Elsevier

Marine Policy

Volume 101, March 2019, Pages 8-14
Marine Policy

PACT or no PACT are tourists willing to contribute to the Protected Areas Conservation Trust in order to enhance marine resource conservation in Belize?

https://doi.org/10.1016/j.marpol.2018.12.002Get rights and content

Abstract

The primary objective of this paper is to determine whether tourists are willing to pay (WTP) fees to support conservation in Belize and, if so, to determine their maximum willingness to pay. This is an important issue for Belize and for all countries that heavily rely on the quality of their environmental resources to attract tourists. From 1996 to 2017, the Protected Areas Conservation Trust (PACT) has charged a $3.75US conservation fee to all tourists upon their departure from Belize. In April of 2017, this fee was raised to $20.00US, but not without controversy. In May 2012, February 2013, and again in May 2014 almost 400 tourists were surveyed to determine if raising the fee was possible and by how much. Results suggest a significant percentage of tourists are willing to pay for conservation in Belize; many in excess of the current fee of $20.00US. So far, the increased fee does appear to have had any impact on tourism arrivals. This empirical observation, combined with the results of this paper, are important pieces of information as it relates to conservation finance in Belize and has potential implications for conservation finance in other tropical destinations.

Introduction

Like most Caribbean countries, Belize is heavily dependent on the tourism industry and the tourism industry in Belize is heavily dependent on the quality of the environment: particularly marine ecosystems [17], [4], [41]. Tourism is the nation's principle source of foreign exchange, and the main use of the Belize Barrier Reef (http://belizetourismboard.org/wp-content/uploads/2018/07/TravelTourismDigest2017v2.pdf). The Belize Barrier Reef is the largest in the western hemisphere, second in size only to the Great Barrier Reef in Australia. Established as a World Heritage Site in 1996, this diverse system of reefs, cayes and atolls is responsible for approximately 30% of national GDP via fisheries production and tourism and contains one of the highest levels of marine biodiversity in the Atlantic [14], [30]. It is the quality of the mangroves, sea-grass, coral reefs, and sea life that attract tourists to Belize [43]. Therefore, protecting and improving the quality of these environmental resources is important for economic development [26], [39]. Failing to protect marine resources jeopardizes future economic prosperity by deterring tourists and compromising the flow of ecological services [4]. Unfortunately, the agencies that manage and protect these resources are often underfunded [21], [25], [38]. Ideally, those who derive benefits from using the environment, including tourists, should bear the cost of preservation and conservation [47]. One mechanism for accomplishing this is the use of entrance or exit fees. These entrance/exit fee systems can be viewed as payment for environmental services (PES) received by the tourists [28], [3].

From 1996 to 2017, every international visitor to Belize has been charged $3.75US/$7.50BZ upon their departure. This fee is part of Belize's conservation strategy and the revenue goes directly into the Protected Areas Conservation Trust, better known as PACT. From 2012 to 2014 (the time period covered by this study), Belize received an annual average of more than 300,000 overnight visitors (not including cruise ship passengers).

In April of 2017, the Government of Belize decided to raise the conservation fee to $20.00US/$40.00BZ. This created an outcry from tourist industry providers, arguing the fee would “cripple” tourism in Belize.1 This research is aimed at better understanding the effect this increase might have on visitation and whether the fee could be even higher than $20.00US. The primary research question addressed is whether tourists visiting Ambergris Caye and Caye Caulker, Belize, are willing to pay higher fees in order to enhance marine conservation programs. Another question explored is whether or not informing people about the current $3.75 fee would result in respondents anchoring their stated willingness to pay at the existing fee level.2

Hopefully, this information can be used to help establish appropriate conservation fees that support improved marine and coastal management without significantly reducing tourist arrivals. This examination of tourists’ willingness to pay for conservation programming in Belize provides a unique addition to the current marine conservation literature and may provide valuable information to policy makers in determining whether and how much to increase the current exit fee for the PACT in the future. This research also contributes to the non-market valuation literature by examining the potential anchoring effect associated with the provision of information about existing fees in contingent valuation surveys.

The rest of the paper is structured as follows: Section 2 briefly provides some background on ecosystem services and their importance to Belize, a summary of the history, current context, and future plans for PACT, and reviews similar studies on willingness to pay to protect marine resources. Section 3 details the design of the survey, its implementation, and the results of the analysis. Section 4 discusses the results and concludes the paper.

Section snippets

Marine ecosystems, PACT, and financing conservation

The importance of healthy coastal and marine ecosystems is paramount to Belize's economic wellbeing. These ecosystems provide a variety of goods and services to humans [26], [7]. Near shore corals act as natural buffers preventing coastal erosion and mitigating the effects of storm surges by absorbing wave energy, potentially saving Belize millions of dollars annually in avoided damages to manmade coastal infrastructure [17], [40]. Fish stocks provide coastal communities with food security,

Tourist WTP study

There are several approaches to choose from when attempting to determine an individual's willingness to pay for environmental changes and/or changes to public policy.3 The specific method chosen depends on several considerations including, but not limited to – what is being valued, intended policy use, ease of implementation, cost of survey, and cognitive burden [40]. Commonly, a willingness to pay (WTP) survey is used to evaluate

Discussion and conclusion

The primary objective of this paper was to determine if Belize tourists were willing to pay a higher exit fee to help fund conservation, considering that the former $3.75 fee charged by the Protected Areas Conservation Trust has been inadequate to sustainably finance the conservation of Belize's marine ecosystems. For those tourists willing to pay a higher fee, the secondary objective was to determine the maximum fee they were willing to pay. Results indicate that approximately 80% of tourists

Acknowledgement

Partial funding provided by Washington and Lee University Lenfest Grant, USA.

References (51)

  • A. Himes-Cornell et al.

    Valuing ecosystem services from blue forests: a systematic review of the valuation of salt marshes, sea grass beds and mangrove forests

    Ecosyst. Serv.

    (2018)
  • J.C. Ingram et al.

    Evidence of Payments for Ecosystem Services as a mechanism for supporting biodiversity conservation and rural livelihoods

    Ecosyst. Serv.

    (2014)
  • Sierra Ison et al.

    Sustainable financing of a national marine protected area network in Fiji

    Ocean Coast. Manag.

    (2018)
  • Priscila F.M. Lopes et al.

    Paying the price to solve fisheries conflicts in Brazil's marine protected areas

    Mar. Policy

    (2018)
  • Sean Pascoe et al.

    Estimating the potential impact of entry fees for marine parks on dive tourism in South East Asia

    Mar. Policy

    (2014)
  • Michaela Roberts et al.

    User fees across ecosystem boundaries: are SCUBA divers willing to pay for terrestrial biodiversity conservation?

    J. Environ. Manag.

    (2017)
  • S. Salas et al.

    Challenges in the assessment and management of small-scale fisheries in Latin America and the Caribbean

    Fish. Res.

    (2007)
  • P.F. Sale

    Management of coral reefs: where we have gone wrong and what we can do about it

    Mar. Pollut. Bull.

    (2008)
  • P. Schuhmann et al.

    Recreational SCUBA divers' willingness to pay for marine biodiversity in Barbados

    J. Environ. Manag.

    (2013)
  • P.W. Schuhmann et al.

    Visitor preferences and willingness to pay for coastal attributes in Barbados

    Ocean Coast. Manag.

    (2016)
  • Rodelio F. Subade et al.

    Do non-users value coral reefs?: economic valuation of conserving Tubbataha reefs, Philippines

    Ecol. Econ.

    (2014)
  • J.C. Trujillo et al.

    Coral reefs under threat in a Caribbean marine protected area: assessing divers' willingness to pay toward conservation

    Mar. Policy

    (2016)
  • Steven M. Thur

    User fees as sustainable financing mechanisms for marine protected areas: an application to the Bonaire National Marine Park

    Mar. Policy

    (2010)
  • Gabriel M.S. Vianna et al.

    Shark-diving tourism as a financing mechanism for shark conservation strategies in Malaysia

    Mar. Policy

    (2018)
  • K. Arrow et al.

    Report of the NOAA Panel on Contingent Valuation

    (1993)
  • Cited by (13)

    • Ticket prices and revenue levels of tourist attractions in China: Spatial differentiation between prefectural units

      2021, Tourism Management
      Citation Excerpt :

      The United States and Canada have a long tradition of charging visitors for the use of their national parks and other protected areas (Mackintosh, 1983; Sharpley & Sharpley, 1997), a practice followed in most other countries. Apart from admission fees, there are various ways of raising funds to maintain tourist attractions, such as tourism development taxes, environmental taxes, protection fees, nature conservation funds, and tourism facility improvement funds (Maria, Song, & Jerome, 2008; Edwards, 2009; Byun & Jang, 2015; Lopesa & Villasante, 2018; Caseya & Schuhmann, 2019). However, charging admission fees, generally collected in exchange for a ticket, is a relatively common practice.

    • Estimating visitors' willingness to pay for a conservation fund: sustainable financing approach in protected areas in Ethiopia

      2020, Heliyon
      Citation Excerpt :

      The result confirms that visitation is income elastic and the demand for ecotourism is highly affected by the propensity of household income and the nation's wealth. As noted by Thur (2010) and Casey and Schuhmann (2019), the demand for biodiversity conservation raises with increasing nation's wealth to allocate more budgets for the conservation of PAs. The finding unfolds that the more concerned visitors would be more willing to pay than the less concerned visitors.

    View all citing articles on Scopus
    View full text