Reflecting Deer Restoration in Kenting National Park, Taiwan
The Effects of the Re-introduced Sika Deer toward Ecosystems and Rural Communities

Review of Formosan Sika Deer Status
Formosan Sika Deer (Cervus nippon taiouanus) is a Taiwanese endemic subspecies, and the only extinct deer in the Taiwan wilderness. They were once widespread over the island of Taiwan, and had a huge population living in the plains and hills of the low and middle altitude about 300-400 years ago. However, deer have an important economic value and have been traditionally utilized in many ways. So, in the early history of Taiwan, the migrant and indigenous people hunted deer for their food and by-products. In this century, as many as 50,000 Sika Deer skins a year went to Japan, and the deer pelt exports peaked at 100,000 one year (Kuo 1994). In addition, the native habitat was destroyed by expanding agriculture and development. Those factors of severe exploitation and habitat degradation led to the deer's extinction in the wild. McCullough (1973) pointed out Formosan Sika Deer would be extinct by 1969, and the only deer left were in captivity.


The Origin of the Sika Deer Re-introduction Project
In the 1980's, the Taiwan government and the public generally started to reflect on their conservation policy. For many decades, the government and people thought that industrial and economic development have a supreme priority, and ignored proper environmental protection. When the land was heavily industrialized and densely populated, a civic movement of conservation gradually developed. The will and demand of civic society also influenced government. The government finally passed its environmental policy plans for sustainable development including ecological perspectives. Since 1987, there has been a re-introduction project of Sika deer conducted by Kenting National Park. The government tried to restore the Sika Deer population here first, because it is the only lowland National Park in Taiwan, and is also a historic site of Sika deer distribution.

My question is:

What are the effects of re-introduced Sika Deer in the ecosystems and the rural communities?


We will deal with two primary factors:
1. One is natural component: to use Geographic Information System (GIS) skills to analyze and simulate the deer browsing impacts upon vegetation and avian-biodiversity in the ecosystem; 2. the other one is social component: to conduct qualitative, in-depth interviews to explore how the local communities interact with the deer impact and the re-introduction project of Kenting National Park.

Natural Science Component
Successful re-introduction project is judged by profitability over time, and we should ensure that re-introduction practices are ecologically desirable in an ecosystem perspective . After releasing 10 deer first into the wild in 1995, the National Park merely had a basic monitor project to trace the survival and population dynamics of few radio-collared deer. There is still not any research about the ecological impact on the whole ecosystem scale . In this re-introduced stage, it is very important to examine the up-to-date outcome continuedly, and to establish any ecological adjustment if need. Recently due to a high-density population in the earliest release Area 1, the deer grazing impact was intensive . The browsing effect gradually included soil erosion, degradation of vegetation succession, changing the forestry composition and abundance, changing the avian bio-diversity and other factors. Besides, in the low-density deer area where we released deer into the wild, the population has increased rapidly to 20-30 individuals since 1995. All the detailed impact is unknown and needs to research.

Method: To understand the status of the re-introduced deer in population and ecological levels, I will focus on a spatially ecological research of the deer population, and a landscape simulation for the whole ecosystem management responses to various forms of deer impacts. I intend to collect data on the spatial selection of food and habitat by Formosan Sika Deer in the wild. In order to understand their distribution model and resource partition, I will concentrate on the ecological patterns of browsing effects by building the fundamental background of the GIS database. Based on the above information, this research will evaluate further management strategies after the release of the deer. I will use the GIS spatial explicit model to generate the deer-impact simulation in the vicinty of the park, and suggest the practical management practices for biodiversity conservation and ecosystem management.

Social Science Component
According to Earle (1997), ecosystem management integrates knowledge of ecological relationships within a socio-political value framework. But in the beginning, the whole re-introduced project was mostly centered on a self-sustainable deer population in single-species perspective. The project ignored the socio-economically acceptablity and the social changes in rural communities. In the preliminary interviews(1996), most residents refused to support the deer re-introduction because they were dissatisfied with the practices and controls of the National Park. The human-park or human-deer conflicts also resulted from the low degree of public-invlovement in the decision-making process, and the residents didn't realize the benefits from the re-introduction project. Continuously monitoring the restoration program in a human dimension allows all of the stakeholders to keep learning, build their own experiences, and adjust our strategies to achieve the goals of the re-introduced project and ecosystem management as efficiently as possible.

Economic Value? Evaluate Ecosystem and Biodiversity?


Method: Management effectiveness should be concerned with resident attitudes and reactions, either in their outward behavior or in their perception. I will conduct a qualitative survey for community's self-evaluation mainly in the local opinion-leadership scale and traditional county institutional levels. Study factors will be various types of recreational, environmental, economic benefits and problems, which the re-introduction project either directly provided or caused (Kellert 1984). The research will provide a better understanding of the human-deer interaction in the rural communities near Kenting National Park, especially the socio-economic impact and the new trend of eco-tourism. This attitudinal survey can effectively offer guidance for further management adjustment, as well as provide baseline data to assess management policies (Byers 1996). While working with the local people and economic-politic organizations who face the ecosystem management issue, my data will also improve the re-introduction project, and enhance the participation of local people as stewards. The goal of this research is looking forward to the total ecosystem management or the holistic resource management with a view toward broad human dimensions.


Literature Cited

Abel, N. and P. Blaikie. 1986. Elphants, people, parks and development: the case of the Luangwa Valley, Zambia. Environmental Management 10(6):735-751.

Byers, B. A. 1996. Understanding and influencing behaviors in conservation and natural resources management. African Biodiversity Series, No. 4. Biodiversity Support Program in USAID. Washington, D.C. 43-61Pp.

Earle, J. L. 1997. Across-cultural study of individual attitudes toward natural resources and natural resources development, San Luis Valley, Colorado. Ph.D. thesis. University of Colorado.

Kellert, S. R. 1984. Assessing wildlife and environmental values in cost-benefit analysis. Journal of Environmental Management 18(4):355-363.

Kuo, Guol-way. 1994. The study of field behavior and habitat use of Formosan Sika Deer (Cervus nippon taiouanus). M.S. thesis. National Taiwan Normal University, Taipei, Taiwan.

McCullough, D. R. 1974. Status of larger mammals in Taiwan. Tourism Bureau, Taipei, Taiwan, R. O. C. 35Pp.

Asian Ungulates Conservation

Nutritional Condition of Sika Deer in Kenting