Australia: Biodiversity Conservation and Ecotourism
By James Lee
Tourism
is one of Australia's fastest growing industries. It is a major source of foreign exchange, domestic product,
income, and employment. Within this
sector, a trend described variously as nature-based tourism and ecotourism has
emerged as a strong segment over the past few decades. The prospects for expansion of this trade,
based on both international and domestic visitors, are significant. Historically, the increase of nature based and
ecotourism worldwide was largely a result of the increase in awareness of the
plight of the world's diminishing biological diversity and a reaction against
mass tourism and its demonstrative lack of care of conservation issues.
Ecotourism
is originally defined as traveling to relatively undisturbed or uncontaminated
areas with the specific object of studying, admiring, and enjoying the scenery,
its wild plants and animals, as well as any existing cultural manifestations
found in these areas. In more recent
years, ecotourism is redefined as nature-based tourism that involves education
and interpretation of the natural environment and is managed to be ecologically
sustainable. The concept of ecotourism
has evolved over the past decade from a reaction to mass tourism to a force,
which is contributing to the general greening of the tourism industry. In this sense it can be seen as a process
and its importance in inducing change in the tourism industry may be more significant
than its categorization as a small niche market of small operators. The greening of tourism is essential for the
ecological and sociological advancement and sustainability of the industry.
Biodiversity,
biological diversity, is the variety within and among living organisms and of
the ecological systems they comprise.
Biodiversity conservation is a relatively recent term, which originates
from the concept of conservation of national parks and wilderness, wildlife,
landscapes and ecosystems, and is the result of better understanding of the
needs for conservation of biological diversity. Tntegration of biodiversity conservation and tourism development
has emerged as an important national objective, with strong support by
government, industry and the community.
The National Strategy for Ecologically Sustainable Development (1992)
addressed this relationship, noting that the central challenge is to develop
and manage the tourism in a way which conserves its natural resource and built
heritage base, and minimizes any negative environmental, societal, and cultural
impacts.
The
economic benefits of nature based and ecotourism can be measured in terms of
the total economic value that they yield to the community. Economic benefits are customarily measured
using the techniques of benefit-cost analysis, and are distinct from financial
values which are associated with market transactions and cash flows of
governments and private enterprises.
Total
economic value has several components:
1) Direct use values, such as those
derived from recreational and educational experience in natural areas.
2) Option values, comprising the value
placed on having an opportunity make use of natural areas at some future stage.
3) Vicarious use values, referring to the
value derived from knowing about the direct experiences of other people.
4) Existence value or the value associated
with the knowledge that natural system or species continue to exist.
5) Bequest values or the value derived
from the ability to bequeath natural assets to future generations.
6) Quasi-option values, which refer to the
value obtained from delaying exploitative actions to learn more about the
potential threats or risks to natural areas and the strategies or management
practices that may be put in place to avoid or minimize adverse impacts.'
Many
economic values find direct expression through market transactions,
particularly for direct uses. A good
example is the willingness to pay for ecotours or accommodation in natural
areas. Other values may not be
measurable in market data. Many people may
travel long distances for a nature-based experience, without necessarily paying
for use of the area. Techniques are
available to measure the value of the natural implicitly, such as the travel
cost method (TCM). TCM provides
information on use values; it is relevant to the valuation of biodiversity only
inasmuch as biodiversity or ecosystem attributes are the main factor attracting
people to particular sites.
Non-use
values are more difficult to measure, because markets often do not exist
through which people may express their values or preferences. A celebrated study by Krutilla and Fisher
(1975) introduced an interesting method (the threshold value approach) of
valuing natural areas when there is only limited information on the direct
value of preservation options. A
commonly used technique for the valuation of natural areas is the contingent
valuation method (CVM). Under this
technique a hypothetical market for some natural good or service is described
to a sample of subjects, who are then asked about their willingness to pay for
it. The mechanism through which values
are expressed is known as a "payment vehicle".
Application
of CVM is one way of determining whether people are prepared to pay for the
protection of biodiversity, and if so, how much. A typical application would be to determine the willingness to
pay for the preservation of biodiversity in designated natural areas, by means
of an entry fee, user permit or special management fund. A common misconception is that CVM is
necessarily restricted to non-market or existence values; in fact it can be
used to estimate the willingness to pay for direct use values. In some contexts, hypothetical markets for
natural attributes could be transformed into actual markets, even for existence
values. Proposals to introduce new
funding mechanisms designed to protect biodiversity could be pre-tested by
means of CVM and the payment vehicle could then become a reality. Such funding mechanisms include user fees,
permits, and special management funds, charges collected by tourism operators
and direct purchase of areas of ecological significance.
From
an industry perspective, financial rather than economic values are what count:
that is, net returns on their operations.
Net returns are an important part of the total economic benefits accruing
to the community: in a benefit-cost analysis, they are described as 'producers'
surplus'.
An
economic evaluation of ecotourism should include an assessment of public sector
investments and other costs required to support ecotourism activity, such as
roads, airports, water and sewerage and costs of managing natural areas,
including information systems, site supervision and monitoring activities.
Other
indirect effects of ecotourism may also be included in an economic evaluation. For example, if there is significant
unemployment in a particular region, ecotourism may create new job
opportunities. The value of such
employment would be an important element in a benefit-cost analysis. Input-output models may be used to predict
the possible role of ecotourism in alleviating regional unemployment. Care should be taken, however, in
interpreting the economic significance of indirect employment effects; they may
not all comprise economic benefits in the benefit-cost sense, even though their
incidence may be important for particular industries or segments of the work
force .
The
most comprehensive survey undertaken on financial and economic values of
protected natural areas in Australia is the study by Driml (1994). The main focus of the study is the Great
Barrier Reef but other areas are also included. I)riml has compiled a comprehensive data set with details of the
size of the area, the primary purpose of management, direct uses, the number of
visitors per year, annual expenditure by tourists and financial values of other
commercial activities. The study
provides estimates that when combined show that every year the Great Barrier
Reef, the wet tropics of Queensland, Kakadu, Uluru Kata Tjuta and Kosciusko
National Parks and the Tasmanian wilderness alone generate in excess of $2
billion from tourism as set out by the table below. The main results of the survey by Driml are summarized below.
Annual
Expenditure by Tourists to Six Protected Areas, 1991-1992.
Protected Area |
Annual Expenditure
from Tourism and Recreation ($m) |
|
|
Great Barrier Reef |
776 |
Wet Tropics |
377 |
Kakadu National
Park |
122 |
Uluru Kata Tjuta
National Park |
38 |
Tasmanian
Wilderness |
59 |
Kosciusko
National Park |
640 |
Total |
2012 |
Source: (Driml, p.6)
All
states in Australia have developed and adopted strategies for tourism and
nature-based tourism which recognize the fundamental importance of the natural
resource. Some have also recognized
that tourism-based activities have a basic requirement to channel some of the
revenue into the management and sustenance of natural resources.
The
policy and administrative mechanisms for placing values on the use of the
natural resources are mostly in place.
The challenge will be to design and implement systems that will not
disadvantage any particular group of operators, and at the same time be of
greatest advantage to the natural environment.
A
draft National Strategy for the Conservation of Australia's Biological
Diversity has been prepared by the Australian and New Zealand Environment and
Conservation Council (ANZECC Task Force on Biological Diversity 1993), in
consultation with the Agricultural and Resource Management Council of Australia
and New Zealand, the Australian Forest Council, the Australian and New Zealand
Fisheries and Aquaculture Council, the Australian and New Zealand Minerals and
Energy Council, and the Industry, Technology and Regional Development
Council. No peak tourism body was
included in consultations, although the views of local governments represented
by the Australian Local Government Association, business (including tourism),
industry, and the conservation movement was sought. The provisions of the Convention on Biological Diversity and the
draft national strategy prepared by the Biological Diversity Advisory
Committee, were taken into account in the preparation of the document. The goal of the draft Strategy is to protect
biological diversity and maintain ecological processes and systems. It aims to bridge the gap between current
activities and the effective identification, conservation and management of
Australia's biodiversity, and acknowledges the core objectives of the National
Strategy for Ecologically Sustainable Development and accepts its guiding
principles. The draft Strategy's
primary focus is Australia's indigenous biological diversity.
The
Draft Strategy covers all of Australia's biodiversity including terrestrial
marine and other aquatic
ecosystems
and those of external territories. The
establishment of a comprehensive, representative and adequate system of
ecologically viable protected areas is central to the conservation of
Australia's biodiversity. In addition,
the strategy recognizes the significant contribution environmentally
sympathetic management of nonreserve areas can make in meeting biodiversity
conservation objectives.'
Ecotourism
is considered to be an incentive for conserving natural areas, a source of
financial and physical resources for conservation, and a stimulus for an
environmental ethic that goes beyond ecotourism. Australia will have an ecologically sustainable ecotourism
industry that will be internationally competitive and domestically viable. Ecotourism in Australia will set an
international example for environmental quality and cultural authenticity while
realizing an appropriate return to the Australia community and conservation of
the resource.
1
James, D. The application of Economic Techniques in Environmental Impact
Assessment. Kluwer Academic Publishers,
Dordrecht.
2
Dixon, J.A. and Sherman, P.B. Economics of Protected Areas. Island Press, Washin-ton, DC.
3
Krutilla, J.V. and Fisher, A.C. The Economics of National Environments. Johns Hopkins University
Press,
Baltimore, 1975.
4
James, D. The application of Economic Techniques in Environmental Impact
Assessment. Kluwer
Academic
Publishers, Dordrecht.
5
Website: www.ecotourisni. com