The Economic Impacts of Ecotourism
By Kreg Lindberg, PhD Lecturer, Charles Sturt University 3 November
1996
There are two related, but distinct, economic concepts in ecotourism:
economic impact and economic value. This issues paper focusses on
economic impact, which refers to the change in sales, income, jobs,
or other parameter generated by ecotourism. A common ecotourism
goal is the generation of economic benefits, whether they be profits
for companies, jobs for communities, or revenues for parks. Ecotourism
plays a particularly important role because it can create jobs in
remote regions that historically have benefited less from economic
development programs than have more populous areas. Even a small
number of jobs may be significant in communities where populations
are low and alternatives are few.
This economic impact can increase political and financial support
for conservation. Protected areas, and nature conservation generally,
provide many benefits to society, including preservation of biodiversity,
maintenance of watersheds, and so on. Unfortunately, many of these
benefits are intangible. However, the benefits associated with recreation
and tourism in protected areas tend to be tangible. For example,
divers at a marine park spend money on lodging, food, and other
goods and services, thereby providing employment for local and non-local
residents. These positive economic impacts can lead to increased
support for the protected areas with which they are associated.
This is one reason why ecotourism has been embraced as a means for
enhancing conservation of natural resources.
Several studies in Australia and elsewhere have assessed the economic
impacts of ecotourism. Predictably, the level of benefits varies
widely as a result of differences in the quality of the attraction,
access, and so on. In some cases, the number of jobs created will
be low, but in rural areas even a few jobs can make a big difference.
Still, ecotourism benefits should not be oversold, or there may
be a backlash as reality fails to live up to expectations.
The impacts of ecotourism, or any economic activity, can be grouped
into three categories: direct, indirect, and induced. Direct impacts
are those arising from the initial tourism spending, such as money
spent at a restaurant. The restaurant buys goods and services (inputs)
from other businesses, thereby generating indirect impacts. In addition,
the restaurant employees spend part of their wages to buy various
goods and services, thereby generating induced impacts. Of course,
if the restaurant purchases the goods and services from outside
the region of interest, then the money provides no indirect impact
to the region -- it leaks away. Figure 1 illustrates some of these
impacts and leakages.
By identifying the leakages, or conversely the linkages within
the economy, the indirect and induced impacts of tourism can be
estimated. In addition, this information can be used to identify
what goods are needed but are not being produced in the region,
how much demand there is for such goods, and what the likely benefits
of local production would be. This enables policy makers to determine
priorities for developing inputs for use by the tourism or other
industries.
How, then, are these direct, indirect, and induced impacts to be
estimated? For small areas with non-diverse economies, there are
relatively few indirect and induced impacts, and there are relatively
little data available for modeling these impacts. Therefore, surveys
of visitors, residents, and/or businesses often are used to identify
tourism's direct impacts. For larger areas, such as states or countries,
economists have developed various techniques for estimating indirect
and induced impacts, including computable general equilibrium (CGE)
and input-output (IO) analysis.
Examples
| |
Driml and Common (see below for references) present the following
data on 1991/1992 annual visitor expenditure at the following
World Heritage Areas:
|
|
Great Barrier Reef
|
AU$776 million
|
|
|
Wet Tropics
|
AU$377 million
|
|
Kakadu
|
AU$122 million
|
|
Uluru
|
AU$38 million
|
|
Tasmanian Wilderness
|
AU$59 million
|
| |
Powell and Chalmers used input-output analysis to estimate
that Dorrigo National Park in New South Wales contributed
7% of gross regional output and 8.4% of regional employment.
|
| |
Lindberg and Enriquez used resident surveys and input-output
analysis to estimate local and national economic impacts associated
with tourism in Belize. National total (direct, indirect,
and induced) impacts for 1992 were estimated at US$211 million
in sales and US$41 million in personal income.
|
|
A common priority is to increase economic benefits, and the
traditional approach is to attract more visitors. Given that
negative impacts (environmental, experiential, sociocultural,
and economic) correspond, to varying degrees, to visitor numbers,
generally it is preferable to increase local benefits by:
|
|
|
increasing spending per visitor;
|
|
|
increasing backward linkages (reducing leakages); or
|
|
|
increasing local participation in the industry.
|
Spending per visitor can be increased through, for example, provision
of handicrafts where such provision currently does not exist. In
some cases, there may also be prospects for attracting higher-spending
visitors. Backward linkages can be increased through greater use
of local agricultural and other products. In order to increase backward
linkages and local participation in the industry, it may be necessary
to implement or expand capital availability and training programs.
Economic impact analysis can provide valuable information when evaluating
the costs and benefits of such programs.
For more information and examples
In an article for the Australian Journal of Environmental Management
(volume 2, number 1, pages 19-29), Sally Driml and Mick Common provide
data on visitor expenditure (direct impacts) and user fees collected
at five World Heritage Areas.
In their report for the NSW National Parks and Wildlife Service
(Regional Economic Impact: Gibraltar Range and Dorrigo National
Parks, 1995, available for $10 from NSW NPWS (02) 585 6333),
Roy Powell and Linden Chalmers use input-output analysis to estimate
the economic impacts of ecotourism at these national parks.
In their report for WWF
(US) (An Analysis of Ecotourism's Economic Contribution to Conservation
and Development in Belize, 1994), Kreg Lindberg and Jerry Enriquez
use resident surveys to estimate local economic impacts and input-output
analysis to estimate national economic impacts of tourism.
In a presentation at the 1996 Tourism and Hospitality Research
Conference ("Kate Fischer or Liz Hurley, Which Model Should
I Use?"), Trevor Mules discusses various economic impact models.
The proceedings are published by the Bureau of Tourism Research
(06) 279 7264.
The Australian
Bureau of Statistics publishes Information Paper, Australian
National Accounts, Introduction to Input-Output Multipliers,
Catalogue No. 5246.0, Fax (06) 252 5380.
If you have comments on this issues paper or want to add a relevant
reference, please contact Kreg
Lindberg
|