II. Laws and regulations and administrative measures
218. Annex III, article 4, paragraph 4, of the Convention requires the sponsoring State to adopt laws and regulations and to take administrative measures. Thus, there is here a stipulation that the adoption of laws and regulations and the taking of administrative measures are necessary. The scope and extent of the laws and regulations and administrative measures required depend upon the legal system of the sponsoring State. The ad option of laws and regulations is prescribed because not all the obligations of a contractor may be enforced through administrative measures or contractual arrangements alone, as specified in paragraphs 223 to 226.
III. Compliance by means of a contract?
223. It is the requirement in Annex III, article 4 , paragraph 4, of the Convention, that the measures to be taken by the sponsoring State should be in the form of laws and regulations and administrative measures. This means that a sponsoring State could not be considered as complying with its obligations only by entering into a contractual arrangement, such as a sponsoring agreement, with the contractor. Not only would this be incompatible with the provision referred to above but also with the Convention in general and Part XI thereof in particular.
224. Mere contractual obligations between the sponsoring State and the sponsored contractor may not serve as an effective substitute for the laws and regulations and administrative measures referred to in Annex III, article 4, paragraph 4, of the Convention. Nor would they establish legal obligations that could be invoked against the sponsoring State by entities other than the sponsored contractor.
IV. Content of the measures
227. The Convention leaves it to the sponsoring State to determine what measures will enable it to discharge its responsibilities. Policy choices on such matters must be made by the sponsoring State. In view of this, the Chamber considers that it is not called upon to render specific advice as to the necessary and appropriate measures that the sponsoring State must take in order to fulfill its responsibilities under the Convention.
240. Under Annex III, article 21, paragraph 3, of the Convention, the rules, regulations and procedures concerning environmental protection adopted by the Authority are used as a minimum standard of stringency for the environmental or other laws and regulations that the sponsoring State may apply to the sponsored contractor. It is implicit in this provision that sponsoring States may apply to the contractors they sponsor more stringent standards as far as the protection of the marine environment is concerned.
241. Article 209, paragraph 2 , of the Convention is based on the same approach. According to this provision, the requirements contained in the laws and regulations that States adopt concerning pollution of the marine environment from activities in the Area "undertaken by vessels, installations, structures and other devices flying their flag or of their registry or operating under their authority . . . shall be no less effective than the international rules, regulations , and procedures" established under Part XI, which consist primarily of the international rules, regulations and procedures adopted by the Authority.
242. For these reasons,
THE CHAMBER,
1. Unanimously,
Decides that it has jurisdiction to give the advisory opinion requested.
2. Unanimously,
Decides to respond to the request for an advisory opinion.
3. Unanimously,
Replies to Question 1 submitted by the Council as follows:
Sponsoring States have two kinds of obligations under the Convention and related instruments:
A. The obligation to ensure compliance by sponsored contractors with the terms of the contract and the obligations set out in the Convention and related instruments.
This is an obligation of "due diligence". The sponsoring State is bound to make best possible efforts to secure compliance by the sponsored contractors.
B. Direct obligations with which sponsoring States must comply independently of their obligation to ensure a certain conduct on the part of the sponsored contractors.
4. Unanimously,
Replies to Question 2 submitted by the Council as follows:
The liability of the sponsoring State arises from its failure to fulfil its obligations under the Convention and related instruments. Failure of the sponsored contractor to comply with its obligations does not in itself give rise to liability on the part of the sponsoring State.
The conditions for the liability of the sponsoring State to arise are:
(a) failure to carry out its responsibilities under the Convention; and
(b) occurrence of damage.
5. Unanimously,
Replies to Question 3 submitted by the Council as follows:
The Convention requires the sponsoring State to adopt, within its legal system, laws and regulations and to take administrative measures that have two d istinct functions, namely, to ensure compliance by the contractor with its obligations and to exempt the sponsoring State from liability.
The scope and extent of these laws and regulations and administrative measures depends on the legal system of the sponsoring State.
Such laws and regulations and administrative measures may include the establishment of enforcement mechanisms for active supervision of the activities of the sponsored contractor and for co-ordination between the activities of the sponsoring State and those of the Authority.
NOTES AND QUESTIONS
1. The ITLOS Advisory Opinion was well-received especially because all three questions were answered unanimously by the court. Was the court correct in interpreting the standard for compliance to be due diligence instead of strict liability? Was the court correct in stating that the obligations of both kinds---due diligence and direct obligations---apply equally to developed and developing states? What is the relationship between the due diligence and the direct obligations?
2. How does the standard of liability for sponsoring states differ from the standard of liability for the sponsored contractor?
3. How do you evaluate the care with which the Authority is preparing for exploitation of the resources of the deep seabed? Do you think the Authority is doing enough to protect marine ecosystems and the marine environment?
SECTION V. Operational Ship Pollution
The safe operation of ships is comprehensively addressed by IMO conventions. The relevant IMO conventions in this regard are listed in section II of this chapter. Several IMO conventions deal specifically with various forms of operational ship pollution. Two conventions deal with particular environmental problems of shipping: (1) the International Convention on the Control of Harmful
Antifouling Systems on Ships (Antifouling Convention) (2001), which prohibits the use of harmful organotins (listed in Annex I of the convention) in antifouling paints used on ships, and (2) the International Convention for the Control and Management of Ships' Ballast Water and Sediments
( Ballast Water Convention) (2004), which seeks to prevent, minimize, and ultimately eliminate the transfer of harmful aquatic organisms and pathogens through the control and management of ships' ballast water and sediments. The Antifouling Convention entered into force i n 2008; the Ballast Water
Convention is not yet in force. The United States is not a party to either convention.
The principal IMO convention dealing with operational ship pollution is the International Convention for the Prevention of Pollution from Ships ( London, 1973 and 1978), which is known as MARPOL 73/78. MARPOL consists of two types of regulations. First, technical regulations cover the design and construction of ships and their onboard equipment. For example, after the Exxon Valdez oil spill in 1989, MARPOL was amended to require double-hull construction for new oil tankers ( Regulation
13F), and single-hull tankers were required to be phased out (Regulation 13G). Second, MARPOL sets out discharge standards and regulations governing the discharge of certain categories of substances from ships.
MARPOL's operational pollution standards are contained in Annexes I to VI, as follows:
Annex I: Prevention of pollution by oil
Entry into force: 2 October 1983
The 1973 Convention maintained the oil discharge criteria prescribed in the 1969 amendments to the 1954 Oil Pollution Convention, without substantial changes, namely:
Operational discharges of oil from tankers are allowed only when all of the following conditions are met:
1. the total quantity of o il which a tanker may discharge in any ballast voyage whilst under way must not exceed 1/15,000 of the total cargo carrying capacity of the vessel;
2. the rate at which oil may be discharged must not exceed 30 litres per mile travelled by the ship; and
3. no discharge of any oil whatsoever must be made from the cargo spaces o f a tanker within 50 miles of the nearest land.
An oil record book is required, in which is recorded the movement of cargo oil and its residues from loading to discharging on a tank-to-tank basis.
In addition, in the 1973 Convention, the maximum quantity of oil permitted to be discharged on a ballast voyage of new oil tankers was reduced from 1/15,000 of the cargo capacity to 1/ 30,000 of the amount of cargo earned. These criteria applied equally both to persistent (black) and non- persistent (white) oils.
As with the 1969 OILPOL amendments, the 1973 Convention recognized the "load on top" (LOT) system which had been developed by the oil industry in the 1960s. On a ballast voyage the tanker takes on ballast water (departure ballast) in dirty cargo tanks. Other tanks are washed to take on clean
ballast. The tank washings are pumped into a special slop tank. After a few days, the departure ballast settles and oil flows to the top. Clean water beneath is then decanted while new arrival ballast water is taken on. The upper layer of the departure ballast is transferred to the slop tanks. Alter further settling and decanting, the next cargo is loaded on top of the remaining oil in the slop tank, hence the term load on top.
A new and important feature of the 1973 Convention was the concept of “special areas” which are considered to be so vulnerable to pollution by a oil that oil discharges within them have been completely prohibited with minor and well-defined exceptions. The 1973 Convention identified the Mediterranean Sea, the Black Sea, and Baltic Sea, the Red Sea and the Gulfs area as special areas. All oil-carrying chips are required to be capable of operating the method of retaining oily wastes on board through the “load on top” system or for discharge to shore reception facilities.
This involves the fitting of appropriate equipment, including an oil-discharge monitoring and control system , oily-water separating equipment and a fitting system, slop tanks, sludge tanks, piping and pumping arrangements.
New oil tankers (i.e. those for which the building contract was placed after 31 December 1975) o f 70, 000 tons deadweight and above, must be fitted with segregated ballast tanks large enough to provide adequate operating draught without the need to carry ballast water in cargo oil tanks.
Secondly, new oil tankers are required to meet certain subdivision and damage stability requirements so that, in any loading conditions, they can survive after damage by collision or stranding.
The Protocol of 1978 made a number of changes to Annex I o f the parent convention. Segregated ballast tanks (SBT) are required on all new tankers of 20,000 dwt and above (in the parent convention SBTs were only required on new tankers of 70,000 dwt and above). The Protocol also required SBTs to be protectively located - that is, they must be positioned in such a way that they will help protect the cargo tanks in the event of a collision or grounding.
Another important innovation concerned crude oil washing (COW), which had been developed by the oil industry in the 1970s and offered major benefits. Under COW, tanks are washed not with water but with crude oil - the cargo itself. COW was accepted as an aitemat1ve to SBTs on existing tankers and is an additional requirement on new tankers.
For existing crude oil tankers (built before entry into force of the Protocol) a third aitemative was permissible for a period of two to four years after entry into force of MARPOL 73/78. The dedicated clean ballast tanks (CBT) system meant that certain tanks are dedicated solely to the carnage of
ballast water. This was cheaper than a full SBT system since It utilized existing pumping and piping, but when the period of grace has expired other systems must be used.
Drainage and discharge arrangements were also altered in the Protocol, regulations for improved stopping systems were introduced.
Some oil tankers operate solely in specific trades between ports which are provided with adequate reception facilities. Some others do not use water as ballast. The TSPP Conference recognized that such ships should not be subject to all MARPOL requirements and they were consequently exempted from the SBT, COW and CBT requirements. It is generally recognized that the effectiveness o f international conventions depends upon the degree to which they are obeyed and this in turn depends largely upon the extent to which they are enforced. The 1978 Protocol to MARPOL therefore introduced stricter regulations for the survey and certification of ships.
The 1992 amendments to Annex I made it mandatory for new oil tankers to have double hulls - and it brought in a phase-in schedule for existing tankers to fit double hulls, which was subsequently revised in 2001 and 2003.
Annex II: Control of pollution by noxious liquid substances
Entry into force: 6 April 1987
Annex II details the discharge criteria and measures for the control of pollution by noxious liquid substances carried in bulk.
Some 250 substances were evaluated and included in the list appended to the Convention. The discharge of their residues is allowed only to reception facilities until certain concentrations and conditions (which vary with the category of substances) are complied with.
In any case, no discharge of residues containing noxious substances is permitted within 12 miles of the nearest land. More stringent restrictions applied to the Baltic and Black Sea areas.
Annex III: Prevention of pollution by harmful substances in packaged form
Entry into force: 1 July 1992
The first of the convention's optional annexes. States ratifying the Convention must accept Annexes II and II but can choose not to accept the other three - hence they have taken much longer to enter into force.
Annex III contains general requirements for the issuing of detailed standards on packing, marking, labeling, documentation, stowage, quantity limitations, exceptions and notifications for preventing pollution by harmful substances.
The International Maritime Dangerous Goods (IMDG) Code has, since 1991, included marine pollutants.
Annex lV: Prevention of pollution by sewage from ships
Entry into force: 27 September 2003
The second of the optional Annexes, Annex IV contains requirements to control pollution of the sea by sewage. A revised Annex was adopted in 2004.
Annex V: Prevention of pollution by garbage from ships
Entry into force: 31 December 1988
This deals with different types of garbage and specifies the distances from land an the manner in which they may be disposed of. The requirements are much stricter in a number of “special areas” but perhaps the most important feature of the Annex is the complete ban imposed on the dumping into the sea of all forms of plastic.
Annex VI: Prevention of Air Pollution from ships
Entry into force: 19 May 2005
The regulations in this annex, when they come into force, will set limits on sulphur oxide and nitrogen oxide emissions from ship exhausts and prohibit deliberate emissions of ozone depleting substances.
Enforcement
Any violation of the MARPOL 73/78 Convention within the jurisdiction of any Party to the Convention is punishable either under the law of that Party or under the law of he flag State. In this respect, the term “jurisdiction” in the convention should be construed in the light of international law in force at the time the Convention is applied or interpreted.
With the exception of very small vessels, ships engaged on international voyages must carry on board valid international certificates which may be accepted at foreign ports as prima facie evidence that the ship complies with the requirements of the Convention.
If, however, there are clear grounds for believing that the condition of the ship or tis equipment does not correspond substantially with the particulars of the certificate, or if the ship does not carry a valid certificate, the authority carrying out the inspection may detain the ship until it is satisfied that the ship can proceed to sea without presenting unreasonable threat of harm to the marine environment.
Under Article 17, the Parties to the Convention accept the obligation to promote, in consultation with other international bodies and with the assistance of UNEP, support for those Parties which request technical assistance for various purposes, such as training the supply of equipment, research, and combating pollution.
INTERNATIONAL MARITIME ORGANIZATION
Vessel Discharge Regulations
Annex I (oil)
TABLE I
OIL TANKERS OF ALL SIZES
Control of discharge of oil from tank areas including cargo pump room
|
Within special areas OR outside special areas, within 50 nautical miles (nm) from the nearest land
|
ANY DISCHARGES IS PROHIBITED, except clean or segregated ballast
|
Outside special areas, more than
50 nm from the nearest land
|
ANY DISCHARGE IS PROHIBITED, except clean or
segregated ballast, or when:
-
the tanker is proceeding en route, and
-
the instantaneous rate of discharge of oil does not exceed 30 litres/nm, and
-
the total quantity of oil discharged into the sea does not exceed
- 1 /15,000 (for existing tankers) and/
- 1 /30,000 (for new tankers)
of the total quantity of the cargo which was carried on the previous voyage, and
-
the tanker has in operation a monitoring and control system for the discharge of oil, and slop tank arrangements as required by Regulation 15.
|
TABLE II
OIL TANKERS OF ALL SIZES
OTHER SHIPS OF 400 GRT AND ABOVE
Control of discharge of oil from machinery spaces
|
Within special areas
|
ANY DISCHARGES IS PROHIBITED, except when
-
the ship is proceeding en route, and
-
the oil content of the effluent without dilution does not exceed 15 ppm, and
-
the ship has in operation oil filtering equipment with automatic 1 5 ppm stopping device, and
-
bilge water is not mixed with oil cargo residue or cargo pump room bilges (on oil tankers)
|
Outside special areas
|
ANY DISCHARGE IS PROHIBITED, except when
-
the ship is proceeding en route
-
the oil content of the effluent is less than 15 ppm, and
-
the ship has in operation an oil discharge monitoring and control systems, oily-water separating or filtering equipment of other installation required by Regulation 16, and
-
bilge water is not mixed with oil cargo residue or cargo pump room bilges (on oil tankers)
Note : Oily mixtures which are not mixed with oil cargo residue or cargo pump room bilges, and where the oil content of the effluent without dilution does not exceed 1 5 ppm may be discharge outside special areas without any additional restrictions.
|
TABLE Ill
SHIPS BELOW 400 GRT OTHER THAN OIL TANKERS
Control of discharge of oil from machinery spaces
|
Within special areas
|
ANY DISCHARGES IS P ROH I BITED, except when the oil content without dilution does not exceed 15 ppm
|
Outside special areas
|
ANY DISCHARGE IS PROHIBITED, except when the Flag State considers that all the following conditions are satisfied as far as practicable and reasonable:
-
the ship is proceeding en route, and
-
the oil content of the effluent is less than 15 ppm , and
-
the ship has in operation suitable equipment as required by Regulation 16
Note: Oily mixtures where the oil content of the effluent without dilution does not exceed 15 ppm may be discharged without any additional restrictions.
|
Annex II (noxious liquid substances in bulk)
1. General
Division of noxious substances into 4 categories:
Category
|
Hazard to marine resources
|
Harm to amenities or other legitimate uses of the sea
|
A
|
Major hazard
|
Serious harm
|
B
|
Hazard
|
Harm
|
C
|
Minor hazard
|
Minor harm
|
D
|
Recognizable hazard
|
Minimal harm
|
Group
|
In all areas
|
A, B and C
| -
ship is proceeding en route
-
minimum speed 7 knots (self-propelled) or 4 knots (not self-propelled
-
at least 12 nautical miles from the nearest land
-
discharge below the waterline
-
minimum water depth 25 metres
|
And
|
Outside special areas
|
Within special areas
|
A
|
Maximum concentration of tank washings 0.1 percent by weight
|
Maximum concentration of tank washings 0.05 percent by weight
|
| -
per tank max. 1 cubic metre or 1/3,000 of the tank capacity in cubic metres
-
concentration of the substance in the wake astern of the ship max. 1 ppm
| -
The tank has been precleaned, and the washings have been discharge to a reception facility
-
concentration of the substance in the wake astern of the ship max. 1 ppm
|
C
| -
per tank max. 3 cubic metres or 1/1,000 of the tank capacity in cubic metres
-
concentration of the substance in the wake astern of the ship max. 10 ppm
| -
per tank max. 1 cubic metre or 1/3,000 of the tank capacity in cubic metres
-
concentration of the substance in the wake astern of the ship max. 1 ppm
|
D
|
In all areas
-
Ship is proceeding en route
-
Minimum speed 7 or 4 knots
-
At least 12 nautical miles from the nearest land
-
Max. one part of the substance in ten parts of water
|
1. Discharge of cargo residues
-
Baltic Sea
-
Black Sea
-
Antarctica
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