Student Clinic
Improving Enforcement and Compliance
with the Convention on International Trade in Endangered Species
Prepared for the World Wildlife Fund
by the Yale Environmental Protection Clinic
[public document]
INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . .2
I. CITES-BASED MONITORING AND ENFORCEMENT . . . . . . . . . . .4
Scientific Collaboration and Coordination . . . . . . . . .4
Listing Criteria. . . . . . . . . . . . . . . . . . . . . .5
Information Collection and Dissemination. . . . . . . . . .6
Permit Process. . . . . . . . . . . . . . . . . . . . . . .7
Loopholes in CITES. . . . . . . . . . . . . . . . . . . . .9
Capacity-Building . . . . . . . . . . . . . . . . . . . . 10
II. CITES-BASED INCENTIVES FOR COMPLIANCE. . . . . . . . . . . 13
Publicity and Education Campaigns . . . . . . . . . . . . 13
CITES Seal of Approval. . . . . . . . . . . . . . . . . . 14
Funding Mechanisms for Enforcement and Compliance Incentives15
III. DOMESTIC ENFORCEMENT. . . . . . . . . . . . . . . . . . . 18
Improving National Enforcement. . . . . . . . . . . . . . 18
Incentives to Corporations and Private Parties. . . . . . 19
IV. INTERNATIONAL ENFORCEMENT. . . . . . . . . . . . . . . . . 21
Trade Sanctions . . . . . . . . . . . . . . . . . . . . . 21
Regional Regimes. . . . . . . . . . . . . . . . . . . . . 22
International Criminal Justice Coordination . . . . . . . 24
International Tribunals . . . . . . . . . . . . . . . . . 25
CONCLUSION . . . . . . . . . . . . . . . . . . . . . . . . . . 27
INTRODUCTION
This options paper was prepared by three members of the
Yale Environmental Policy Clinic at the request of World Wildlife Fund
- USA to examine options to improve enforcement of and compliance with
the Convention on International Trade in Endangered Species of Fauna
and Flora (CITES). Section One suggests ways to improve CITES-based
enforcement mechanisms. Section Two proposes incentives that could be
implemented to achieve compliance. Section Three recommends measures to
be taken at the national level. Section Four turns to international means
of implementing the Convention.
CITES was signed in Washington, DC in 1973 and entered into
force two years later. One hundred twenty-five nations are currently party
to CITES, making it the most important international wildlife conservation
treaty. CITES attempts to regulate international trade in endangered plant
and animal species by requiring member nations to establish a system whereby
export and/or import permits must be obtained from the appropriate government
authorities before trade in species listed in the treaty's appendices
can legally occur. Some 34,000 species are listed in these appendices,
which reflect a graduated system. Trade in Appendix I species, defined
as "endangered," is the most strictly regulated. Virtually all
commercial trade in these species is prohibited. In the limited instances
in which trade is allowed, both import and export permits are required.
Commerce in Appendix II species, termed "threatened," requires
export permits from the country of origin. Appendix III species, which
are added to the list by countries wishing to protect their native flora
and fauna, need export permits only if they originate in the listing country.
Although CITES has accomplished much to protect endangered
species from the ravages of commercial over-exploitation, there remain
major difficulties in achieving enforcement of and compliance with its
provisions. One obvious problem is that there exists no supranational
government or structure capable of ensuring that states honor their international
obligations. Instead, the global political order is characterized by the
ideology of national sovereignty. In this respect, the problems faced
by CITES in convincing sovereign nations to act in ways perceived to conflict
with their national interests are shared by every international convention
or regime. Another major problem is that CITES itself is weakly drafted
in places and contains several critical loopholes which are extensively
exploited by black marketeers. In addition, CITES parties have failed
to commit sufficient financial resources to implement and enforce CITES
both domestically and internationally. The massive underfunding of government
agencies mandated to enforce the Convention and the severe financial constraints
faced by the CITES Secretariat are inevitably reflected in the inability
of CITES countries and the Secretariat to monitor the legal trade in wildlife
effectively, let alone eliminate the lucrative black market. Again, these
problems are not unique to CITES, but are weaknesses of the international
system in general.
The following analysis draws on lessons learned from other
international treaties and regimes, both in the environmental arena and
in other areas such as human rights, trade, intellectual property, and
arms control. Some of the suggestions presented below are taken from these
lessons, while others stem from a recognition that innovative measures
are needed to provide incentives for private actors to comply with CITES.
I. CITES-BASED MONITORING AND ENFORCEMENT
Scientific Collaboration and Coordination
CITES parties should cooperate in scientific research and population estimation
efforts to evaluate the status of Appendix I and II species and any detrimental
effects of legal trade under CITES. A Scientific Authority could be established
as a permanent staff function of the CITES Secretariat to coordinate and
disseminate scientific information on CITES-listed species.
Populations of many species are in decline due to habitat
modification or destruction as well as the pressures of legal and illegal
trade. Increased scientific research and population estimation are needed
to enable CITES parties to reevaluate the status of listed species on
a regular basis and to allocate scarce resources available for wildlife
protection and CITES enforcement. To evaluate the status of threatened
or endangered species, nations should cooperate in gathering scientific
data on species, using ecosystemic or bioregional research strategies.
Specific examples of joint research efforts that might be conducted are
the evaluation of the effects of noncommercial trade in Appendix I species
and the evaluation of legal trade in the most critically threatened Appendix
II listed species. This information would be invaluable in determining
whether further measures such as uplisting a species from Appendix II
or banning all trade in an Appendix I species are necessary.
Nations should endeavor to make the results of scientific
research on wildlife available to other CITES parties. To facilitate the
compilation and dissemination of this data, member nations should consider
establishing a Scientific Authority with a permanent staff under the direction
of the Secretariat to act as a central collection point and clearinghouse
for all scientific information relating to CITES-listed species. The Scientific
Authority could provide technical training and support to national scientific
authorities, management authorities, and enforcement officials, and coordinate
international scientific research efforts.
Listing Criteria
CITES parties should consider moving Appendix II listed species to Appendix
I within five years unless population levels adequate to sustain trade
are demonstrated to exist. Member nations should reconsider changing the
scope of CITES to allow trade only in specifically approved animal species.
Unfortunately, current and accurate data on the populations
and distributions of many Appendix II species is lacking. In the absence
of such data, many countries may be trading in Appendix II species which
are actually endangered rather than merely threatened, thereby undermining
the purpose of CITES. Member nations should consider uplisting all Appendix
II species to Appendix I after five years unless CITES parties or individuals
wishing to continue trade in these species submit evidence to the proposed
CITES Scientific Authority that populations sufficient to sustain trade
exist. Those plant and animal populations that are validated within the
five-year period and remain on the Appendix II list should be revalidated
on a definitive time schedule.
Member nations should reconsider substantively revising
the current listing procedures to implement a reverse listing approach.
Only those species shown to be non-endangered or non-threatened would
be permitted in international commercial trade. No other species could
be legally traded until member nations or individuals wishing to place
it in commerce demonstrated to CITES that the species is neither endangered
nor threatened. The newly listed species could only be exported from those
specific countries to which the scientific information pertains. This
procedure would shift the burden to those wanting to trade in a species
for which data on population and range is nonexistent or inadequate to
prove that commercial trade would not jeopardize its survival. As an experiment,
a reverse listing appendix for a narrow category of species, such as mammals,
could be implemented. If successful, this could serve as a model for other
categories of species.
Information Collection and Dissemination
The CITES Secretariat or other competent organization should consider
compiling information about listed species on CD-ROM.
The Secretariat or other competent agency could computerize
and disseminate CITES parties' annual reports and infractions reports.
These databases and the training and equipment to use them
should be acquired by or provided to member nations and other interested
parties.
One of the most crucial tools available in the monitoring
and policing of international wildlife trade is information. Thus, another
option to consider would be to develop an efficient mechanism to manage
the vast quantities of information relevant to CITES and the wildlife
trade. Following the lead of such organizations as Australia's CSIRO (Commonwealth
Scientific and Industrial Research Organization) and the U.S. Department
of Agriculture, which have developed CD-ROM systems for cargo inspectors
to identify beetle larvae and fruit flies, CITES should computerize a
standardized identification system for all CITES listed species, derivatives,
and parts.
This information would include scientific data as to range
and population, treaty reservations, and identification techniques for
species, parts, and derivative products, as well as look-alike species.
The database should be configured in such a way that non-experts in wildlife
(e.g., customs agents and inspectors) can easily identify the species
of a specimen or derivative product by its notable characteristics. Each
species should be cross-referenced by scientific nomenclature, common
names in the treaty's working languages, and a unique database reference
number to be used on all import and export permits. Where possible, the
CD-ROM should include pictures and other descriptive graphics as well
as text.
This database, and the training and equipment to use it,
should be acquired by or provided to all member nations for use by customs
and enforcement agents at all designated ports of entry. The advantages
of this system would be its universality of use, its accessibility to
non-experts, its facilitation of rapid specimen identification, and its
ability to be updated to reflect changing scientific information.
A computerized system for cataloging and cross-referencing
annual reports and infractions reports would also significantly enhance
the ability of the CITES Secretariat and other interested parties to monitor
legal and illegal wildlife trade. Organizing the information on a CD-ROM
database would enable the Secretariat, government officials, and non-governmental
organizations to study the effects of wildlife trade by species, nation,
region, year, or any other logical parameter.
The barriers to the implementation of a computerized data
management system are obvious: the startup costs of establishing this
database would require significant funding commitments. Moreover, effective
implementation would require all CITES parties to acquire potentially
expensive technology and to train their enforcement officers to use it.
These barriers, while formidable, are not insurmountable. To begin with,
the scientific data necessary to establish such a database already exists,
so constructing a database is a matter of compiling and organizing current
information into a useful format. The money, technology, and training
necessary to implement a computerized data management system might be
donated by developed nations, philanthropic foundations, and computer
companies. If implementation barriers can be overcome, a computerized
system has an enormous potential to increase enforcement through more
efficient monitoring and information exchange.
Permit Process
The CITES Secretariat should consider assuming the responsibility of
providing member nations with standardized permit forms.
All exporters, importers and transporters of live species
should be registered with the CITES Secretariat.
A permit tracking system should be developed to require
exporters, importers and transporters to maintain copies of the permit
and to report their trading activities to the CITES Secretariat at scheduled
intervals.
The permit process needs to be strengthened to prevent forgery
and fraud and to improve accountability and record reconciliation. A uniform
and tamper-resistant permit that government officials charged with enforcing
CITES can easily recognize as genuine will help to eliminate some of the
problems of forgery and corruption that plague the current permitting
system. The CITES Secretariat should create and distribute a standard
permit form in the three official CITES languages using printing techniques,
such as watermarked security paper, that inhibit the production of forged
copies. Unique numbered sets should be issued to each member nation, which
should be required to provide records of the permits it issues.
CITES parties should also consider implementing an international
registration system whereby all individuals or organizations that wish
to export or import listed species or transport live species must register
with CITES. If the application were approved, a unique registration number
would be issued. Requirements established for registration could include:
a commitment to open and accurate record-keeping, an agreement to allow
inspection of records and facilities, a written plan for the safe transport
of live animals and plants in accordance with internationally accepted
standards, and a prescribed certification statement signed by an individual
owner or organization official validating the authenticity of the registration
application and agreeing to be held personally liable for criminal or
civil penalties if found in violation of CITES provisions. The registration
numbers of the importer, exporter, and transporter would be included on
the import and export permits issued by national management authorities.
The permit process might build on the model offered by the
manifest requirements for shipping hazardous wastes within the United
States under the Resource Conservation and Recovery Act. Both importers
and exporters must keep records and supporting documents and make them
available to national and international inspectors. Exporters would be
required to reconcile their records to prove shipments were delivered
with all the necessary approvals. Importers, in addition to keeping copies
of the export/import permit, would also maintain verifiable records on
the final disposition of the species. The records of transporters, importers,
and exporters should be subject to inspection for a period of years as
determined by CITES.
The registered exporters, importers and transporters
would submit information such as the registration of the parties involved
in the transaction, the quantity of species, the identification number
of the species, and the date to CITES on a periodic basis. The data should
be submitted in a standard format. CITES should integrate this information
into a computerized database to facilitate identification of trends that
could point to abuse of the system and decline of populations, as well
as other parameters that would be useful in gathering scientific information
or identifying illegal traders.
Loopholes in CITES
CITES should be amended to forbid nations from taking reservations to
listed species.
No wildlife trade should occur with non-party nations or
with member nations whose procedures are not in compliance with CITES
standards.
Oversight provisions of the captive-breeding program should
be strengthened.
Exemptions for sports hunting of Appendix I species, for
household and personal effects, and for pre-existing stocks should be
eliminated.
Parties to CITES should no longer issue reservations that
exempt them from the requirements of the Convention with respect to specific
species. Although the ability to take reservations may once have been
an important inducement to sovereign nations for signature and ratification,
a current trend in international environmental law is towards conventions
that specifically forbid signatories from taking reservations to its provisions.
Two significant examples are the Montreal Protocol on Substances that
Deplete the Ozone Layer and the Basel Convention on the Control of Transboundary
Movements of Hazardous Wastes and their Disposal.
In addition, member nations should discontinue wildlife
trade with non-CITES parties as well as other member nations whose procedures
are not in compliance with CITES provisions. This is necessary as illegally
traded species are often obtained by taking advantage of the relaxed standards
applied to imports or exports from non-party states or by using forged
documents from parties with poor enforcement procedures. Again, both the
Montreal Protocol and the Basel Convention have precedential value, as
both contain provisions banning trade with non-member nations in the substances
subject to treaty regulation.
Furthermore, the current lack of oversight mechanisms in
the captive-breeding exemption enables smugglers to launder wild-caught
animals through these operations. All newborn captive-bred animals should
be registered with the government by a certain age. Registration should
include a government-licensed non-removable identification number that
will remain with the animal throughout its life. The live birth registration
and number must be noted on the export/import permits. Animals not registered
and marked by a certain age should be considered wild-captured and ineligible
for the captive-breeding exemption.
Exemptions for sports hunting of Appendix I species should
be eliminated, as should exemptions for household and personal effects
and exemptions for stocks of listed species and products claimed to have
been in existence prior to ratification by a member nation. These exemptions
facilitate illegitimate trade in protected species and make it very difficult
for customs and wildlife agents to ascertain the origin of species and
derivative products. These exemptions also perpetuate the public perception
that the individual taking of endangered species is acceptable as long
as the specimen is not blatantly intended for organized commercial trade.
Capacity-Building
The CITES Secretariat should consider developing a comprehensive and
uniform training curriculum, including video tapes, manuals, and interactive
CD-ROM disks, and should have the authority to approve each nation's CITES
training program.
The CITES Secretariat and CITES parties should cooperate
in providing technical training to all customs and wildlife agents as
well as awareness training for local police forces. Wildlife enforcement
agents should receive highly specialized police training to combat smuggling
and poaching.
Member nations to CITES should consider developing an independent
international corps of wildlife inspectors.
Technical training of wildlife and customs agents is frequently
inadequate because of the scientific complexity of species identification,
the intricacy of the permitting process, and the lack of national resources
devoted to training. A uniform program of instruction in the basics of
CITES implementation, supplemented by information developed for regions
or specific countries, would be of enormous benefit in improving enforcement.
The CITES Secretariat, in consultation with experts in customs, international
law enforcement, and international law, should consider developing a training
curriculum and sponsoring "train the trainer" sessions. The
Secretariat should have the responsibility of reviewing a member nation's
entire training program periodically and approving it or suggesting improvement
measures. This oversight authority might include access to each country
to audit the training program and test individuals randomly. Unapproved
training programs or ineffectively run programs could be viewed as non-compliance
with CITES.
Trained individuals need access to basic and advanced training
materials that they can take back to their countries. The Secretariat
could develop a uniform series of video tapes and manuals explaining the
entire CITES program, to be dubbed or translated into the local language
as necessary. These materials may need to be supplemented by regional
or local information. As discussed above, a CD-ROM database of the listed
species containing pictures and keying information needs to become the
working tool for all field agents. Training to use this tool is particularly
important since non-scientists are required to make science-based decisions
about species on a regular basis.
Each nation could designate an official to coordinate the
CITES training program. Nations could enact legislation that requires
a minimum number of hours of training, including initial and refresher
courses, for each customs and wildlife agent. Successful completion of
this training could be a condition for employment as for wildlife agents.
In addition, highly specialized police training for wildlife law enforcement
personnel engaged in combatting smuggling and poaching should be encouraged.
Cooperation between developed and developing states is particularly important
in this regard. To a lesser extent, police officers should receive CITES
awareness training, to gain knowledge of the potential for criminal activity.
CITES parties should consider developing an independent
international corps of inspectors under the direction of the CITES Secretariat.
This corps would function to verify compliance with CITES provisions,
and would inspect a nation's or corporation's compliance and enforcement
procedures either at the invitation of the nation or when violations are
reported by other nations, non-governmental organizations, or private
parties. The membership of the corps would be drawn from experts in the
fields of natural science, law, administrative policy, and enforcement.
They would have access to all parts of the country including habitat areas,
zoos, scientific research labs, records and facilities of wildlife import/exporters,
governmental records (for example, training records, import/export permits,
enforcement actions), and captive-breeding farms. Reports of the corps,
including suggestions for improving compliance and enforcement, would
go back to the Secretariat for verification, then to the inspected entity
for clarification, rebuttal, and implementation of suggestions. Final
reports would be released to the public.
Various international agreements have set precedents for
inspections to verify compliance with treaty obligations. These agreements
include: the Intermediate Nuclear Forces Treaty, the Treaty on Conventional
Armed Forces in Europe, and the International Atomic Energy Agency's Safeguards
Agreements. In addition, the International Convention for the High Seas
Fisheries of the North Pacific Ocean, contains enforcement provisions
which allows appropriate officials of any party to board a fishing vessel
found in waters where that party has agreed to avoid exploiting a species
of fish. The vessel and records may be inspected. The observation of an
violation or probable cause to believe a violation has occurred enables
the inspection team to arrest the crew and seize the vessel.
II. CITES-BASED INCENTIVES FOR COMPLIANCE
Publicity and Education Campaigns
Information about offending states, companies, individuals and goods
should be well publicized.
Education about the benefits to humans of endangered species
and biodiversity should be encouraged on a grand scale.
Education about alternatives to endangered species products
should be provided to reduce consumer demand.
Publicity and education are two critical elements to increase
public awareness and decrease the demand for commercial trade in endangered
species and derivative products. Commercial over-exploitation of many
wildlife species is driven by the demands of zoos, circuses, museums,
traditional healers and craftspeople, the fashion and pet industries,
and collectors. Without a reduction in demand, increased enforcement will
never succeed in diminishing legal trade and eliminating illegal trade.
The success in drastically reducing the ivory trade serves as one example
of the effectiveness of education and publicity in decreasing the demand
for a wildlife product. In the current international regime, information
is one of the most important tools states, organizations and individuals
can employ to effect change.
Negative publicity about governmental corruption or the
ineffectiveness of a nation's implementing legislation and internal enforcement
mechanisms may affect its ability to engage in diplomacy and negotiation
with other countries, attract investment, and promote tourism. In addition,
doubt may be cast on a state's legitimacy and reliability, especially
with regard to its image as a dependable participant in the international
community. Negative publicity about private offenders can have profound
effects on their actions as they seek to improve their images in the eyes
of their customers and the general public.
Education programs are equally important in addressing the
endangered species problem. Individual consumers must understand the dangers
posed to the earth and its component ecosystems by their choice of products.
This requires education about the effects of species utilization and the
alternatives to endangered species products. Consumers must realize that
products derived from endangered species, such as certain traditional
medicines, must be replaced by those containing more commonplace or synthetically
derived substances. Individuals must recognize that their demand for these
products is contributing to the destruction of the global environment.
Many organizations and the CITES Secretariat have
engaged in publicity and education campaigns. These projects should be
continued and expanded in both producing and consuming nations. Special
attention should be given to the latter nations; without a market, producing
states will not feel the compelling need to allow or engage in species-endangering
actions.
CITES Seal of Approval
A CITES Seal of Approval could be developed as a positive incentive
to private parties and corporations engaged in sustainable wildlife trade.
Publicity about the Seal of Approval to make consumers aware
of its meaning would provide an incentive for zoos, manufacturers, and
wildlife importers and exporters to participate in this program.
A CITES Seal of Approval would acknowledge compliance with
CITES standards pertaining to species, permits, shipping and handling
methods, and documentation. The Seal could also acknowledge contributions
to wildlife conservation efforts by private parties and corporations involved
in wildlife trade, farming, or research into alternatives to wildlife
for use in consumer goods. Zoos, merchants, corporations, and individuals
would qualify for the CITES Seal of Approval, as would goods derived from
species harvested in a sustainable manner. Wildlife traders and shipping
companies could be recognized for their compliance with international
guidelines to minimize the risks to live specimens of cruel treatment,
injury, and mortality during shipment. This Seal of Approval, if publicized
sufficiently in conjunction with an education campaign, could increase
the market competitiveness of the recipients and act as a financial and
public relations incentive for compliance.
The member nations would follow Secretariat guidelines in
granting the Seal of Approval to qualified entities within their jurisdiction;
these grants would be reviewable by the appropriate governmental agency
on an annual or biennial basis to ensure continuing compliance. The grant
of the seal would also be reviewable by the Secretariat, which would be
empowered to consider relevant information submitted by other CITES parties
or non-governmental organizations. Each member nation would bear the responsibility
for ensuring that only qualified organizations, persons, or goods would
receive the Seal; governmental abuses of the grants would be sanctionable
as a violation of CITES. Funding for the Seal of Approval program could
come from a tax on wildlife products as well as from fines levied on illegal
wildlife trade.
The member nations and the Secretariat would annually publicize
those parties certified, decertified, and refused certification under
the Seal of Approval program, and the reasons for the certification or
lack thereof. Such positive publicity would provide important incentives
for private actors to come into compliance with CITES. As most people
are essentially law-abiding citizens, they seek to associate with those
who they feel are the same. In addition, if environmentally conscious
organizations and individuals seek to promote those institutions receiving
the Seal within their clientele, the purchasing power and charitable contributions
of conservation-minded people can be brought to bear directly in overcoming
the economic incentives in illegal wildlife trade.
Funding Mechanisms for Enforcement and Compliance Incentives
Member nations should consider the effectiveness of the current financial
apparatus and evaluate new funding mechanisms and sources.
Funds could be used to increase the capability of the Secretariat
by providing more money for monitoring enforcement, publicity and education
campaigns, scientific research and evaluation, database development and
enforcement agent training.
Finding more funding and developing creative financing methods
should be a top priority. It will require large amounts of money to carry
out necessary scientific research, monitor wildlife trade, and effect
the necessary enforcement measures as well as to implement the education
programs needed to reduce public demand for endangered species.
CITES is currently funded by its member nations, who contribute
to the triennial budget of the Trust Fund based on their contributions
to the United Nations. However, this funding is insufficient to develop
and manage adequate enforcement mechanisms. Funding must be increased
if the CITES Secretariat is to undertake any significant new enforcement
initiatives. Member nations should consider renegotiating the method by
which contributions to the CITES budget are currently allocated. One possibility
is to replace it with an assessment system based on a percentage of the
gross national product of each nation, with developing countries assessed
a lower percentage than developed countries. This system would have the
advantage of replacing the outmoded United Nations scale, which no longer
reflects global economic realities, and basing national contributions
to CITES on equitable principles.
In addition, programs to solicit private contributions to
the CITES Trust Fund from concerned individuals, corporations, and environmental
organizations could be an important source of funds. Publicity campaigns
such as the proposed CITES Seal of Approval that highlight the names of
contributors, if they wish to be known, could be highly effective in this
regard.
For those states concerned about raising the funds for contributions
to CITES, wildlife consumption taxes and tariffs could be used. A possible
danger, however, is that a country will become dependent on trade in endangered
species to provide the funds for its CITES assessment. This should be
avoided by applying these taxes and tariffs to nonendangered wildlife
trade in addition to those species listed under CITES.
Developing states could also receive bilateral or multilateral
financial assistance as an incentive to forego the economic advantages
of trade in endangered species and to fund enforcement mechanisms and
personnel. The Montreal Protocol provides an example of successful multilateral
assistance: it creates a fund to provide money and technology to assist
developing countries in decreasing their dependency on chlorofluorocarbons
(CFCs). This is an excellent demonstration of how a multilateral fund
established under an international treaty can help developing countries
implement environmentally sound policies that will not unduly hinder their
economic growth.
Many of the suggestions presented in this paper need funding
to be effective. Although not all of these alternatives are discussed
in this analysis, activities for which funding is needed include:
Strengthening the CITES Secretariat to enhance its enforcement and compliance
monitoring capabilities.
Scientific research about endangered species, their habitats and their populations.
Development of international databases of endangered species, parts and
derivative products, wildlife traders and CITES violators.
Development of a computer network to track and verify permits.
Training of national and international enforcement agents.
Education and publicity campaigns.
Research into alternatives to wildlife products.
Research and promotion (if appropriate) of sustainable use and farming methods.
Preservation of endangered species in zoos and captive breeding programs for
reintroduction into the natural habitat.
Economic alternatives for native gatherers of wildlife.
Funding for wildlife sanctuaries and habitat protection.
Debt-for-wildlife swaps.
Reparations for wildlife-caused damage.
III. DOMESTIC ENFORCEMENT
Improving National Enforcement
Member nations of CITES that have not done so should implement legislation
to establish or increase criminal and civil liability for illegal wildlife
trade.
CITES parties should grant non-governmental organizations
and foreign nationals standing to press charges under civil statutes against
illegal wildlife traders and to apply for injunctive relief to block the
issuance of import or export permits to suspicious shipments.
Member nations must make information on their activities
relevant to CITES available to interested parties and the general public.
CITES parties might consider conditioning military and development
aid on the fulfillment by recipient nations of their CITES obligations.
All member nations should implement or improve national
legislation establishing civil and criminal penalties for persons who
capture, destroy, or trade illegally in endangered species inside and
outside their borders. Furthermore, member nations should seriously consider
harmonizing these penalties, the better to deter illegal traders. (See
Cyrille de Klemm, Guidelines for Legislation to Implement CITES, IUCN
Environmental Policy and Law Paper No. 26, 1993). The implementing legislation
should grant legal standing to conservation organizations to bring civil
suits against the government or individuals. It should also provide for
extradition to other member countries of individuals accused of violating
CITES requirements. In addition, non-governmental organizations and other
appropriate private parties should have standing to appeal the granting
of import and export permits, and should have the ability to submit relevant
information to the tribunal adjudicating such an appeal.
At the national level, compliance with CITES requirements
needs to be evaluated by the appropriate authorities within the government
and by independent organizations. This can only be accomplished if CITES
parties undertake to disseminate information on their official activities
relevant to CITES. Governments should provide in their implementing legislation
for the publication of information on export and import permits granted
by the Management Authority, and should make available to the public their
Annual Reports filed with the Secretariat.
Member nations might consider the possibility of unilaterally
conditioning security and/or economic assistance on compliance by recipient
nations with their CITES obligations. This mechanism has proved effective
in the United States aid allocation process in the context of human rights.
Congress is required by statute to evaluate the human rights record of
a recipient state before granting military assistance (22 U.S.C.
2304) or financial assistance (22 U.S.C. 2151n). If a recipient
government engages in a consistent pattern of gross violations of internationally
recognized human rights, Congress may not approve assistance to that regime
(with the exception of assistance that directly benefits needy people).
To facilitate this evaluation process, the State Department compiles and
publishes country-by-country human rights reports annually. The United
States is also required, under 701 of the International Financial
Institutions Act, to use its vote in international financial institutions
such as the World Bank to advance human rights by seeking to channel international
assistance to non-human rights abusers. Despite the likely effectiveness
of parallel measures to promote wildlife protection through the granting
or withholding of foreign assistance, realistically, the political will
to develop these measures is not likely to be high.
Incentives to Corporations and Private Parties
Tax and tariff relief can be given to corporations and individual wildlife
traders who comply with CITES provisions.
Government funds should be committed to promote research
and development of substitutes for wildlife products.
Governments could fund publicity, reward, and protection
programs for individuals providing information on criminal and civil violations
of CITES.
Incentives to corporations and private individual, if developed
and aggressively implemented, could encourage full compliance with wildlife
trade laws, provide positive publicity to responsible actors, and make
"business as usual" less economically viable for illegal traders.
Companies and traders that comply with CITES trade provisions
could be given tax and tariff relief as incentives to ensure their present
and future cooperation with and adherence to CITES standards. Such a program
would require nations to adopt standards for measuring compliance by trading
entities. These standards could be the same as those used in awarding
the CITES Seal of Approval. Any product carrying the Seal would automatically
receive tariff relief and any company qualifying for the Seal would be
given a tax rebate or deduction.
Unfortunately, this type of tariff or tax relief may not
be allowed under the General Agreement on Tariffs and Trade (the GATT).
GATT panels have been reluctant to recognize the legitimacy of environmental
regulations that hinder free trade, as demonstrated in the decision in
the tuna-dolphin dispute between Mexico and the United States. The same
lack of an exemption for international environmental concerns that hinders
the effective use of trade sanctions could negate the proposed relief
provisions. Free trade agreements must be amended to provide adequate
means for effectuating global environmental policy.
Member nations, especially consumer nations, should fund
research on the development of alternative products as substitutes for
wildlife products. Corporations, research institutes, and universities
should receive government incentives to develop new substitute products.
These incentives should include not only research funding but also positive
publicity such as the CITES Seal of Approval.
Member nations could also provide funds to publicize (if
appropriate), reward, and protect (if necessary) persons who provide information
regarding criminal and civil violations of CITES. Encouraging people to
come forward by promising financial rewards and protection from retribution
has had a long and successful history in the criminal justice system of
the United States. One source of funds for this program could be the seizure
and sale of the personal and real property of illegal wildlife traders,
such as cars, boats, and houses. The United States has used this approach
in combatting the drug trade under the Racketeer Influenced and Corrupt
Organizations (RICO) Act. Other funding sources might include fines levied
on illegal operations and taxes on wildlife products.
IV. INTERNATIONAL ENFORCEMENT
Trade Sanctions
Member nations should utilize trade sanctions against states which do
not comply with CITES provisions when other mechanisms do not work.
Sanctions could be imposed unilaterally or multilaterally
either without relying on a specific CITES mechanism or within the CITES
framework.
CITES parties could impose trade sanctions on non-wildlife
products to achieve swifter compliance with treaty obligations.
Trade sanctions are a historically effective method of compelling
states to comply with environmental objectives. The United States has
authorized the use of trade sanctions to enforce compliance with CITES
via the Pelly Amendment to the Fisheries Protection Act of 1967. The first
actual use of the Pelly Amendment is the current imposition of sanctions
against Taiwan to gain its compliance with CITES standards on rhinoceros,
tiger and other endangered species trade. The United States has also previously
employed sanctions and the threat of sanctions to obtain compliance with
the International Convention for the Regulation of Whaling and the current
whaling moratorium. In fact, in the case of the whaling treaty, the application
of sanctions seems to have been the only method that achieved compliance
as other nations have effectively blockaded all other means of enforcement
described in that convention. In a move to enhance formal trade sanctions
as an international treaty enforcement mechanism, the Montreal Protocol
has implicitly included trade sanctions as a means to compel states to
comply with the treaty's requirements to decrease chlorofluorocarbon (CFC)
usage.
However, trade sanctions should be applied only when no
other options are available, as there are dangers inherent in their use.
First, many governments are unwilling to apply sanctions to major trading
partners but may use them freely against less important nations. For example,
the U.S. may be unwilling to use sanctions against Japan for fear of starting
a trade war. The U.S. would, however, be less reluctant to use sanctions
against smaller, less economically powerful states.
Another problem with sanctions is their often unilateral
nature. The international community frequently regards unilateral sanctions
as retaliatory, mean-spirited and protectionist. Imposition of multilateral
trade sanctions by a unified international community or bloc of nations
would contribute to a perception that such sanctions are effective and
legitimate instruments of international diplomacy. Multilateral sanctions
could be imposed by groups of nations operating outside the official CITES
framework. Alternatively, a resolution/protocol could be added to CITES
to provide an official mechanism for instituting sanctions against recalcitrant
states. The Standing Committee currently has power to suggest that sanctions
be used, as in the recent case of Italy, but this language needs to be
strengthened to encourage action.
A further impediment to the use of trade sanctions against
CITES violators is that sanctions are usually limited to wildlife and
wildlife products. Although these are not negligible import and export
items they are certainly only a small part of a much larger picture. States
should be willing to extend sanctions to goods other than wildlife products.
Such a move would have much greater impact on non-complying states and
demonstrate the seriousness of the international community with respect
to protection of endangered species.
Finally, it is possible that trade agreements such as the
GATT may hinder the use of trade sanctions by declaring them violative
of the free trade provisions of those treaties. Previous decisions of
GATT panels seem to indicate that trade sanctions against countries based
upon their nonperformance of environmental treaty duties may not be interpreted
as valid exceptions to free trade requirements. For trade sanctions to
be acceptable, agreements such as the GATT must be modified to allow exceptions
for international environmental treaty obligations.
Regional Regimes
CITES parties could negotiate and implement regional agreements to enhance
cooperation in monitoring and enforcing CITES.
Regional agreements signed pursuant to global environmental
treaties may pose several advantages over the global treaty standing alone.
The smaller number of states involved allows the agreement to be more
narrowly tailored to suit the geographical, biological, economic, and
political considerations affecting the region in question. A regional
agreement allows similarly situated countries to pool their resources
and take advantage of shared information and increased cooperation. It
also enhances the possibilities of protecting threatened ecosystems and
species across coherent bioregions.
One example of a regional agreement signed under the auspices
of a global environmental treaty is the 1991 Bamako Convention on the
Ban of the Import into Africa and the Control of Transboundary Movement
and Management of Hazardous Wastes within Africa, negotiated by African
nations as a regional agreement under the 1989 Basel Convention on the
Control of Transboundary Movements of Hazardous Wastes and their Disposal.
The Bamako Convention, which has not yet received the necessary ratifications
to come into force, bans the importation of all hazardous wastes into
African member nations. This agreement could provide a useful model for
CITES nations in particular regions that want to curtail or eliminate
trade in certain highly endangered species.
Other examples of regional regimes are found in the areas
of human rights and trade. Organizations such as the Commission for Environmental
Cooperation (established by the North American Free Trade Agreement) as
well as the European Commission of Human Rights (established by the European
Convention for the Protection of Human Rights and Fundamental Freedoms)
are empowered to mediate inter-governmental disputes and receive information
from non-governmental organizations and private parties on violations
of treaty agreements.
Regional agreements may enhance the effectiveness of CITES
monitoring by promoting exchange of scientific data and information on
individuals and corporations engaged in legal and illegal wildlife trade.
They may also facilitate multilateral cooperation in prosecuting illegal
trade in the region carried out by multinational corporations or syndicates.
The first such agreement was signed in September of 1994, when ministers
from Kenya, South Africa, Swaziland, Tanzania, Uganda, and Zambia signed
the Lusaka Agreement on Cooperative Enforcement Operations Directed at
Illegal Trade in Wild Fauna and Flora. This agreement, open to accession
by any African nation, will combat the illegal trade in wildlife by forming
a multinational task force to facilitate cooperation among the CITES parties
and carry out cross-border investigations.
Member nations who enter into regional agreements should
strive to ensure that their legislation implementing both CITES and the
regional agreement brings their operating requirements and procedures
into conformity, standardizes incentives and penalties, and harmonizes
reporting requirements. The regional agreement should not derogate from
or undermine CITES provisions in any way. The intergovernmental taskforce
empowered to coordinate or enforce the actions of the member nations should
emulate the regional human rights regimes in establishing a system for
receiving and investigating evidence of illegal trade brought by non-governmental
organizations or private parties. This intergovernmental taskforce should
also be empowered to examine allegations of corruption or improper conduct
on the part of national officials.
International Criminal Justice Coordination
Member nations should cooperate with Interpol in establishing a system
to track criminal activity in the international wildlife trade.
CITES parties could sign an international extradition agreement.
An international system is needed to maintain records of
criminals convicted of violating wildlife laws. An agreement should be
reached with Interpol to provide a mechanism for gathering and disseminating
information about criminal activity involving wildlife trade. Member nations
could provide technical, financial, and human resource support to the
system.
A general extradition agreement signed by all member nations
could be implemented. This would provide a simple and effective mechanism
for the extradition of accused persons from one member nation to another
to stand trial for violating the extraditing nation's laws with respect
to CITES. This proposal is similar to the enforcement provision contained
in the 1976 Convention on the Protection of the Archaeological, Historical,
and Artistic Heritage of the American Nations.
International Tribunals
CITES parties could form international or regional tribunals in which
civil and/or criminal charges can be brought against state and/or individual
violators.
The tribunal(s) could allow the CITES Secretariat, member
nations and/or private parties to bring suits to enforce CITES provisions
or to prosecute wildlife violators.
The tribunal(s) could have the power to order declaratory
judgments, injunctive relief, civil damages, trade sanctions (in the case
of state violators) and criminal penalties (in the case of individual
violators).
Member nations could enact domestic legislation giving full
faith and credit to the decisions of the tribunal(s).
International or regional tribunals, capable of hearing
civil or criminal complaints, would be useful to encourage the implementation
of CITES in individual countries and to prosecute wildlife violators when
domestic remedies are inadequate due to nonenforcement of treaty obligations
or lack of an independent judiciary that can competently adjudicate CITES
complaints. Civil tribunals have been organized pursuant to the American
Convention on Human Rights (under the auspices of the Organization of
American States) and the European Convention for the Protection of Human
Rights and Fundamental Freedoms.
Both instruments create a commission and a court. The commission
under both conventions has jurisdiction to accept petitions against states
from individuals, organizations, and other states. If it finds merit in
the petition it can attempt to mediate a friendly settlement between the
petitioner and the state involved. If this effort is unsuccessful, the
commission may refer the case to the court. Other than the commission,
only states may bring claims before the court. The courts in both conventions
may order declaratory or injunctive relief as well as damages. Unfortunately,
both treaties allow a state party to accept or reject the court's jurisdiction
at any time. In addition, there are no specific enforcement mechanisms
that the court can implement to guarantee that its orders are carried
out.
This situation raises the concern that judgments of an international
court will be ignored by affected states. National courts must become
more willing to enforce judgments against a state or individuals that
have been ordered by foreign and international courts. There has been
some progress in achieving national enforcement of international arbitral
awards under the Convention on the Recognition and Enforcement of Foreign
Arbitral Awards. Many national courts have been willing to accept and
enforce awards from independent arbitral tribunals without additional
judicial review except where the order is explicitly contrary to the public
policy of the enforcing state.
Furthermore, states have submitted themselves to arbitral
tribunals under rules described in the Convention on the Settlement of
Investment Disputes between States and Nationals of Other States (ICSID).
This treaty allows nations to resolve disagreements with investors by
agreeing at the time the original investment contract is executed to submit
any disputes to arbitration before a private tribunal. This convention
has seen a significant number of successful outcomes, as awards allocated
through this process have been upheld in national courts. It is important
to note that in these cases the states agreed to the court's jurisdiction
in contracts with individual investors. In the CITES case, however, where
there is no contract there is a need for automatic jurisdiction without
explicit consent from CITES members.
The proposal for a criminal court is based upon the examples
of the post-World War II Nuremburg and Tokyo Tribunals and the current
War Crimes Tribunal associated with the Bosnian conflict. However, these
international criminal courts have only been implemented under the most
limited of circumstances. Although there has been persistent talk of creating
a permanent international criminal court for the purpose of prosecuting
human rights abusers, such a court has never been considered a serious
political objective in the current international arena.
We include this suggestion on our list of possible enforcement
mechanisms as something to work towards for the future. Both international
civil and criminal tribunals will be a necessary part of enforcement of
international treaties if independent states are not diligent in their
own enforcement actions. Unfortunately, such fora will not come into existence
until states become willing to relinquish part of their sovereignty and
allow themselves and their citizens to be tried in courts outside their
boundaries.
CONCLUSION
The major difficulty with CITES, lack of enforcement, is
a common characteristic of most, if not all, international treaties. However,
movement is being made toward rectifying some of these shortcomings. The
pace may seem glacially slow, but change is occurring, as nations become
more cognizant of the global scope of the harms we are inflicting on our
planet. Despite the weaknesses and imperfections of current environmental
treaties, nations must be encouraged, cajoled, and pressured to fulfill
their treaty obligations, even if only in an incremental fashion. It is
important to remain aware of how other international treaties are approaching
the problem of enforcement, and how their evolutions and innovations can
be applied to CITES.
It is also evident that international commercial over-exploitation,
the primary subject of CITES, is only one threat faced by wildlife. The
34,000 species extended a measure of protection by CITES represent a tiny
fraction of the planet's threatened biodiversity, when compared to the
1.5 million species currently known to science and the millions more species
estimated to exist. These species may disappear from the face of the earth
before we ever discover them, let alone find a commercial use that would
make them eligible for CITES protection. The species-by-species approach
is already outdated, and must be augmented if not replaced by an ecosystemic
approach to habitat conservation. The international community must ensure
that existing and future environmental agreements address environmental
conservation and species protection in a holistic manner.
Nonetheless, for all of its philosophical and practical
weaknesses, the CITES agreement has an important role to play in combatting
one highly visible and lucrative component of the wildlife holocaust.
The options presented in this paper should be viewed within this context.
Any one of these proposals, if implemented alone or in tandem with others,
will improve CITES enforcement or compliance. Realistically, it will require
an intensive cooperative effort on the part of the CITES Secretariat,
member nations, and non-governmental organizations to bring any of these
proposals to fruition. Perhaps more practically, future enforcement efforts
will have to be directed at putting pressure on the root cause of commercial
over-exploitation of endangered species - the workings of the market and
its private actors.
Yale Center for Environmental
Law and Policy
Sage Hall
205 Prospect Street
New Haven, CT
Telephone: 203.432.3123
Fax: 203.432.6597
Email: barbara.ruth@yale.edu
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