-
1
THE ANALYSIS OF THE FRAMEWORK CONVENTION FOR THE PROTECTION
OF
MARINE ENVIRONMENT OF THE CASPIAN SEA
Nurseit Baizhanov
People blame their environment. There is only one person to
blame - and only one - themselves.
Robert Collier
I. Introduction
The Caspian Sea is the largest lake on Earth and the largest
inland water body. It
constitutes more than 40 percent of the world's total inland
water according to the United Nations
Global International Waters Assessment (GIWA)1.
The isolation of the Caspian Sea basin within specific climate
conditions and salinity
gradients of the sea have created a unique ecosystem in the
world. The sea, including its coastal
area, is a habitat for an abundant variety of unique and rare
species of fauna. The Caspian Sea is
the only habitat on Earth: for one of two freshwater seal
species and for the rare white-tailed sea
eagle (which is the largest bird of prey in Europe). The
extensive Caspian coastal wetlands offer
a popular winter ground and migration stop-off for many birds,
in particular, the region hosts
rare visiting birds during the winter period, including the
swamp hen and the purple flamingo.
Besides those species, the huge water area of the Caspian Sea
with is a home to over 30 mammal
species, 250 bird species, and 58 fish species2. Also, over 90
percent of the world's sturgeon
catch is produced in the Caspian Sea, and the Caspian region
holds the largest share of the
world's black caviar production3.
Besides rich and unique flora and fauna, the Caspian Sea area is
one of the first industrial
oil-producing regions on Earth, and is a fast-growing and
potentially significant source of global
energy output. This sea is shared by five littoral (coastal)
countries Russia, Azerbaijan, Iran,
Kazakhstan, and Turkmenistan. These countries have oil and
natural gas reserves amounting to
-
2
about 14.6 percent of the worlds total proven oil reserves and
almost 50 percent of the worlds
total proven natural gas reserves4.
Many international and national environmental organizations are
concerned that the
unique Caspian ecosystem could be lost because of long-term
extraction of hydrocarbon
resources and fast growing offshore extraction of those
resources for the last decade. The
environmental problems of the Caspian have been disregarded from
the first modern oil
exploration in the early 1870s. At beginning of 20th century,
there were more than 3,000 oil
wells in Baku (Azerbaijan) that is counted as one of the black
gold capitals of the world.5
The environmental situation around the Caspian Sea worsened
after the collapse of the
Soviet Union when new four independent littoral states were
established. When the common
resources (that are non-excludable and non-rivalry public goods)
are owned by a larger number
of the owners, there are more incentives for free-riding and
overusing the resources. This
problem is known as the tragedy of the commons. Also, the
economic crisis and the weakness of
developing state institutions of the new countries made it
difficult for these countries to control
the environmental situation in the Caspian Sea.
For a long time, the Caspian Sea has been known widely in the
world for its sturgeon
fishery and caviar. Nevertheless, for a long period there has
been a continuing trend of an
extreme drop in the sturgeon catch. The sturgeon catch decreased
from around 30,000 tonnes in
1985 to 13,300 tonnes in 1990, down to 2,100 tonnes in 1994 [a
6-fold decrease after the break-
up of the Soviet Union in comparison to 1990] and even less,
around 1000 tonnes in the last few
years 6 (Markandya, 2004). After the dissolution of the USSR,
the strong fishery regulatory
system collapsed as well. As a consequence of that, the illegal
catch in Caspian and the Volga
River is estimated at six to ten times the legal catch. The 1998
US Fish and Wildlife Survey
-
3
estimated that 50 percent of worldwide trade in caviar is
illegal (Markandya, 2004)7. A drastic
drop is observed in other endemic species of the Caspian Sea
such as tulka (kilka) and mammals
(CEP, 2011)8.
Damage to fisheries and to the whole biodiversity of the Caspian
Sea stems from water
pollution by rivers and oil spills. The main river polluter of
the Caspian Sea is Volga. The World
Bank assesses that one million cubic meters of untreated
industrial wastewater empty into the
Caspian annually (Markandya, 2004)9. The growing extraction and
transportation of oil is
related with significant oil spills. According to the World
Banks research the risks of spills are
highest from the abandoned Kazakh flooded oil fields in the
vicinity of the Tengiz field in the
North Caspian10.
One factor that works against finding solution to the
aforementioned environmental
problems of the Caspian Sea is the issue of the legal status of
the Caspian Sea insofar as it relates
to the problem of what kind of international rules should be
applied in the Caspian Sea case.
Different international rules would be applied if the Caspian
water body were defined as
a sea or lake. Technically, the Caspian Sea should be counted as
a lake (an enclosed water
body with no natural connection with oceans), but considering
its large water surface area and an
artificial connection to the Atlantic ocean through the
Volga-Don channel (through the Azov, the
Black, and the Mediterranean seas), the Caspian Sea can be
considered a sea as well. However,
because there is no legal definition for the Caspian Sea, the
littoral states should unanimously
agree on its legal status as a sea or a lake.
In the case when the Caspian Sea is legally defined as a sea,"
than the littoral states
should apply the United Nations Convention on the Law of the Sea
of 1982 (UNCLOS). Under
this Convention, the coastal states would hold an area up to
twelve nautical miles from shore as a
-
4
territorial sea, up to nautical 200 miles as an exclusive
economic zone, and continental shelf.
According to UNCLOS, because the widest part of Caspian Sea is
less than 200 nautical miles,
than a median line between the littoral states should be
applied. In that case, Kazakhstan would
receive 29% of the seabed, Turkmenistan, Azerbaijan, Russia
would get 19% each and only Iran
would have 14% (Antonenko, 2004)11
. In this event, Irans share of the seabed would be under
deep water making extraction highly expensive, and large
hydrocarbon resources have not yet
been found there.
If the Caspian Sea be recognized is a legal lake, then the
boundaries should be
determined by bilateral or multilateral agreements. Based on
customary international law, the
littoral states should border the seabed and the surface of the
Caspian Sea by dividing the sea in
equal shares (around 20 percent to each state) based on the
equidistant line.
Map 1. Caspian Gas and Oil Reserves and the Delimitation of the
Sea Based on the Equidistant Line on the South of the Sea (dotted
blue line) and Agreed-upon Maritime Boundaries on the North of the
Sea (solid blue line) agreed between Kazakhstan, Russia,
Azerbaijan.
Map 2. Caspian Gas and Oil Reserves and Delimitation of
the Sea: on the Equidistant Line (red dotted line) v. on the
Median Line (solid line)
-
5
Source: US Energy Information Administration12
Source: The Heritage Foundation13
Discussions over the legal status of the Caspian Sea by the
littoral states have continued
since the dissolution of the Soviet Union. The crux of those
discussions has been how to divide
the seabed of the Caspian Sea, which is very rich with
hydrocarbon resources.
Before the breakdown of the Soviet Union, the Caspian Sea was
regulated by the Treaty
of Friendship concluded in 1921 between the Russian Socialist
Federal Republic and Persia
(later Iran). According to Article 11 of that treaty, only
Russia and Iran have a right to free
shipping for their cargo and warships. This treaty granted free
shipping to both states, thus
allowing Iran to have both cargo ships and warships on the sea
waters. Later, the Treaty of
Commerce and Navigation that was concluded in 1940 between
Russia and Iran granted Iran
more rights to navigation and exclusive right to fishing on sea
area from ten nautical miles the
coasts of each state (Nick, 2005, 597)14. So, all the treaties
were based on a number of
premises, most importantly that the Caspian is closed to all but
Iranian and the Soviet shipping,
that those parties have equal access to the Sea and equal
treatment on its waters, and that any
decisions affecting the Sea and its resources must be made
jointly by them (Zimnitskaya &
Geldern, 2011)15
. However, as observed by the experts, [when] the treaties were
signed the
issue of exploitation of the seabed and subsoil resources did
not yet exist. Consequently, there
are no articles in the treaties regarding that issue
(Zimnitskaya & Geldern, 2011)16.
Initially, in the 1990s Iran and Russia actively cooperated to
persuade the other littoral
states to follow the USSR-Iran treaties that recognized the
Caspian Sea as a large lake, and urged
those states to acknowledge the Caspian seabed resources as a
common ownership and develop
those resources with consent of other littoral states (Mamedov,
2001)17
-
6
However, other littoral states opposed Russias and Irans stance.
These countries,
especially Azerbaijan and Kazakhstan would stand to reap greater
benefits under UNCLOS rules
that would devide the sea into national sectors. Azeri and
Kazakhstani national sectors divided
according to the UNCLOS rules by the median line have much more
oil and gas reserves than
other countries. To justify a median line seabed delimitation
position, Azerbaijan argued that the
above USSR-Iran treaties should be annulled because the
dissolution of the Soviet Union
constituted a case where the principle of rebus sic stantibus
(the fundamental change of
circumstances provided by article 62 of the 1969 Vienna
Convention on the Law of Treaties),
and the customary international law rebus sic stantibus (clean
slate) doctrine should be applied.
Thus, the Caspian Sea must be divided among the littoral states
according to the rules of
UNCLOS (Sanei, 2001) 18
. Moreover, Azerbaijan reasonably argued that as mentioned
above
that the treaties are applied to shipping issues and they do not
regulate delimitation of the
Caspian seabed and its resources. Azerbaijan also pointed out
that Iran did not object to the
exploitation of natural resources of Caspian seabed by Tsars
Russia and then by the Soviet
Union (Sneider, 1993)19
.
For the last two decades, positions of Russia and Iran were
gradually altered due to the
following changes and factors:
1) As a first Caspian littoral state, Azerbaijan claimed its
sovereignty over its
Caspian seabed sector by concluding the Contract of the Century
in Baku in 1994 with
thirteen largest transnational oil companies in the world from
eight countries (United States,
Great Britain, Saudi Arabia, Norway, Turkey, Japan, Russia, and
Azerbaijan). Those companies
-
7
already spent over U.S. $8 billion to explore and develop
Caspian seabed resources, and they
plan to invest $100 billion additionally in following three
decades (Nassibli, 2004)20
.
2) The discoveries of large oil and gas reserves in the Russian
Caspian seabed sector
and decreasing levels of oil and gas in current reservoirs in
Siberia.
3) Increasing activity of Azerbaijan, Kazakhstan, and
Turkmenistan to build oil and
gas transportation bypassing the Russian Federation,
4) The change of Russian foreign policy to recover and increase
its influence on the
former Soviet Republics.
5) The increasing international isolation of Iran by the
international community.
Because of these factors, the pressure of the Russian oil and
gas companies participating
in the Contract of the Century and their strong will to develop
independently the Russian
sector of Caspian seabed, Russia began to observe the divided
bottom, common waters
approach in the Caspian Sea. As a result of that approach, the
modified median line method of
delimitation of the North Caspian seabed was accepted by Russia,
Kazakhstan, and Azerbaijan
according to their trilateral agreement concluded on May
2003.
Iran has changed its position from one of common ownership of
the seabed resources to
one that supports equal national sectors of each littoral state
based on the equidistant line. One
of the reasons for this change in position, besides the changed
Russian position, is a possible
military threat from the US via Azerbaijan to Iran in the case
of free shipping of all littoral
states in the Caspian Sea (free shipping should be applied in
case of the legal lake).
Although Turkmenistan is still supporting the approach of
dividing the Caspian seabed
into national sectors, it continues to negotiate with Kazakhstan
and Azerbaijan about how to
divide the Caspian seabed between these countries. The most
difficult negotiations are going on
-
8
with Azerbaijan because these countries have had long disputes
(over 14 years) about the
ownership of three oil fields (Chirag, Azeri, and Kypaz) located
between their national seabed
sectors (Abbasov, 2012)21
.
As mentioned above, the continuing discussion on the legal
status of the Caspian Sea and
the unsettled issue of the delimitation of the Caspian Sea were
decisive factors that delayed the
conclusion of a regional environmental agreement by the littoral
states. These factors make it
unclear how the littoral states will take responsibility for the
marine environment if they do not
know where their sovereignty lies.
However, despite the pending legal status of the sea, the five
littoral States had shown
growing interest in common collaboration for the environmental
protection of the Caspian Sea.
The intensive development of the North Caspian seabed, the
aggravation of the environmental
situation in the sea, and ineffectiveness of the previous
non-binding regional agreements
prompted the littoral states to negotiate a comprehensive
binding environmental agreement.
The representatives of all littoral states of the Caspian Sea
adopted the Framework
Convention for the Protection of the Marine Environment of the
Caspian Sea (Framework
Convention) on November 2003. The former UN Secretary-General
Kofi Annan characterized
the adoption of the Framework Convention as a significant step
forward for the region and
noted that, once ratified, this landmark treaty will benefit the
health and livelihoods of hundreds
of millions of people22.
The Framework Convention works as a set legal instrument
(obligations) based on
general requirements and institutional procedures in order to
protect the environment from all
sources of pollution, preserve and restore the Caspian marine
environment, and facilitate
cooperation between Caspian States in those activities.
-
9
However, even though that document was a sign of progress to
protect the marine
environment, results of monitoring as well as statements of
concerned states and environmental
organizations are showing that the Framework Convention is not
yet working properly.
On January 27, 2013, the Deputy Head of Irans Department of
Environment for Marine
Environment accused Azerbaijan and BP of continued pollution of
the Caspian Sea by dumping
waste oil into the Caspian Sea. He stated that the southern
coastlines of the Caspian Sea have
been covered with oil slicks over the past few years with the
last such incident happening four
months ago, when about 25 tons of crude oil was cleared from
Iranian shores." These oil spills
have minimized the chances for the survival of aquatic creatures
in the sea because they
decrease oxygen content available to aquatic animals, leading to
their death23.
Also, on November 4, 2013, this same Iranian official during the
ceremony of the 10th
anniversary of signing the Framework Convention stated that the
Caspian Sea seal's population
has decreased from one million to 100,000 during last twenty
years. This has occurred because
of uncontrolled hunting and pollution24
.
Based on satellite-based monitoring, the specialists of ScanEx
RDC detected 70 oil slicks
in the northern part of the Caspian Sea, most of them
originating from ships. The total zone of
identified oil spills constituted 185 square kilometers25.
These facts can be considered proof of the tragedy of the
commons when each coastal
state is going to exploit the sea to gain maximum benefits
despite significant social cost. There
are many other facts that show that the environmental problems
are still continuing to degrade
the environmental situation in the Caspian Sea basin. One reason
for this situation is that the
Framework Convention is not adequately protecting the marine
environment of the Caspian Sea.
-
10
Accordingly, the goal of this paper is an analysis the Framework
Convention with a focus
on what possible weaknesses of the Framework Convention may have
led to the continuing
deterioration of ecology in the Caspian Sea.
-
11
II. Analysis of The Framework Convention
1. The Main Provisions of the Framework Convention.
The Framework Convention for Protection of the Marine
Environment of the Caspian Sea
is a regional instrument for building environmental principles
specific to this sea, as well as to
develop mechanisms and procedures to provide more effective
environmental protection for this
trans-boundary and unique sea.
The objective of the Framework Convention is to protect the
Caspian environment from
all sources of pollution, and to protect, preserve, sustainably
and rationally use its biological
resources 26.
In my mind, the cornerstone of the Framework that can be used to
protect the marine
environment of Caspian is the recognition by all littoral states
of the sea the following principles:
1) The guiding principle that should be used is the threat of
serious or irreversible damage
to the Caspian Sea environment." The principle suggests lack of
full scientific certainty
shall not be used as a reason for postponing cost-effective
measures to prevent such
damage27. This principle is widely referred to in international
environmental law as
Principle 15 (also called precaution," the precautionary
approach, and the principle
of the precautionary approach) in the Rio Declaration on
Environment and Development
(Rio de Janeiro, 3-14 June 1992)28
. The precautionary principle is an important concept
used to protect the environment, and it is the most frequently
used principle in
international environmental law affairs. However, the principle
is one of the most
controversial [] because of disagreements over its precise
meaning and legal status and
because of concern that it may be misused for
trade-protectionist purposes29.
-
12
2) According to the Framework Convention,"the polluter pays
principle (PPP) implies
the polluter bears the costs of pollution including its
prevention, control and
reduction30. This principle is recognized as the cornerstone of
international
environmental law31. It is similar to the Principle 16 of the
Rio Declaration provides.
Initially, the PPP was adopted of the Declaration of the United
Nations Conference on the
Human Environment in Stockholm at 1972 (Principle 21)32
. The scope of the PPP covers
all costs related to pollution.
3) The principle of accessibility of information provided in the
Framework Convention
obliges the Contracting States to provide each other with
relevant information in the
maximum possible amount33. This principle is important for the
decision-making
process and the trans-boundary monitoring of the marine
environment. The principle of
access to information is also provided in Principle 10 of the
Rio Declaration, but in the
Framework Convention the access is limited only to the states.
In comparison to the Rio
Declaration, the public participation by NGO and other Civil
Society Organizations is not
mentioned in the Framework Convention. This drawback of the
Framework Convention
will be discussed later in this paper.
Also, although that is not provided as a principle in the
Framework Convention, a
principle to cooperate between the littoral countries is implied
by Articles 6 Duty to Cooperate,"
18 Cooperation between the Contracting Parties and Part VI
Institutional Arrangements of
the Framework Convention. The obligation to cooperate is one of
most referred and accepted at
global, regional and bilateral levels in the international law.
There are 191 states, members of the
UN, who ratified the Charter of the United Nations, and who are
obliged to cooperate according
to articles 55 and 56 of chapter IX of that Charter. Also,
Principle seven of the Rio Declaration
-
13
provides States shall cooperate in a spirit of global
partnership to conserve, protect and restore
the health and integrity of the Earths ecosystem34.
These Principles lay out the crucial features of international,
regional regulation with
respect to the Caspian Sea. They also constitute new legal
norms, and provide guidance to
interpret ambiguous or too general legal provisions at global,
regional and bilateral levels,
including the Framework Convention. Also, the principles can
fill gaps in the regulation
protecting the marine environment of the Caspian Sea.
Generally, the Framework imposes the obligations to the littoral
states to prevent, reduce
and control:
1) Pollution from Land-Based Sources,
2) Pollution from Seabed Activities,
3) Pollution from Vessels,
4) Pollution Caused from Dumping,
5) Pollution from Other Human Activities,
6) Invasive Alien Species.
The Framework Convention obliges the states to endeavor to
develop coastal zone
management and to alleviate the implications of the Caspian sea
level fluctuations.
Also, the Framework provides some procedures and mechanisms that
help the littoral
countries to observe their obligations. One effective procedure
to protect the marine environment
is an environmental impact assessment (EIS) of any planned
activity that is likely to cause a
significant adverse effect on the marine environment of the
Caspian Sea35. As provided in the
Framework, results of the EIS must be disseminated between the
contacting parties36
(1The
Convention). Besides the EIS, the Framework mandates the
adoption of protocols that should
-
14
play a leading role in determining, in detail, the states
obligations when expressed too generally
in the Framework. To develop this approach, UNEPs Regional
Office for Europe offered the
development of the protocols such as on the Conservation of
Biological Diversity, on the
Protection of the Caspian Sea Against Pollution from Land-Based
Sources and Activities, on the
Environmental Impact Assessment in a Trans-Boundary Context, on
the Regional Preparedness,
Response and Co-operation in Combating Oil Pollution Incidents.
Those Protocols were assigned
as priority by the Contracting Parties to the Framework
Convention37
.
Based on the official website of the Framework Conventions
Secretariat, up to now two
Protocols have been adopted:
1) The Protocol Concerning Regional Preparedness, Response and
Co-operation in
Combating Oil Pollution Incidents ("Aktau Protocol") has been
adopted and signed at the Third
Meeting of the Conference of the Parties (COP3) in Aktau,
Kazakhstan on August 12, 2011. The
Republic of Azerbaijan, I.R. of Iran, Turkmenistan and Russian
Federation already ratified the
Aktau Protocol38
.
2) The Protocol for the Protection of the Caspian Sea against
Pollution from Land-
based Sources and Activities ("Moscow Protocol") has been
adopted and signed at the Fourth
Meeting of the Conference of the Parties (COP4) in Moscow,
Russian Federation on December
12, 2012. The Republic of Azerbaijan has acceded to the Moscow
Protocol on 25 February 2014.
(Tehran Convention web-cite)39
.
Also, Part V of the Framework Convention envisages procedures to
conduct research and
monitoring of the Caspian Seas environment. The Framework
Convention also set up a
Conference of Parties. Among other functions, the Conference is
responsible for keeping under
review the implementation of the Convention. The Secretariat is
defined as an administrative
-
15
body of the Convention. Finally, the Framework Convention
addresses in very broad and general
terms the procedures for compliance and liability for damage,
simply requiring states to
cooperate on the future development of these provisions. It does
not create a dispute settlement
mechanism, but directs Parties to settle disputes by
consultation, negotiation or other peaceful
means at their discretion.
2. The Main Drawbacks of the Framework Convention
The basis for effective control and enforcement of any
regulation is transparency and
access to information. Those elements are crucial to ensure
effective public control and
sustainable development. Because environmental issues are
important in any society, a society
needs to know all about any decision-making process, the factual
background of that process,
and any other aspects of actions that can impact human health
and the environment. Moreover, it
is a prerequisite for the active involvement of civil society
organizations, including Non-
Governmental Organizations (NGOs) to control government actions
and to exert public
pressure in order to enforce environmental regulation. The
principle of public access to the
information is one of the most used principles in the
environmental law and it was reaffirmed in
the Principle 10 of the 1992 Rio Declaration that states:
At the national level, each individual shall have appropriate
access to information
concerning the environment that is held by public authorities,
including information on
hazardous materials and activities in their communities Although
the Principles of Rio
Declarations are non-binding rules, they are well established
and are regarded by some as a rule
of customary international law40.
However, this basic principle of environmental law is not
accounted for sufficiently in the
Framework Convention. As mention above, in accordance with
article 21, there is a limited
-
16
possibility for exchange of, and for public access to,
environmental information concerning the
Caspian Sea. The Framework Convention provided the norm obliging
only for states to exchange
on regular basis information in accordance with provisions of
the Framework Convention. There
is no obligation for the states to prompt private companies to
share environmental information
about the marine environment to the public. The Framework
Convention just requires the
Contracting Parties to ensure public access to environmental
conditions of the Caspian Sea,
measures taken or planned to be taken to prevent, control and
reduce pollution of the Caspian
Sea41.
The Framework Convention borrowed that norm from the Convention
on Access to
Information, Public Participation in Decision-Making and Access
to Justice in Environmental
Matters42
(Aarhus Convention) that establishes: Each Party shall endeavor
to ensure that
officials and authorities assist and provide guidance to the
public in seeking access to
information43. Nevertheless, the former provides the public the
possibility to access
environmental conditions and the measures that much less by the
scope than information. It
can be interpreted by the governmental agencies or companies to
allow the public only to
monitor the environment of the Caspian Sea by their own or share
information with the public
about taken or planned actions. However, that norm in the
Framework Convention does not
oblige the sharing of environmental information regarding, for
example, losses of endangered
species or results of ecologic inspections or observations that
are fraught with danger to the
marine environment. Also, even though the Framework Convention
prompts the Contracting
Parties to develop a centralized database and information
management system to function as a
repository of all relevant data," that data is offered in
non-binding manner to use as as a general
source of information and education for specialists,
administrators and the general public.44.
-
17
The Aarhus Convention obliges the parties endeavor to guarantee
...in facilitating
participation in decision-making and in seeking access to
justice in environmental matters45 that
is not provided in the Framework Convention. The approach to
consider access to information
and the procedural rights in decision-making and redressing
processes as a whole of one element
is confirmed in Principle 10 of the 1992 Rio Declaration: States
shall facilitate and encourage
public awareness and participation by making information widely
available. Effective access to
judicial and administrative proceedings, including redress and
remedy, shall be provided46.
Consequently, the Framework Convention does not oblige the
Contracting Parties to
extend for their societies the ability to employ the
applications of information for
environmental protection purposes. The right of the public to
participate in the decision-making
process and access to justice is an integral part and corollary
to the right to get information. Also,
public participation is an indispensable part of sustainable
development, effective environmental
management, and environmental justice. This statement is
confirmed in many documents,
namely the 1992 Rio Declaration that declares that Environmental
issues are best handled with
the participation of all concerned citizens, at the relevant
level.47.
Although the Framework Convention provides the public access in
accordance with
their national legislation and taking into account provisions of
existing international agreements
concerning public access to environmental information48, those
legislation and agreements
cannot secure the public access and participation. For example,
it becomes apparent against the
background of human rights watch organizations statements
relating to the problems of
observance of fundamental human rights in all littoral countries
of the Caspian Sea, especially
about freedom of speech and movement. Also, it is a fact that
only three (Azerbaijan, Kazakhstan
and Turkmenistan) out of five countries are signatories to the
Aarhus Convention; only one
-
18
country (Russia) is a signatory of the United Nations Convention
on the Law of the Sea. Under
these conditions where the states assumed different
international obligations and have different
environmental interior regulations, the situation can cause
significant environmental problems
for the enclosed sea where all its parts and components are
complex and mutually related to each
other.
The Framework Conventions provisions with respect to public
access right and public
participation right are much more restrictive in comparison to
analogous conventions, codes
regulating regional sea or inland waters issues. For example,
the Code of Conduct on Accidental
Pollution in Trans-boundary Inland Water, which exists in order
to promote informed decision-
making by central, regional or local authorities in proceedings
concerning accidental pollution of
trans-boundary inland waters prescribes the countries to
facilitate participation of the public
likely to be affected in hearings and preliminary inquiries and
the making of objections in respect
of proposed decisions, as well as recourse to and standing in
administrative and judicial
proceedings49.
The Convention on the Protection of Marine Environment of the
Baltic Sea Area
(Helsinki Convention) prescribes what kind of information should
be available to the public: a)
permits issued, and the conditions required to be met; b)
results of water and effluent sampling
carried out for the purposes of monitoring and assessment, as
well as results of checking
compliance with water-quality objectives or permit conditions,
and c) water-quality
objectives50. That information would be sufficient for the
public to evaluate the degree of
threats to their health, flora and fauna of the marine
environment.
Also, the approaches to secure the public related rights can
ensure transparency and
broader involvement of the public to protect the marine
environment in the Caspian Sea, and
-
19
eventually increase effective realization of the objective of
the Framework Convention and other
important environmental acts.
An additional argument that the Framework Convention lacks real
possibilities for the
public to take part in the decision-making process is the
absence of any provisions for Non-
Governmental Organizations to take part in preparing main
documents that are corollaries of the
Framework Convention (for example, the protocols). There is no
article obliging the Contacting
States to organize public hearings on preparing domestic
legislature or regional agreements that
regulate the Caspian Sea basin.
Based on the information of the environmental group Crude
Accountability," the
Framework Convention itself was not prepared with the
participation of any environmental
NGO. The Ministries of Environmental Protection of Russia,
Kazakhstan, Azerbaijan conceded
that they did not attract environmental organizations to provide
commentary on the Convention.
Based on answers of Irans and Turkmenistans environmental NGO,
those countries were also
barred from the Convention discussion although at least half a
dozen organizations expressed
interest in receiving information about the Convention during
the preparation phase51
."
The Framework Convention contains too general obligations. The
majority of all
obligations of the states are defined with terminology of taking
all appropriate measures." For
example, The Framework Convention states that the Contracting
Parties shall:
(a) individually or jointly take all appropriate measures to
prevent, reduce and control
pollution of the Caspian Sea.
(b) individually or jointly take all appropriate measures to
protect, preserve and restore
the environment of the Caspian Sea52.
-
20
The meaning appropriate has a broad interpretation and can be
differently interpreted
by the littoral states. The states have different standards of
various pollutions, different
approaches to estimate harms and threats to the marine
environment, and different environmental
regulations for sea and rivers that are tributaries to the
Caspian Sea. Thus, whereas for one
country some environmental standards or environmental actions
can be considered as
appropriate, for another those measures can be viewed as
unsuitable.
Also, the International Environmental Law in the Seabed Disputes
Chamber in its
Advisory Opinion on Responsibility and Liability for
International Seabed Mining interpreted
the meaning necessary and appropriate measures that must be
assumed by the Contacting State
order to fulfill its obligation under the UNCLOS. The Chamber
concluded that a sponsoring
state must take to ensure that it has acted with all requisite
due diligencea state must have
effective laws and supporting administrative regulations in
place; simple contractual
arrangements are not sufficient. Those laws and regulations must
be regularly enforced by
monitoring and inspection. Moreover, they must be no less
effective than international rules,
regulations and procedures, [footnote omitted] primarily those
adopted by the Authority53.
Thus, ideally the meaning of appropriate measures that shall be
taken by the states
must be uncovered with prescribed timelines or mechanisms to
enforce the obligations;
otherwise it would lead to non-fulfillment of the obligations or
delaying of their resolution. For
example, the first Protocol (Protocol concerning Regional
Preparedness, Response and Co-
operation in Combating Oil Pollution Incidents) that should be
adopted right after the conclusion
of the Framework Convention was signed after eight years
(August, 2011). The Framework
Convention does not cover all states that can influence the
quality of water in the Caspian Sea.
The Framework Convention states that [these laws] shall be
applied to the marine environment
-
21
of the Caspian Sea, taking into account its water level
fluctuations, and pollution from land based
sources54.
Even though the Framework Convention can be applied to the sea,
the reservation of the
article with respect to pollution from land-based sources makes
the Framework Convention
applicable to the whole basin of the Caspian Sea. The notion of
pollution from land-based
sources implies all likely discharges into the sea, including
water, air, solid or immediate
coastal discharges into the sea. Hence, a basin approach should
be employed, and the Framework
Conventions scope includes all rivers and those tributaries that
eventually flowing to the
Caspian Sea. Based on Table 1, there are three rivers: Kura,
Sulak, Terek whose the riparian
countries: Armenia (AM), Georgia (GE), Turkey (TR) are not
signatories of the Framework
Convention.
The Kura river system including its tributaries is
trans-bordered by Turkey, Armenia,
Georgia, Iran, and Azerbaijan. This river system is polluted by
the discharge of poorly treated
or untreated wastewater from the 11 million people living in the
catchment area55. According to
the measurements made by Azerbaijan at the Georgian-Azerbaijan
border (the river flowing from
Georgia to Azerbaijan), the maximum allowable concentration
(MAC) [is] exceeded8-12
times for phenols, 2-3 times for oil products, 8-14 times for
metals, and 1-2 times for
sulphates56.
The basin of the Sulak River is shared by Georgia and the
Russian Federation. Even
though the river system is in decent environmental and chemical
status57
, the increasing
irrigation (that can impact on Caspian Sea level fluctuations)
and increasing number of human
settlements with untreated sewage (that can pollute the Caspian
Sea) have negative effects on the
basin.
-
22
The Terek River, whose riparian states are Georgia (upstream
country) and Russia
(downstream country), is the main natural asset in the Caucasus
area. This river is in decent
environmental and chemical status58
, but irrigation and sewage contamination can be negative
factors for the marine environment of the Caspian Sea in the
future.
It should be mentioned that in order to implement Article 7 of
the Framework
Convention, the Caspian littoral states signed the Protocol for
the Protection of the Caspian Sea
against Pollution from Land-based Sources and Activities
("Moscow Protocol") on December
12, 2012. Besides water emissions originating from land-based
points, the scope of the Protocol
(and thus the scope of the Framework of Convention) covers
inputs of polluting substances
transported through the atmosphere into the marine environment
of the Caspian Sea from land-
based sources and pollution resulting from activities that
affect the marine environment and/or
coastal areas of the Caspian Sea, including physical alteration
of the natural state of the coastline
and alteration or destruction of the landscape or habitats.59.
So, considering the possible
negative air impact, possible losses of fishes or other marine
fauna of the Caspian Sea originating
from the rivers that flow into the Caspian Sea (for example,
sturgeons), it makes sense to attract
Georgia, Armenia, and Turkey to join to the Framework Convention
or its agreements (that are
corollaries of the Framework Convention) as Contracting or
Non-Contracting Parties.
As mentioned above, there is still a significant problem with
vessel-source pollution
even after adoption of the Framework Convention. One of the
reasons for that situation is a lack
of regulation and control of this problem. The Framework
Convention requires the Contacting
Parties take all appropriate measures to prevent, reduce and
control pollution of the Caspian Sea
from vessels and co-operate in the development of protocols and
agreements to the Convention
prescribing agreed measures, procedures and standards to that
effect, taking into account relevant
-
23
international standards. The problem of possible different
interpretations of the term
appropriate have been already discussed above, and this is
applicable for this case as well.
Another problem is that the adoption of those protocols or
agreements controlling pollution from
vessels is not even planned by the Secretariat of the Framework
Convention.
Applying relevant international rules, it is also vague because,
as mentioned above, the
littoral states have not agreed on the legal status of the
Caspian Sea (in case of the sea,
UNCLOSs standards should be applied or customary international
law in the case of lake). Also
mentioned above, not all states are signatories of UNCLOS
convention or the International
Maritime Organizations conventions that UNCLOS refers. Thus, we
need to prescribe the
littoral states to adopt a protocol to prevent, reduce, control
and monitor pollution from vessels.
Another problem that can potentially degrade the marine
environment of the Caspian Sea
is the necessity to adopt unified standards for all sources of
pollution. It is important in case of
pending legal status of the sea or in case of giving the Caspian
Sea the status of a sea. The
problem is connected with the jurisdiction of the territory
where the sources of pollution can
occur. For example, it is problematic to define a threshold of
harm from pollution in neutral
waters (in case of sea scenario) or in the disputed area between
Turkmenistan, Azerbaijan and
Iran (in case of the current situation) because there would be
no applicable national standards,
and also international standards from other relevant conventions
that should be ratified by all
littoral states. Determining the unified standards of all
sources of pollution will also be
demanding in case of the application of Trans-boundary
Environmental Impact Assessment or
application of polluter pays principle or reference to the
obligation to use the resources in
such a way as not to cause harm to the marine environment of the
Caspian Sea60. Therefore, that
should be resolved by adopting an adequate protocol.
-
24
III. Conclusion
One of the main reasons why the Framework Convention does not
cover all necessary
problems is that the Framework Convention is a compromise
between different countries. That
document was adopted by the governments of new states that did
not have sufficient experience
to manage an independent country. Also, those governments that
are concerned to improve
economic situation in their countries do not attach adequate
importance to sustainable
development that is a necessary condition for sustainable
independence of any country.
Increasing popularity of the idea of the sustainable development
among people and influential
political groups of the Caspian region can be decisive factors
for initiating the adoption of
amendments the Framework Convention. Those above-mentioned
proposals and any other
proposals should be discussed with broad public participation
and should be adopted only after
public hearings. The Caspian Sea is a unique gift, and our
responsibility is to pass this gift on to
our future generations.
-
25
References
1 US EIA. Caspian Region, assessed 05/20/2014,
http://www.eia.gov/countries/regions-topics.cfm?fips=csr
2 Cox Rory and Doug Norlen. "The Great Ecological Game: Will
Caspian Sea Oil Lead to Environmental Disaster?"
January 1999. The Pacific Environmental Resources Center. 1
March 2000. 3 Rowell, Andrew "Crude Operators: The Future of the
Oil Industry" The Ecologist. Vol. 27. NO.3 May/June 1997. p.
99-107. 4 Mehdi Parvizi Amineh (November,2003). Caspian Energy:
A viable alternative to the Persian Gulf?. European
Institute of Asian Studies, 1 page,
http://www.eias.org/publication/briefing-paper/caspian-energy-viable-alternative-persian-gulf
5 Jeff Spath (2014). Focus on the Caspian. The Journal of Petroleum
Technology, assessed 05/20/2014 at
http://www.spe.org/jpt/article/6051-presidents-column-20 6
Markandya A. (2004). Gains of Regional Cooperation: Environmental
Problems and Solution. ZEF Discussion
Papers On Development Policy No. 80, Center for Development
Research, Bonn, pp. 24 available at
http://www.zef.de/uploads/tx_zefportal/Publications/zef_dp80.pdf 7
Id
8 Caspian Sea State of the Environment (2011). Report of the
Caspian Environment Programme. Tehran Convention
web-site, assessed 06/22/2014 available at
http://www.tehranconvention.org/IMG/pdf/Caspian_SoE_Eng_fin.pdf 9
Markandya A. (2004). Gains of Regional Cooperation: Environmental
Problems and Solution. ZEF Discussion
Papers On Development Policy No. 80, Center for Development
Research, Bonn, pp. 24 available at
http://www.zef.de/uploads/tx_zefportal/Publications/zef_dp80.pdf
10
Caspian Sea State of the Environment (2011). Report of the
Caspian Environment Programme. Tehran Convention web-site, assessed
06/22/2014 available at http://www.tehranconvention.org/IMG/pdf/
Caspian_SoE_Eng_fin.pdf 11
Antonenko, O. (2004). Russias policy in the Caspian Sea region:
reconciling economic and security agendas. In S.Akiner (Ed.), The
Caspian: Politics, energy and security (pp. 244262). New York:
RoutledgeCurzon. 12
US Energy Information Administration web-site assessed
06/22/2014, available at
http://www.eia.gov/countries/regions-topics.cfm?fips=csr 13
Cohen A. (September, 2002). Iran's Claim Over Caspian Sea
Resources Threaten Energy Security. The Heritage Foundation
web-site assessed 06/22/2014, available at
http://www.heritage.org/research/reports/2002/09/irans-claim-over-caspian-sea-resources-threaten-energy-security
14
Nick, M. (2005). Rethinking multinational corporate governance
in extractive industries: the Caspian development project and the
promise of cooperative governance. Vanderbilt Journal of
Transnational Law, 38(2), 577614, available at
http://heinonline.org/HOL/Page?handle=hein.journals/vantl38&div=22&g_sent=1&collection=journals#591
15
Zimnitskaya H. & Geldern J. (January 2011). Is the Caspian
Sea a sea; and why does it matter? The Journal of Eurasian Studies,
pages 1-14, available at
http://www.sciencedirect.com/science/article/pii/S1879366510000424
16
Id 17
Mamedov, R. (2001). International legal status of the Caspian
Sea: issues of theory and practice. The Institute of Geology and
Geophysics of Azerbaijan National Academy of Sciences web-site
assessed 06/22/2014 at
http://www.gia.az/view.php?lang=en&menu=47&id=835. 18
Sanei, F. (2001). The Caspian Sea legal regime, pipeline
diplomacy, and the prospects for Irans isolation from the oil and
gas Frenzy: reconciling Tehrans legal options with its geopolitical
realities. Vanderbilt Journal of Transnational Law, 34(3), 681845
available at http://heinonline.org/HOL/Page?handle=hein.journals/
vantl34&div=27&g_sent= 1&collection=journals#695 19
Sneider, D. (1993). Rich prospects spur Caspian Sea oil plans.
The Christian Science Monitor6, 4 August 1993. 20
Nassibli, N. (2004). Azerbaijan: policy priorities towards the
Caspian Sea. In S. Akiner (Ed.), The Caspian: Politics, energy and
security (pp. 157180). London: Routledge Curzon 21
Abbasov S. (2012). Azerbaijan & Turkmenistan: Renewing
Caspian Sea Energy Dispute. Eurosianet.Org, web-site assessed
06/23/2014 at http://www.eurasianet.org/node/65646
-
26
22
Tehran Convention (the official web-site of the Framework
Conventions Secretariat), History of the Convention, assessed
05/20/2014 at http://www.tehranconvention.org/spip.php?article1
23
Press TV web-site (January, 2013). Iran to sue Azerbaijan over
oil pollution in Caspian Sea, assessed 05/16/2014,
http://www.presstv.com/detail/2013/01/27/285888/iran-to-sue-baku-over-caspian-pollution/
24
Trend web-site (November, 2013).Pollution threatens Caspian Sea
seal, assessed 05/15/2014, available at
http://en.trend.az/regions/iran/2208040.html 25
ScanEx RDC Press Center web-site (31 January, 2013).
Satellite-based monitoring of oil spills in Caspian Sea: 2012
results, assessed 05/15/2014 at
http://press.scanex.ru/index.php/en/news/item/3749-sea 26
Article 2 of the Framework Convention available at Tehran
Convention (the official web-site of the Framework Conventions
Secretariat) http://www.tehranconvention.org/spip.php?article4
27
Article 5 a) of the Framework Convention available at Tehran
Convention (the official web-site of the Framework Conventions
Secretariat) http://www.tehranconvention.org/spip.php?article4
28
Rio Declaration on Environment and Development, The Report of
the United Nations Conference on Environment and Development. The
UN web-site assessed 06/01/2014 available at
http://www.un.org/documents/ga/conf151/aconf15126-1annex1.htm
29
UNEP Training Manual on International Environmental Law Manual
Training,
http://www.unep.org/environmentalgovernance/Portals/8/documents/training_Manual.pdf,
at page30 30
Article 5 (b ) of the Framework Convention available at Tehran
Convention (the official web-site of the Framework Conventions
Secretariat) http://www.tehranconvention.org/spip.php?article4
31
Philippe Sands, Principles of International Law (Cambridge:
Cambridge University Press, 2003, 2nd
edition), at 236 32
http://www.unep.org/Documents.Multilingual/Default.asp?documentid=97&articleid=1503
33
Article 5 (c) of the Framework Convention available at Tehran
Convention (the official web-site of the Framework Conventions
Secretariat) http://www.tehranconvention.org/spip.php?article4
34
Principle 7 of the Rio Declaration on Environment and
Development, The Report of the United Nations Conference on
Environment and Development. The UN web-site assessed 06/01/2014
available at
http://www.un.org/documents/ga/conf151/aconf15126-1annex1.htm
35
Article 17 Environmental Impact Assessment of the Framework
Convention available at Tehran Convention (the official web-site of
the Framework Conventions Secretariat)
http://www.tehranconvention.org/spip.php?article4 36
Id 37
Tehran Convention (the official web-site of the Framework
Conventions Secretariat)
http://www.tehranconvention.org/spip.php?article41 38
Id 39
Tehran Convention (the official web-site of the Framework
Conventions Secretariat)
http://www.tehranconvention.org/spip.php?article41 40
Training Manual on International Environmental Law, clause 25,
page 27 41
Article 21 of the Framework Convention available at Tehran
Convention (the official web-site of the Framework Conventions
Secretariat) http://www.tehranconvention.org/spip.php?article4
42
The Convention adopted by United Nations Economic Commission for
Europe (UNECE) and entered into force on 30 October 2001, available
at http://www.unece.org/fileadmin/DAM/env/pp/documents/cep43e.pdf
43
Article 2 of the Framework Convention available at Tehran
Convention (the official web-site of the Framework Conventions
Secretariat) http://www.tehranconvention.org/spip.php?article4
44
Article 19 of the Framework Convention available at Tehran
Convention (the official web-site of the Framework Conventions
Secretariat) http://www.tehranconvention.org/spip.php?article4
45
Id 46
Article 10 of the Framework Convention available at Tehran
Convention (the official web-site of the Framework Conventions
Secretariat) http://www.tehranconvention.org/spip.php?article4
47
Principle 10 of the Framework Convention available at Tehran
Convention (the official web-site of the Framework Conventions
Secretariat) http://www.tehranconvention.org/spip.php?article4
-
27
48
Clause 2 of Article 21 of the Framework Convention available at
Tehran Convention (the official web-site of the Framework
Conventions Secretariat)
http://www.tehranconvention.org/spip.php?article4 49
Clause 1 Section VII, Code of Conduct on Accidental Pollution in
Trans-boundary Inland Waters, adopted by the Economic Commission
for Europe at 1990, available at
http://faolex.fao.org/docs/pdf/eur16417.pdf 50
Convention on the Protection of Marine Environment of the Baltic
Sea Area entered into force on 17 January 2000, available at
http://www2.unitar.org/cwm/publications/cbl/synergy/pdf/cat3/helsinki_convention.pdf
51
Watters K. & Kinman M. CrudeAccountibilty (web-site). The
Framework Convention for the Protection of the Marine Environment
of the Caspian Sea: Omitting the Public Makes for a Weaker Document
available at
http://crudeaccountability.org/wp-content/uploads/2012/06/crude_convention_analysis_en.pdf,
page 3, assessed 05/15/2014 52
Article 4 General Obligations of Part II General Obligations of
the Framework Convention 53
International Environmental Law in the Seabed Disputes Chamber.
Advisory Opinion on Responsibility and Liability for International
Seabed Mining (ITLOS Case No. 17), page 10, available at
http://ssrn.com/abstract=1793216 54
Article 3 Scope of Application of the Framework Convention
available at Tehran Convention (the official web-site of the
Framework Conventions Secretariat)
http://www.tehranconvention.org/spip.php?article4 55
Drainage Basin of the Caspian Sea. UNECE web-site assessed at
06/10/2014 available at
http://www.unece.org/fileadmin/DAM/env/water/blanks/assessment/caspian.pdf,
page 99 56
Id., page 100 57
Id, page 111 58
Id, page 113 59
Tehran Convention (the official web-site of the Framework
Conventions Secretariat)
http://www.tehranconvention.org/IMG/pdf/Protocol_on_Pollution_from_Land_Based_Sources_and_Activities.pdf
60
Article 4 (c) of Framework Convention available at Tehran
Convention (the official web-site of the Framework Conventions
Secretariat) http://www.tehranconvention.org/spip.php?article4