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The Parties to the Convention
on International Trade in Endangered Species of Wild
Fauna and Flora (CITES) have recognized, in Articles
III and IV, that international commercial trade in plants
and animals must not be detrimental to the survival
of species, or in other words, that it must be sustainable.
Too often, use of a species is claimed to be sustainable
in the absence of evidence to support this claim. Such
evidence should be provided by those who wish to label
a use “sustainable”. The following criteria
have been developed to assist Parties when assessing
the sustainability of trade in wild fauna and flora.
The criteria may be adapted and applied when assessing
the sustainability of other types of uses. Proposals
to remove or reduce the level of protection afforded,
or to start or increase international commercial trade
in, a species should meet these criteria.
1. Information is collected
Sufficient information is collected on
the population of a species used, and on the social
and economic factors affecting it, to permit a conclusion
that the level of use is not detrimental to the long-term
survival of the species throughout its range, or detrimental
to its habitat or ecosystem, and that this level of
use produces conservation benefits sufficient to justify
the use.
Valid scientific information is needed on: a) the size,
structure, dynamics, status and trend of the population
(such as recruitment, natural and human caused mortality,
immigration, emigration, mating system, age structure,
age distribution, sex ratio, density, growth rates,
age to sexual maturity, dispersal and ranging behavior,
disease, genetic composition); b) the status and trend
of habitats or other ecosystem components is necessary
for the survival of the population; c) the relationship
between the population and associated species and communities
(such as predators, prey, seed dispensers, pollinators,
competitors, etc); and d) abiotic factors (such as pollution
and climate) that might influence the status and trend
of the species or supporting ecosystem. Information
is needed on the types and levels of past, current,
and projected use, and the social, cultural, political
and economic factors affecting or likely to affect use.
2. A science-based management system
is in place
A science-based management system is developed
and implemented to ensure that use of a species is not,
and will not become in the future, detrimental to populations
or species or their habitats and ecosystems.
The management system adapts and adjusts in response
to biological changes in the population of a species,
or type or level of use of the population, or its habitat
or supporting ecosystem. Such a system requires continued
monitoring of the effect of use, both legal and illegal,
on the managed population or species and its habitat
and ecosystem. The management system: a) is based on
a management plan that summarizes the basic information
on which management is established, sets out the steps
by which the effect of use on the population or species
and its habitat and ecosystem are monitored, details
how use types and levels are adjusted based on the monitoring,
and describes how uses are regulated; b) manages biological
populations as a whole, including cooperative management
of populations straddling international borders; c)
addresses the cultural, social, political or economic
factors that affect use; d) ensures that markets are
not stimulated beyond the limits of the population;
e) develops a mechanism by which use will be terminated
if it becomes detrimental to the survival of the population;
and f) ensures independent monitoring and access to
scientific information on which management is based.
3. The Precautionary Principle is applied
The precautionary principle is rigorously
applied in order to reduce the risk of harm to populations
or species and their habitats and ecosystems.
The precautionary principle has been adopted in many
international agreements, including CITES, which in
Resolution Conf. 9.24 (Criteria for Amendment of Appendices
I and II) defines the term as follows: “Scientific
uncertainty should not be used as a reason for failing
to act in the best interest of the conservation of the
species.” Application of the precautionary principle
includes a mechanism for rapidly scaling back or stopping
the use if necessary to avoid harm to wild populations
or species and their habitats and ecosystems.
4. Government policies, laws and institutions
are in place
Government policies, laws and institutions
are adopted and enforced to ensure that use of a species
is not, and will not become in the future, detrimental
to wild populations or species and their habitats and
ecosystems.
Laws are enacted to establish appropriate user fees
and management payments that can be used to ensure proper
enforcement and implementation of laws and regulations.
State and local conservation and other agencies are
established, trained, and equipped to enforce applicable
statutes and regulations. Administrative and criminal
sanctions are established and enforced to deter and
punish illegal uses such as poaching and smuggling.
A wild population of a species whose range crosses or
straddles international borders is subject to a management
agreement between the countries concerned. International
agreements are adhered to and implemented. Activities
within a State’s jurisdiction or control do not
impair the viability of wild species in another State
or in other areas of international jurisdiction or control
do not impair the viability of wild species in another
State or in other areas of international jurisdiction.
Species are protected from avoidable negative impacts
of military activities.
5. People living in the vicinity of
the used population are empowered and experience benefits
Economic benefits from the use are directed
equably among those involved in the use including people
living in the vicinity of the used population (“local
people”). Such benefits reduce the detrimental
impact of such people on the survival of the population
or species and its habitat and ecosystem. Governments
involve local people in decisions affecting the use
while continuing to base management decisions on science.
Local people agree to make adjustments to current uses,
and take other actions as necessary to ensure successful
implementation of the management plan.
6. Economic sustainability is demonstrated
All costs associated with the proposed
use are carefully calculated or projected. Such costs
include those associated with biological monitoring,
management and enforcement needed to ensure that the
use is not, and will not become in future, detrimental
to wild populations or species and their habitats and
ecosystems. Fees and taxes or other means exist to ensure
that these costs are borne by those profiting from the
use.
7. Long-term conservation benefits are
demonstrated
The use provides demonstrable long-term
conservation benefits to the wild population or species
(such as increased anti-poaching efforts) and its habitat
and ecosystem (such as protection of critical habitat)
and ensures the recovery of depleted populations. Proposals
for new uses should demonstrate significantly greater
conservation benefits than those provided by the existing
conservation regime.
8. The use is compatible with other
uses of the species and is not detrimental to other
species
Theuse of a species is compatible with
other uses of the species and is not detrimental to
other populations or species and their habitats and
ecosystems.
9. Animals are protected from cruelty
and suffering, and incidental mortality is avoided
Animals are protected from cruelty and
suffering. Incidental mortality of animals or plants
of the species subject to use or other species (such
as mortality caused by the use of unselective collection
techniques or by the mistreatment of live specimens
in capture, holding, transport or shipping) is avoided.
Collection of scientific information is non-lethal unless
otherwise unattainable. The welfare status of the animals
used (such as the conditions under which they are captured,
held, transported, killed) is recorded, assessed, and
monitored.
These Criteria were prepared in August 1996 by the Wildlife
Use Working Group of the Species Survival Network, an
international coalition of organizations committed to
the promotion, enhancement, and strict enforcement of
the Convention on International Trade in Endangered
Species of Wild Fauna Flora (CITES). The following organizations
are members of the Working Group and endorse these Criteria:
Animal Welfare Institute, Defenders of Wildlife, Environmental
Investigation Agency, Humane Society of the United States,
Humane Society International, Humane Society International-Australia,
International Wildlife Coalition, Wildlife Conservation
Philosophy Specialist Group of Japan, Mountain Gorilla
and Rainforest Direct Aid, IUCN Turtle Specialist Group,
Royal Society for the Prevention of Cruelty to Animals,
Tusk Force.
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