encouraged to maintain and exchange information relevant to these
Guidelines through the Organization. Accordingly, administrations are
encouraged to provide the Organization with the following: .1
Information on severe outbreaks or infestations of harmful aquatic
organisms which may pose a risk; .2 Copies of current domestic laws and
regulations; .3 Technical and research information; .4 Education
materials (such as audio and video tapes) and printed materials; and .5
Location and terms of use of alternative exchange zones, contingency
strategies, availability of shore reception facilities, fees,
etc.
5.2 Member States, applying ballast water and sediment
discharge procedures, should notify the Organization of specific
requirements and provide to the Organization, for the information of other
Member States and non-governmental organizations, copies of any
regulations, standards, exemptions or guidelines being applied.
Verification and detailed information concerning port State requirements
should be obtained by the ship prior to arrival.
5.3 Port State
authorities should provide the widest possible distribution of information
on ballast water and sediment management and treatment requirements that
are being applied to shipping. Failure to do so may lead to unnecessary
delays for ships seeking entry to port States.
5.4 Shipping
organizations and ships' managers should be familiar with the requirements
of port State authorities with respect to ballast water and sediment
management and treatment procedures, including information that will be
needed to obtain entry clearance.
5.5 Member States are invited to
provide the Organization with details of any research and development
studies that they carry out with respect to the impact and control of
harmful aquatic organisms and pathogens in ships' ballast water and
sediment.
5.6 Member States should provide to the Organization
details of records describing reasons why existing requirements could not
be complied with, e.g. force majeure, heavy weather, failure of equipment,
or lack of information concerning port State
requirements.
6 Training and
education
6.1 Training for
ships' masters and crews as appropriate should include instructions on the
application of ballast water and sediment management and treatment
procedures, based upon the information contained in these Guidelines.
Instruction should also be provided on the maintenance of appropriate
records and logs. Governments should ensure that their marine training
organizations include this in the contents of their syllabus.
6.2
The application of processes and procedures concerning ballast water
management are currently at the core of the solution to minimize the
introduction of harmful aquatic organisms and pathogens.
6.3
Governments are encouraged to include knowledge of duties regarding the
control of pollution of the sea by harmful aquatic organisms and pathogens
in their training requirements for certificates.
7 Procedures for ships and port States
7.1 Procedures for ships
7.1.1 Every ship
that carries ballast water should be provided with a ballast water
management plan to assist in the minimization of transfer of harmful
aquatic organisms and pathogens. The intent of the plan should be to
provide safe and effective procedures for ballast water
management.
7.1.2 The ballast water management plan should be
specific to each ship.
7.1.3 The ballast water management plan
should be included in the ship's operational documentation. Such a plan
should address, inter alia: - relevant parts of these Guidelines; -
approval documentation relevant to treatment equipment; - an indication
of records required; and - the location of possible sampling
points.
7.2 Procedures for port States
7.2.1 Reception and
treatment facilities should be made available for the environmentally safe
disposal of ballast tank sediments.
7.2.2 Discharge of ship's
ballast water into port reception and/or treatment facilities may provide
an acceptable means of control. Port State authorities wishing to utilize
this strategy should ensure that the facilities are
adequate.
8 Recording and
reporting procedures
8.1
Procedures for ships
8.1.1 Where a port State authority requires
that specific ballast water procedures and/or treatment option(s) be
undertaken, and due to weather, sea conditions or operational
impracticability such action cannot be taken, the master should report
this fact to the port State authority as soon as possible and, where
appropriate, prior to entering seas under its jurisdiction.
8.1.2
To facilitate the administration of ballast water management and treatment
procedures on board each ship, a responsible officer should be appointed
to maintain appropriate records and to ensure that ballast water
management and/or treatment procedures are followed and
recorded.
8.1.3 When taking on or discharging ballast water, as a
minimum, the dates, geographical locations, ship's tank(s) and cargo
holds, ballast water temperature and salinity as well as the amount of
ballast water loaded or discharged should be recorded. A suitable format
is shown in appendix 1. The record should be made available to the port
State authority. 8.1.4 The location and suitable access points for
sampling ballast or sediment should be described in the ship's ballast
water management plan. This will allow crew members to provide maximum
assistance when officers of the port State authority require a sample of
the ballast water or sediment.
8.2 Procedures for port
States
8.2.1 Consistent with 5.2 above, port States should provide
ships with the following information: - details of their requirements
concerning ballast water management; - location and terms of use of
alternative exchange zones; - any other port contingency arrangements;
and - the availability, location, capacities of and applicable fees
relevant to reception facilities that are being provided for the
environmentally safe disposal of ballast water and associated
sediment.
8.2.2 To assist ships in applying the precautionary
practices described in 9.1.1 below, port States should inform local agents
and/or the ship of areas and situations where the uptake of ballast water
should be minimized, such as: - areas with outbreaks, infestations or
known populations of harmful organisms and pathogens; - areas with
current phytoplankton blooms (algal blooms, such as red tides); -
nearby sewage outfalls; - nearby dredging operations; - when a tidal
stream is known to be the more turbid; and - areas where tidal flushing
is known to be poor.
9 Ships'
operational procedures
9.1
Precautionary practices
9.1.1 Minimizing uptake of harmful aquatic
organisms, pathogens and sediments When loading ballast, every effort
should be made to avoid the uptake of potentially harmful aquatic
organisms, pathogens and sediment that may contain such organisms. The
uptake of ballast water should be minimized or, where practicable, avoided
in areas and situations such as: - areas identified by the port State
in connection with advice relating to 8.2.2 above; - in darkness when
bottom-dwelling organisms may rise up in the water column; - in very
shallow water; or - where propellers may stir up sediment.
9.1.2
Removing ballast sediment on a timely basis Where practicable, routine
cleaning of the ballast tank to remove sediments should be carried out in
mid-ocean or under controlled arrangements in port or dry dock, in
accordance with the provisions of the ship's ballast water management
plan.
9.1.3 Avoiding unnecessary discharge of ballast water If
it is necessary to take on and discharge ballast water in the same port to
facilitate safe cargo operations, care should be taken to avoid
unnecessary discharge of ballast water that has been taken up in another
port.
9.2 Ballast water management options
9.2.1 Ballast
water exchange
Near-coastal (including port and estuarine)
organisms released in mid-ocean, and oceanic organisms released in coastal
waters, do not generally survive. When exchanging ballast at sea,
guidance on safety aspects of ballast water exchange as set out in
appendix 2 should be taken into account. Furthermore, the following
practices are recommended: - where practicable, ships should conduct
ballast exchange in deep water, in open ocean and as far as possible from
shore. Where this is not possible, requirements developed within regional
agreements may be in operation, particularly in areas within 200 nautical
miles from shore. Consistent with 9.1.2 above, all of the ballast water
should be discharged until suction is lost, and stripping pumps or
eductors should be used if possible; - where the flow-through method is
employed in open ocean by pumping ballast water into the tank or hold and
allowing the water to overflow, at least three times the tank volume
should be pumped through the tank; - where neither form of open ocean
exchange is practicable, ballast exchange may be accepted by the port
State in designated areas; and - other ballast exchange options
approved by the port State.
9.2.2 Non-release or minimal release of
ballast water
In cases where ballast exchange or other treatment
options are not possible, ballast water may be retained in tanks or holds.
Should this not be possible, the ship should only discharge the minimum
essential amount of ballast water in accordance with port States'
contingency strategies.
9.2.3 Discharge to reception
facilities
If reception facilities for ballast water and/or
sediments are provided by a port State, they should, where appropriate, be
utilized.
9.2.4 Emergent and new technologies and
treatments
9.2.4.1 If suitable new and emergent treatments and
technologies prove viable, these may substitute for, or be used in
conjunction with, current options. Such treatments could include thermal
methods, filtration, disinfection including ultraviolet light, and other
such means acceptable to the port State.
9.2.4.2 Results concerning
the application and effectiveness of new ballast water management
technologies and associated control equipment should be notified to the
Organization with a view to evaluation and incorporation, as appropriate,
into these Guidelines.
10 Port
State considerations
The
following is provided for the guidance of port State authorities in the
implementation of their ballast water management programme, and to assess
risks in relation to the ballast water containing harmful aquatic
organisms and pathogens.
10.1 Highly disparate conditions between
uptake and discharge ports
Significantly different conditions may
exist between port(s) of origin and the port in which ballast water is
discharged. Examples include freshwater ballast being released into highly
saline ports. There may be organisms capable of surviving such extreme
transfers; however, there is a lower probability of species establishment
under such transport events.
10.2 Ballast water age
The
length of time during which ballast water is within an enclosed ballast
tank may also be a factor in determining the number of surviving
organisms, because of the absence of light, decreasing nutrients and
oxygen, changes of salinity and other factors. However, the maximum length
of survival of organisms in ballast water varies, and in many cases is not
known. Water of an age of 100 days should be considered the minimum for
applying this consideration. Ballast water and sediments may contain
dinoflagellate cysts and other organisms capable of surviving for a much
longer length of time.
10.3 Presence of target
organisms
10.3.1 Under certain circumstances it may be possible to
determine if one or more target species are present in the water of a
specific port and have been ballasted in a ship. In these circumstances,
the receiving port State authority may invoke management measures
accordingly. Even if such target species are not present, however, it
should be noted that the ship may still be carrying many untargetted
species which, if released in new waters, could be potentially
harmful.
10.3.2 Port States are encouraged to carry out biological
baseline surveys in their ports and to disseminate the results of their
investigations.
11 Enforcement
and monitoring by port states
11.1 Consistent with the precautionary approach to
environmental protection, these Guidelines can apply to all ships unless
specifically exempted by a port State authority within its jurisdiction.
In accordance with 5.2 above, port State authorities should inform the
Organization on how the Guidelines are being applied.
11.2 Member
States have the right to manage ballast water by national legislation.
However, any ballast discharge restrictions should be notified to the
Organization.
11.3 In all cases, a port State authority should
consider the overall effect of ballast water and sediment discharge
procedures on the safety of ships and those on board. Guidelines will be
ineffective if compliance is dependent upon the acceptance of operational
measures that put a ship or its crew at risk. Port States should not
require any action of the master which imperils the lives of seafarers or
the safety of the ship.
11.4 It is essential that ballast water and
sediment management procedures be effective as well as environmentally
safe, practicable, designed to minimize costs and delays to the ship, and
based upon these Guidelines whenever possible.
11.5 Any
instructions or requirements of a ship should be provided in a timely
manner and be clear and concise.
11.6 Port States should on request
provide a visiting ship with any requested information relative to ballast
water management and its potential effects with respect to harmful aquatic
organisms and pathogens.
11.7 Any enforcement or monitoring
activities should be undertaken in a fair, uniform and nationally
consistent manner at all ports within the port State. Where there are
compelling reasons whereby nationally consistent procedures cannot be
followed, then deviations should be reported to the
Organization.
11.8 Compliance monitoring should be undertaken by
port State authorities by, for example, taking and analysing ballast water
and sediment samples to test for the continued survival of harmful aquatic
organisms and pathogens.
11.9 Where ballast water or sediment
sampling for compliance or effectiveness monitoring is being undertaken,
port State authorities should minimize delays to ships when taking such
samples.
11.10 When sampling for research or compliance monitoring,
the port State authority should give as much notice as possible to the
ship that sampling will occur, to assist in planning staffing and
operational resources.
11.11 The master has a general obligation to
provide reasonable assistance for the above monitoring which may include
provision of officers or crew, provision of the ship's plans, records
pertaining to ballast arrangements and details concerning the location of
sampling points.
11.12 Sampling methods for research and monitoring
is the responsibility of the individual port State. The Organization
welcomes information on new or innovative methods of sampling and/or
analysis, and any relevant information should be provided to
it.
11.13 Port State authorities should indicate to the master or
responsible officer the purpose for which a sample is taken (i.e.,
monitoring, research or enforcement). Results of analyses of samples
should be made available to ship's operators on request.
11.14 Port
State authorities may sample or require samples to analyse ballast water
and sediment, before permitting a ship to proceed to discharge its ballast
water in environmentally sensitive locations. In the event that harmful
aquatic organisms or pathogens are found to be present in the samples, a
port State's contingency strategy may be applied.
12 Future considerations in relation to ballast water
exchange
12.1 Research
needs
Operational measures such as ballast water exchange may be
appropriate in the short term; however, there is a clear need for further
research. These Guidelines should be revised and adjusted in the light of
results concerning new ballast water management options.
12.2
Long-term evaluation of safety aspects in relation to ballast water
exchange
Recognizing the need to evaluate the hazards and potential
consequences for various types of ships and operations, interested parties
should carry out detailed studies and provide information relevant
to: - experience gained from carrying out ballast water exchange at
sea, including any samples/model procedures; - operational precautions
and procedures implemented to avoid potential hazards and consequences
that may arise during the ballast water exchange at sea; - an
evaluation of the safety margins between the actual metacentric height and
stresses versus the allowable seagoing limits specified in the approved
trim and stability booklet and loading manual, relevant to different types
of ships and loading conditions; - any hazards which may arise due to
human element issues relative to the responsible execution of ballast
water exchange at sea in a manner which may not be fully prudent; -
operational procedures carried out prior to initiating the ballast water
exchange at sea and check points during the exchange; - the extent of
training and management necessary to ensure that the process of ballast
water exchange at sea is effectively monitored and controlled on
board; - plan of action to incorporate any unique procedures should an
emergency occur which may affect the exchange of ballast water at sea;
and - the decision-making process, taking into account relevant safety
matters, including ship's position, weather conditions, machinery
performance, ballast system inspection and maintenance, crew safety and
availability.
13 Ballast system
design
Builders, owners and
classification societies should take these Guidelines into consideration
when designing new ships or modifying existing ships.
____________________________________________________________________________________________________________
Appendix 1
- BALLAST WATER
REPORTING FORM (TO BE PROVIDED TO PORT STATE
AUTHORITY UPON REQUEST)
1. VESSEL
INFORMATION
2. BALLAST WATER
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Vessel Name:
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Type:
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IMO Number:
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Specify Units: m³, MT, LT, ST
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Owner:
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GT: |
Call Sign:
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Total Ballast Water on Board:
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Flag:
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Arrival Date:
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Agent:
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Last Port and Country:
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Arrival Port:
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Total Ballast Water Capacity:
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Next Port and Country:
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3. BALLAST
WATER TANKS
BALLAST WATER MANAGEMENT PLAN ON BOARD? YES_____ NO_____ HAS THIS BEEN
IMPLEMENTED?
TOTAL NO. OF TANKS
ON BOARD_______
NO. OF TANKS IN BALLAST_______ IF NONE IN BALLAST GO TO NO. 5
YES_____ NO_____ NO. OF TANKS
EXCHANGED_________
NO. OF TANKS NOT EXCHANGED___________
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4. BALLAST WATER HISTORY: RECORD
ALL TANKS THAT WILL BE DEBALLASTED IN PORT STATE OF ARRIVAL; IF NONE
GO TO NO. 5
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Tanks/Holds
(list multiple
sources/tanks
separately)
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BW SOURCE
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BW EXCHANGE
: circle one: Empty/Refill or Flow
Through |
BW DISCHARGE
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DATE
ddmmyy
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PORT or
LAT.
LONG |
VOLUME
(units)
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TEMP
(units)
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DATE
ddmmyy
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ENDPOINT
LAT.
LONG. |
VOLUME (units)
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%
Exch.
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SEA
Hgt.
(m) |
DATE
ddmmyy
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PORT or LAT. LONG.
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VOLUME
(units)
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SALINITY
(units)
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Ballast
Water Tank Codes: Forepeak=FP, Aftpeak=AP, Double Bottom=DB,
Wing=WT, Topside=TS, Cargo Hold=CH,
O=Other |
IF EXCHANGES WERE NOT CONDUCTED, STATE
OTHER CONTROL ACTION(S) TAKEN:
______________________________________________________________
IF NONE, STATE REASON WHY
NOT:_______________________________________________
5. IMO BALLAST WATER GUIDELINES ON
BOARD (RES. 868(20))? YES_____ NO_____
RESPONSIBLE OFFICER’S NAME AND TITLE (PRINTED) AND
SIGNATURE___________________________________________________________________________
APPENDIX 2 -
GUIDANCE ON SAFETY ASPECTS OF BALLAST WATER EXCHANGE AT
SEA
1
Introduction
1.1 This document is intended to provide guidance on
the safety aspects of ballast water exchange at sea. The different types
of ships which may be required to undertake ballast water exchange at sea
make it presently impractical to provide specific guidelines for each ship
type. Shipowners are cautioned that they should consider the many
variables that apply to their ships. Some of these variables include type
and size of ship, ballast tank configurations and associated pumping
systems, trading routes and associated weather conditions, port State
requirements and manning.
1.2 Ballast water exchange at sea
procedures contained in relevant management plans should be individually
assessed for their effectiveness from the environmental protection point
of view as well as from the point of view of their acceptability in terms
of structural strength and stability.
1.3 In the absence of a more
scientifically based means of control, exchange of ballast water in deep
ocean areas or open seas currently offers a means of limiting the
probability that fresh water or coastal aquatic species will be
transferred in ballast water. Two methods of carrying out ballast water
exchange at sea have been identified: .1 the sequential method, in
which ballast tanks are pumped out and refilled with clean water;
and/or .2 the flow-through method, in which ballast tanks are
simultaneously filled and discharged by pumping in clean water.
2
Safety precautions
2.1 Ships engaged in ballast water exchange at
sea should be provided with procedures which account for the following, as
applicable: .1 avoidance of over and under-pressurization of ballast
tanks; .2 free surface effects on stability and sloshing loads in tanks
that may be slack at any one time; .3 admissible weather
conditions; .4 weather routeing in areas seasonably affected by
cyclones, typhoons, hurricanes, or heavy icing conditions; .5
maintenance of adequate intact stability in accordance with an approved
trim and stability booklet; .6 permissible seagoing strength limits of
shear forces and bending moments in accordance with an approved loading
manual; .7 torsional forces, where relevant; .8 minimum/maximum
forward and aft draughts; .9 wave-induced hull vibration; .10
documented records of ballasting and/or de-ballasting; .11 contingency
procedures for situations which may affect the ballast water exchange at
sea, including deteriorating weather conditions, pump failure, loss of
power, etc.; .12 time to complete the ballast water exchange or an
appropriate sequence thereof, taking into account that the ballast water
may represent 50 % of the total cargo capacity for some ships; and .13
monitoring and controlling the amount of ballast water.
2.2 If the
flow through method is used, caution should be exercised, since: .1 air
pipes are not designed for continuous ballast water overflow; .2
current research indicates that pumping of at least three full volumes of
the tank capacity could be needed to be effective when filling clean water
from the bottom and overflowing from the top; and .3 certain watertight
and weathertight closures (e.g. manholes) which may be opened during
ballast exchange, should be re-secured.
2.3 Ballast water exchange
at sea should be avoided in freezing weather conditions. However, when it
is deemed absolutely necessary, particular attention should be paid to the
hazards associated with the freezing of overboard discharge arrangements,
air pipes, ballast system valves together with their means of control, and
the accretion of ice on deck.
2.4 Some ships may need the fitting
of a loading instrument to perform calculations of shear forces and
bending moments induced by ballast water exchange at sea and to compare
with the permissible strength limits.
2.5 An evaluation should be
made of the safety margins for stability and strength contained in
allowable seagoing conditions specified in the approved trim and stability
booklet and the loading manual, relevant to individual types of ships and
loading conditions. In this regard particular account should be taken of
the following requirements: .1 stability to be maintained at all times
to values not less than those recommended by the Organization (or required
by the Administration); .2 longitudinal stress values not to exceed
those permitted by the ship's classification society with regard to
prevailing sea conditions; and .3 exchange of ballast in tanks or holds
where significant structural loads may be generated by sloshing action in
the partially filled tank or hold to be carried out in favourable sea and
swell conditions so that the risk of structural damage is
minimized.
2.6 The ballast water management plan should include a
list of circumstances in which ballast water exchange should not be
undertaken. These circumstances may result from critical situations of an
exceptional nature, force majeure due to stress of weather, or any other
circumstances in which human life or safety of the ship is
threatened.
3 Crew training and familiarization
3.1 The
ballast water management plan should include the nomination of key
shipboard control personnel undertaking ballast water exchange at
sea.
3.2 Ships' officers and ratings engaged in ballast water
exchange at sea should be trained in and familiarized with the
following: .1 the ship's pumping plan, which should show ballast
pumping arrangements, with positions of associated air and sounding pipes,
positions of all compartment and tank suctions and pipelines connecting
them to ship's ballast pumps and, in the case of use of the flow through
method of ballast water exchange, the openings used for release of water
from the top of the tank together with overboard discharge
arrangements; .2 the method of ensuring that sounding pipes are clear,
and that air pipes and their non-return devices are in good order; .3
the different times required to undertake the various ballast water
exchange operations; .4 the methods in use for ballast water exchange
at sea if applicable with particular reference to required safety
precautions; and .5 the method of on-board ballast water record
keeping, reporting and recording of routine
soundings. |