International Journal of Ecosystem

p-ISSN: 2165-8889    e-ISSN: 2165-8919

2014;  4(4): 190-196

doi:10.5923/j.ije.20140404.05

Sustainable Tourism Based on Carrying Capacity and Ecological Footprint at Sapeken Archipelago, Indonesia

Agus Romadhon1, Fredinan Yulianda2, Dietriech Bengen2, Luky Adrianto2

1Department of Marine and Science, Trunojoyo University, Kampus Unijoyo, Telang, PO. BOX 2 Kamal Bangkalan

2Faculty of Marine Science and Fisheries, Bogor Agricultural University

Correspondence to: Agus Romadhon, Department of Marine and Science, Trunojoyo University, Kampus Unijoyo, Telang, PO. BOX 2 Kamal Bangkalan.

Email:

Copyright © 2014 Scientific & Academic Publishing. All Rights Reserved.

Abstract

As sustainability has become an important policy issue in small island tourism, there is need to understand the natural limits. These used to know how much small island with their limitation could accommodate tourism needs. Based on that fact, this research aimed to: 1) quantify the environmental carrying capacity for several type of ecotourism in Sapeken archipelago; 2) assessing Sapeken archipelago ability to accommodate ecotourism activities using ecological footprint based from emergy approach; and 3) evaluate sustainability ecotourism activities in Sapeken archipelago. Result showed: 1) Sapeken archipelago have different carrying capacity for each type of ecotourism. For dive tourism 5,330 persons/day, snorkelling 3,590 persons/day, fishing tourism 14,900 persons/day, mangrove tourism 32,100 persons/day and beach tourism 1,990 persons/day; 2) The largest accommodate for tourism are Paliat island (844,000 persons/year) Sepanjang island (217,000 persons/year) and smallest in Sapeken island (50.5 persons/year); and 3) Ecotourism activities in Sapeken archipelago has sustainability (RCC > EF) which indicated by carrying capacity as natural limit is greater than EF as a representation number of tourist can be met.

Keywords: Sapeken archipelago, Carrying capacity, Ecological footprint, Sustainability, Ecotourism

Cite this paper: Agus Romadhon, Fredinan Yulianda, Dietriech Bengen, Luky Adrianto, Sustainable Tourism Based on Carrying Capacity and Ecological Footprint at Sapeken Archipelago, Indonesia, International Journal of Ecosystem, Vol. 4 No. 4, 2014, pp. 190-196. doi: 10.5923/j.ije.20140404.05.

1. Introduction

Sapeken Archipelago is an area consisting of a number of small islands with a several supporting ecosystems such as coral reefs, mangrove ecosystems, coastal ecosystems and fisheries resources [1], indicated as a region with high diversity and susceptible to utilization activities as well [2]. In this regard, the utilization of Sapeken archipelago is in accordance with their limitation as small islands. One of the utilization of small islands is ecotourism activities.
Ecotourism is defined as trip activity to places that are relatively not interfere the places, with the purpose of observing and enjoying biological resources, by minimizing environmental impact so as to encourage respect for the local culture and produce benefits that are fair to all users [3]. Moreover, The International Union for Conservation of Nature (IUCN) said that an ecotourism activity is not only nature-based, but also as an effort to maintain biodiversity while improving the welfare of the local community. However, without adequate planning, the purpose of the ecological balance, social, and economic in ecotourism will not materialize and instead the implementation will be causing damage to the environment [4]; [5]; [6].
Based on reason above, the planning of ecotourism activities at Sapeken Archipelago requires an assessment of the ability of their ecosystems to provide all aspects required to implement sustainable tourism activities. The assessment approaches used are in the form of: 1) an assessment of the regional carrying capacity (RCC), 2) an assessment of touristic ecological footprint (TEF), and 3) an assessment of the sustainability of ecotourism activities.

2. Methodology

This research was conducted at Sapeken Archipelago that formed from a series of small islands chain totalling 201.887 Km2 areas. The islands chain are located at 6° 46 '- 70° 6' LS 115° and 115° 10'-44 'E, part of the District of Sapeken, Sumenep regency, East Java Province (Figure 1). Primary and secondary data were collected from the study sites as well as from various agencies in Sumenep Government and other relevant agencies.
Figure 1. Map of study area at Sapeken Archipelago
The method in this research as a new quantitative approach with combine ecological footprint and emergy approach. Ecological footprint analysis measures agregat land area required for a given population to exist in sustainable manner. [7]; [8]. Furthermore, emergy is a unit of resource use and work potential, is used to quantitatively evaluate intensity of development [9]; [10]. Based on ecological footprint and emergy approch, used for determine carrying capacity for ecotourism in Sapeken archipelago.

2.1. Utilization Carrying Capacity (UCC)

UCC was used to determine the maximum number of visitors that physically can be accommodated in the specific space and time without causing interference with the natural and human. UCC and RCC were calculated with following equation [11]:
(1)
where :
(2)

2.2. The Ability of Sapeken Archipelago Ecotourism Activities

The ability of Sapeken Archipelago ecotourism activities was assessed using ecological footprint (EF) based on the concept of emergy synthesis consists of three stages, i.e : 1) calculate or assess their biocapacity, covering energy capacity and resources capacity, 2) calculate or assess community ecological footprint, and 3) calculate or assess touristic ecological footprint.
Biocapacity of Sapeken Archipelago
Emergy is one form of energy that has undergone a transformation in the form of energy flow [12]; [13]. Energy biocapacity was calculated following. [14]. include solar energy, wind, rain energy, wave energy, and tidal waves. Meanwhile, the resources capacity includes food energy, energy forest and fishery energy [15].
The unit used of energy is solar em joules (seJ). The conversion of energy and / or mass to emergy, calculated using emergy intensity factors (eif)
(3)
where
(4)
where
Community Ecological footprint of Sapeken Archipelago
The calculation refers to the ecological footprint assessment and analysis conducted by Scotti et. al [16]. Equations used are as follows:
(5)
where
Touristic Ecological Footprint
EF of ecotourism plan products is the total accumulated value of the seven components of the previously mentioned [17]. The total value was shown by the following equation:
(6)
where:

2.3. Sustainability of Ecotourism Activity

Sustainability assessment for the utilization of Sapeken Archipelago for ecotourism activities performed by comparing the RRC with the EF with following equations:
(7)

3. Results and Discussion

3.1. UCC of Sapeken Archipelago for Ecotourism Activities

UCC is the maximum number of visitors that limited by the condition of the ecosystem as a natural limit. Ecosystem natural limit for ecotourism based on the results of conformity assessment activities for various types of ecotourism. Table 1 showed the results of UCC assessment of Sapeken Archipelago for ecotourism activities.
Table 1. UCC (person / day) for ecotourism activities in the Sapeken Archipelago
     
UCC of ecotourism activities in the Sapeken Archipelago were depended on the size, condition, and suitability status of the ecosystem for ecotourism. The largest UCC on each type of tourist was mangrove tours (32.100 people); following by fishing (14.900 people); diving (5.330 people); snorkelling (3.590 people), and beaching (1.990 people). Furthermore, those values were the maximum limit of users (tourists) that can be accommodated on the Sapeken Archipelago in order to provide continuous comfort (leisure) without affecting or causing loss of quality of the resources.
There is a need to manage ecotourism system and ecosystem service. It is needed to utilize the small island ecosystems. Ecotourism as a form of utilization should be based on the existing limitations of small island. [18]. The form of management could be adjustments of ecotourism activities to the carrying capacity of small island region by regulating the number of tourists. The control of the number of tourists is intended to regulate the very limited resources and space consumption in the small island in order to give comfort or satisfaction for tourists. This arrangement also minimizes impact of ecotourism activities on the quality of the resource as well as ensuring the ecosystem service in the small islands.
Ecosystem service is the benefits of the existence of an ecosystem to human life [19], which include provisioning service, supporting service, regulating service, and cultural service. Ecosystem service is highly dependent on the condition of the ecosystem. Well-maintained ecosystems will ensure the sustainability of ecosystem services [20]. Referring to that description, the carrying capacity of the Sapeken Archipelago for ecotourism activities represented by the number of tourists per day for diving, snorkelling. fishing, mangrove tour, and beaching, showed that there are limitations in the ability of ecosystems to provide ecosystem services for tourist leisure. The number of tourists who exceed the carrying capacity of the Sapeken archipelago will affect the ability of ecosystems to provide ecosystem services and raise negative impact on the sustainability of ecotourism activities. Furthermore, [21] describes the number of tourists as a form of management to limit the impact of ecotourism activities, ensuring quality of the visitor experience and planning of supporting facilities for ecotourism activities.

3.2. Regional Capacity of Sapeken Archipelago for Ecotourism

Regional capacity of Sapeken archipelago is the quantity of regenerative capacity of the biosphere that is used by tourist activity, carried out by counting the amount of biologically productive land and catchment area required to support a given population at current levels through the consumption and resource efficiency. These assessments includes: 1) biocapacity, consisting of energy and resource biocapacity as supply and 2) ecological footprint, consists of community and touristic ecological footprint as demand. The results of an assessment of the regional capacity of Sapeken Archipelago for ecotourism were showed in Table 2;3; 4; 5 and 6.
Table 2. Energy biocapacity of Sapeken Archipelago
     
Table 3. Resources biocapacity of Sapeken Archipelago
     
Table 4. Community ecological footprint of Sapeken Archipelago
     
Table 5. Touristic ecological footprint of Sapeken Archipelago (gha/capita)
Table 6. Comparison of total biocapacity and total ecological footprint
     
Total comparative value of total biocapacity with the total ecological footprint in Table 6 was the assumption of ability of each small island in the Sapeken Archipelago to accommodate and meet the needs of tourists. The largest number of tourists that can be accommodated was found in Paliat Island (844,000 persons/year) and Sepanjang Island (217,000 persons/year), while the smallest value was found in the Sapeken Island (50.5 persons/year).
The number of visitors or tourists that can be accommodated as a representation of a small island carrying capacity for tourism activities is strongly influenced by existing conditions, such as area, human population, and resource conditions [22]. This condition is an indicator for possibility of utilizing natural capital asset possessed by Sapeken Archipelago. Planning of ecotourism activities is different for island group (archipelagos) and island (single island). In small island group, the development of ecotourism activities should be able to collaborate on cultural and interests differences as well as different levels of development in each small island [23]. Thus, the planning of ecotourism activities in the Sapeken Archipelago should be based on the ability of each small island to meet a number of parameters as a determinant of the suitability of a particular type of tourism that will be developed and their carrying capacity as a marker of ecological limits as well.

3.3. Sustainability of Ecotourism Activities in Sapeken Archipelago

Based on the understanding of ecotourism as social-economic-environmental complex system. an assessment of the sustainability of ecotourism activities in the Sapeken Archipelago were based on the value of RCC that represented the ecological/environmental carrying capacity as the loading capacity and the aggregate value of the ecological footprint (EF) that characterized the socio-economic carrying capacity as a supporting capacity. RCC value and EF aggregate value were compared to obtain the sustainability status of ecotourism activities in the Sapeken Archipelago. Furthermore. [24] described the carrying capacity and the ecological footprint was measured in the same units that can be compared directly. If the value of the ecological footprint (EF) is less than the carrying capacity value. ecotourism activities will be sustainable and vice versa. The results of the comparative value of the RCC and EF at Sapeken Archipelago were showed in Table 7.
Table 7. Comparison of regional carrying capacity (persons/year) and ecological footprint (persons/year) at Sapeken Archipelago
     
The results of the sustainability assessment of ecotourism activities in the Sapeken Archipelago showed that RCC value is greater than the value of EF. This result implies that ecotourism activities that will be carried out in this island group will not decrease the quality of the ecosystems, but providing benefits to the local community, and able to provide a level of comfort (leisure) to tourists.
Small island tourism is tourism activities undertaken by considering the constraints of a small island. For it sustainability, development in small island tourism activities should be able to bring together all the existing needs. Furthermore, synchronization between the utilization activities and quality of the environment is an important condition to be created in order to ensure the economic. social, and ecological sustainability [25]. Limiting factor of the development of ecotourism activities in the Sapeken Archipelago is maximum loading capacity of existing ecosystems. Utilization that exceeds the maximum loading capacity will decline the quality of ecosystems in providing a number of ecosystem services.
Restriction on the number of tourists is management strategies which most plausible to be done on the existing ecotourism activities in the Sapeken Archipelago. Aside from the limitations as a small island, the management steps taken will reduce the pressure on the ecosystem as tourist destinations such as coral reefs, mangroves, and coastal fish resources. Furthermore, restrictions on the number of visitors will make the services associated with the presence of existing infrastructure in the Sapeken Archipelago will be optimally utilized by visitors. Strategy of limiting the number of visitors or other travellers can be done directly or indirectly by applying seasonal visit limitation, zoning, and charges for visitors, as a form of mitigation against the impact of the presence of tourists [26].

4. Conclusions

Sapeken Archipelago has utilization carrying capacities (UCC) which vary for different types of ecotourism activities. The largest UCC on each type of tourist activities was mangrove tours (32,100 persons/day), following by fishing (14,900 persons/day); diving (5,330 persons/day). snorkelling (3,590 persons/day); and beaching (1,990 persons/day).
Total comparative value of total biocapacity with the total ecological footprint represents the ability of each small island in the Sapeken Archipelago to accommodate and meet the needs of visitors in tourism activities. The largest number of tourists that can be accommodated were found in Paliat Island (844,000 persons/year) following by Sepanjang Island (217,000 persons/year), while the smallest value were found in the Sapeken Island (50.5 persons/year).
Related to the planning of ecotourism activities (ecotourism) in Sapeken archipelago by looking at the of availability status of ecosystem services (budgets), it is possible to be developed. Conditions of some natural capital assets that is still able to provide a number of ecosystem services that can be used as a tourism attraction.
Lastly, assessment of carrying capacity for ecotourism based on ecological footprint should be integrated in the planning of tourism activities. in order to provide existing condition in-depth overview related to small island ability for tourism as sustainable development.

ACKNOWLEDGEMENTS

We gratefully acknowledge the anonymous reviewers.

References

[1]  FDC – INNR. 2006. Science Report Zooxanthellae VIII Expedition. Conditions and Reef Ecosystem Potential at Kecamatan Sapeken. Kabupaten Sumenep. East Java Provience. Agustus 2006.
[2]  Romadhon, A., Yulianda, F., Bengen, D.G., Adrianto, L, 2013, Socio Ecological System (SES) Assessment for Tourism at Sapeken Archipelago. Sumenep. Indonesia., International Journal of Ecosystem. 3(5), 106-114.
[3]  Lydia, T., Cabanban, A.S., 2007, Planning for sustainable tourism in southern Pulau Banggi: An assessment of biophysical conditions and their implications for future tourism development., Journal Environmental Management (85), 999-1008.
[4]  Chandralal, K., Palliyaguruge, L., 2010, Impacts of Tourism and Community Attitude towards Tourism: A Case Study in Sri Lanka. South Asian Journal of Tourism and Heritage. Vol. 3, No. 2.
[5]  Robertico, R.C., 2004, A paradigm shift to a new strategy for small island economies: Embracing demand side economics for value enhancement and long term economic stability. Journal Tourism Management (14), 120-128.
[6]  Bengen, D.G., Retraubun, A.W.S, 2006, Reveals the Reality and Management Urgency Based on Small Islands Eco-Socio System. Learning Center and Development of Coastal and Marine. ISBN 979-98867-2-4.
[7]  Wackernagel, M., Rees. W., 1996, Our Ecological Footprint: Reducing Human Impact on The Earth. Philadelphia. PA: New Society Publishers. ISBN 0-86571-312-X.
[8]  Rees, W., 1992, Ecological footprints and appropriated carrying capacity: what urban economics leaves out. Journal Environment and Urbanization (4), 121–130.
[9]  Brown, M., Ulgiati, S., 2001, Emergy measures of carrying capacity to evaluate economic investments. Journal Population Environment (22), 471–501.
[10]  Castellani, V., Sala. S., 2012, Ecological Footprint and Life Cycle Assessment in the sustainability assessment of tourism activities., Journal Ecological Indicator (16), 135–147.
[11]  Yulianda, F., Fachrudin, A., Hutabarat, A.A., Harteti, S., Kusharjani., Kang, H.S., 2010, Integrated Coastal and Marine Resources Management. Bogor: Pusdiklat Kehutanan-Departemen Kehutanan RI-SECEM-Korea International Cooperation Agency (in Indonesian Language).
[12]  Odum, H.T., 2000, Handbook of Emergy Evaluation. Folio #2. Emergy of Global Processes. Center for Environmental Policy Environmental Engineering Sciences University of Florida. Gainesville.
[13]  Hossaini. N., Hewage. K., 2013, Emergy accounting for regional studies: Case study of Canada and its Provinces., Journal of Environment Management (118), 177–185.
[14]  Jungho. N., Chang. W., Kang, D., 2010, Carrying Capacity of an uninhabited island off the southwestern coast of Korea., Journal Ecological Modelling (21),2102-2107.
[15]  Pereira. L., Ortega. E., 2012, A modified footprint method: The case study of Brazil., Journal Ecological Indicator (20), 113-127.
[16]  Scotti, M., Bondalvi, C., Bodini, A., 2009, Ecological Footprint as a tool for local sustainability: The municipality of Piacenza (Italy) as a case study., Journal Environmental Impact Assesment Review (29), 39 – 50.
[17]  Peng. L, Guihua. Y., 2007, Ecological footprint study on tourism itinerary products in Shangri-La. Yunan Province. China., Journal Acta Ecologica Sinica. 27 (7), 2954-2963.
[18]  Twining-Ward, L., Butler, R.., 2002, Implementing STD on a Small Island: development and use of sustainable tourism development indicators in Samoa., Journal Sustainable Tourism. (10), 363–387.
[19]  Layke, C., Mapendembe, A., Brown, C., Walpole, M., Winn, J., 2012, Indicators from the global and sub-global Millennium Ecosystem Assessments: an analysis and next steps., Journal Ecological Indicator. (17), 77–87.
[20]  Chan, K.M.A., Satterfield, T., Goldstein, J., 2012, Rethinking ecosystem services to better address and navigate cultural values., Journal Ecological Economies (74), 8–18.
[21]  Saarinen, J., 2006, Traditions of Sustainability in Tourism Studies., Journal Annals of Tourism Research (33), 1121–1140.
[22]  Priskin. J., 2001, Assessment of natural resources for nature-based tourism: the case of the Central Coast Region of Western Australia., Journal Tourism Management (22), 637–648.
[23]  Sheehan. L., Ritchie. B., 2005, Destination Stakeholders: Exploring Identity and Salience., Journal Annals of Tourism Research (32), 711–734.
[24]  Zhao. S., Zizhen. L., Wenlong, L., 2005, A modified method of ecological footprint calculation and its application., Journal Ecological Modelling (185), 65–75.
[25]  Cowx. I.G., Arlinghaus, R., Cooke, S.J., 2010, Harmonizing recreational fisheries and conservation objectives for aquatic biodiversity in inland waters. Journal of Fisheries Biology (76), 2194–2215.
[26]  Manning, R.E., 2007, Parks and carrying capacity: Commons without tragedy. Washington. D.C.: Island Press.