d. A MISCELLANY
Australia: Urban invasive
species
Many Australian
protected areas in and near cities are severely impacted by invasive species,
especially feral cats and dogs and garden plants that go wild. Local
authorities are helping to control these invasives. Here are two examples:
·
Dandenong Ranges National Park
(IUCN Category II), in the northeastern suburbs of Melbourne, has trouble with
feral cats that prey on wildlife, including ground-dwelling birds. The local
government, the Shire of Yarra Ranges, has enacted strict regulations
controlling pet cats, including a night curfew.
·
Blue Mountains National Park (IUCN
Category II), 100 km west of Sydney, has a serious problem with exotic plants
spreading from private gardens. The park is one of seven protected areas
within the Blue Mountains World Heritage Site. It lies within the city of Blue
Mountains, which calls itself “The City within a World Heritage National
Park.” The city has a public information program aimed at encouraging property
owners to remove exotic invasives and replace them with plants indigenous to
the immediate area, especially those that are wildlife-friendly.
Web sites: Shire of
Yarra Ranges: http://www.yarraranges.vic.gov.au (go to “Infractions”); City of
Blue Mountains: http://www.weedsbluemountains.org.au.
Brazil: The
São
Paolo Greenbelt
The Forest
Institute of the São Paulo state government is using a biosphere reserve as a
mechanism for managing a greenbelt.
São Paulo
has a population of 20.2 million and is the world’s fifth largest urban
agglomeration. It is surrounded by the São Paolo City Green Belt Biosphere
Reserve, composed of several state parks and other protected areas. The Forest
Institute is responsible for coordination. The greenbelt is the subject of a
subglobal assessment under the global Millennium Ecosystem Assessment (Victor
2006; MA 2006, UNESCO 2006b).
In 1993,
the greenbelt was made an integral part of the Mata Atlântica Biosphere
Reserve, which covers important parts of the Atlantic rain forest that
stretches over 3,000 km along Brazil’s coast. Within the southern part of the
biosphere reserve are 25 protected areas that comprise the Southeast Atlantic
Forest Reserves World Heritage Site.
Biosphere
reserves are areas recognized within the framework of UNESCO’s Man and the
Biosphere Programme. They consist of a core protected area, or a cluster of
such areas, a buffer zone, and an outer transition area. They bring together
stakeholders ranging from conservation agencies and scientists to economic
interests and local authorities. In addition, one of their main purposes is to
foster international exchange of information and experience.
Under
UNESCO guidelines, each biosphere reserve is intended to
fulfill
three complementary functions: (1) conservation of landscapes, ecosystems,
species, and genetic variation; (2) local economic development that is
culturally, socially, and ecologically sustainable; and (3) research,
monitoring, education, and information exchange related to local, national,
and global issues of conservation and development.
Although
several biosphere reserves already exist alongside or close to cities, their
role has generally been limited to coordinating conservation activities. The
idea of a distinct category of urban biosphere reserve is being considered in
several countries and by UNESCO. The proponents of this new category offer a
different perspective, among other things, on how managers of protected areas
can cope with (and take advantage of) urbanization and its impacts. Their
ideas and energy could also help to invigorate the biosphere reserve concept,
a good concept that has yet to reach its potential (Trzyna 2005a, 18-19).
Web sites:
São Paulo City Green Belt Biosphere Reserve: http://www.iflorestal.sp.gov.br/rbcv
(Portuguese). Mata Atlântica Biosphere Reserve: http://www.rbma.org.br
(Portuguese). UNESCO Man and the Biosphere Urban Group: http://www.unesco.org/mab/ecosyst.urban.shtml.
Cape Verde: Second-home enclaves
on the island of Sal
Cape Verde, an
independent republic composed of a group of islands in the mid-Atlantic Ocean
some 450 km west of Senegal, is a good example of how tourism, second-home,
and retirement development is affecting vulnerable environments formerly
considered remote.
Much of this is on the
island of Sal, which is only 30 km long by 12 km wide. Sal’s population is
14,000; its largest town, Vila dos Espargos, has 8,000 people. One resort
complex, Murdeira Beach, being built by an Irish Company, has 1,400 residences
in its first stage alone. The company was attracted to Sal by “prices that are
a fraction of those for comparable sites in Europe and the Caribbean” (Brass
2006, 20). Sal has several terrestrial protected areas and one marine natural
reserve, Baia da Murdeira. One area, the Salt Marsh of Pedra Lume, is on the
Tentative List of World Heritage Sites (UNESCO 2006c). It is unclear what
impacts the new development will have on these areas, or on the migratory
birds that use the island as a stopover site. Also, the islands have meager
and erratic rainfall and periodic droughts. Although a desalting plant is
planned, many of the hotels and second homes have swimming pools and are
notorious consumers of water. Similar developments are being built or planned
elsewhere on Sal and on four other islands in the archipelago (CVP 2006).
Research on sustainable
tourism has found that such “enclave tourism” and similar developments often
have hidden economic and social costs, especially in poorer countries (UNEP
2001). Cape Verde’s 421,000 people have a per capita income equivalent to only
U.S. $6,000. Overgrazing and introduced species have already caused severe
loss of natural habitats and stressed a number of endemic plant and animal
species (Stuart 1990, 65-66).
China: Hong Kong’s Country and
Marine Parks
Hong Kong is a fine
example of how pressures of urban intensification on protected areas can be
resisted.
In the preface to his
book Above the World: Stunning Satellite Images from above Earth, Sir
Ranulph Fiennes (2005) describes widespread evidence of environmental damage
around the globe, but makes special note of Hong Kong, “which glows at the
space cameras in the orange hue that denotes fertile vegetation.” Indeed, in
Hong Kong, where 7 million people live in an area of little more than 1,000 sq
km, some 40% of the land is in protected areas, as well as much of the marine
environment. This is one of the best illustrations in the world of how natural
areas can thrive within or right next to dense cities.
The urbanized parts of
Hong Kong, a special administrative region of China, are among the most
crowded areas in the world. The city is a thriving business and financial
center whose population is projected to grow to 8.7 million by 2050. There is
constant demand to open up more land for urban development.
How has this pressure
been successfully resisted? First of all, Hong Kong has strong land-use
planning and regulation. This is essential, but certainly not enough by
itself; many other places have regulations that look good in print but are not
enforced. According to Fook Yee Wong, head of Hong Kong’s Country and Marine
Parks, the key has been fostering a sense of community ownership by organizing
citizen volunteers to carry out projects ranging from nature education to park
clean-up; by involving NGOs, including those represented on government
advisory bodies; by providing information to the public via publications,
signage, and the Internet; and, not least, by encouraging his own staff to
love nature (Wong 2005, 58-61). A citizens’ support group, Friends of the
Country Parks, while recognizing that Hong Kong in many respects “already does
very well” believes “a comprehensive conservation policy would assist the
preservation and management of biodiversity” (Dudgeon and Corlett 2004, 262).
Web sites: Hong Kong Country and Marine Parks: http://www.afcd.gov.hk
(Cantonese/English). Friends of the Country Parks: http://www.focp.org.hk
(Cantonese/English).
Kiribati: Impacts of dense
population on a small scale
In island countries that
are small in both land area and population, migration into towns from outlying
areas can concentrate sewage, garbage, and toxic waste. Where there are
inadequate means of disposing of it, this can have serious impacts on
biodiversity. Tarawa Atoll in the island Republic of Kiribati in the Pacific
Ocean is an extreme example (Connell and Lea 2002, 41, 180-185). Surrounded by
a coral reef that was damaged during a major battle in World War II and
subsequently by pollution and construction, Tarawa includes some of the most
densely populated islands in the world. These include Betio islet, which has a
land area of 1.7 sq km and a population density of over 7,000 per sq km, more
than that of Hong Kong (Taoaba 2006). Although about half of Tarawa Atoll has
been declared a conservation area, it is not clear whether regulations have
been issued or enforced (FAO 2002). It is also unclear what measures are being
taken to manage waste and prevent further damage to the reef from urban
pollution. The country has limited resources (per capita income is equivalent
to U.S. $1,900 a year).
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