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| 墾丁國家公園環境資源管理暨夥伴關係發展計畫-社頂部落 |
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一、計畫緣起
墾丁國家公園管理處於民國94年開始，對社頂部落投入為期三年的社區生態旅遊輔導計畫，居民於95年6月開始進行夜間巡守工作，同年7月開始加入生物監測，累積三年的巡守監測經驗後，墾丁國家公園管理處於98年短期試辦社頂居民參與生物監測，99年藉由委託本計畫，正式將社頂地區生物監測工作交由部落居民執行。
二、研究方法與過程
初步選取社頂地區具特色或對生態旅遊有效益之條背螢、台灣梅花鹿、台灣獼猴、黃裳鳳蝶、大冠鷲等共5種，監測人員選定以具有墾丁國家公園保育志工資格的社頂部落解說員擔任，並邀請各物種專家前來教導監測工作，同時訂定監測的地點、時間、頻度等，讓每位監測人員皆能具備監測基礎之技能，除了前述5種主要監測物種，也列入其他特色生物做為次要物種監測，以求獲得更多生物資料。
三、重要發現
監測結果顯示，條背螢出現時間為6月至10月中，8月份高峰，雄蟲隻次比雌蟲多；台灣梅花鹿兩條路線目擊的隻次相近，籠仔埔略多於工作站路線；台灣獼猴出現高峰在6月和8月，下午目擊隻次明顯高於上午；黃裳鳳蝶監測則以紅紋鳳蝶隻次最多，其次是黃裳鳳蝶，大紅紋鳳蝶最少；大冠鷲以5月和9月目擊隻次最多，且上午目擊隻次明顯高於下午。
監測開始遇到的問題是對新的監測方式不熟悉，經由輔導團隊多次指導，監測人員逐漸得心應手，而自從加入次要物種監測後，每位監測人員能辨識的生物明顯增加，對帶領生態旅遊遊程的監測人員而言，監測的經驗提供許多生態習性上的解說，讓監測人員更有自信，使社頂部落生態旅遊解說內容更趨完整。
四、主要建議事項
經由一年的監測發現，尚有許多地方需要努力，部分缺失也漸漸改善，對於之後監測之建議如下：
1. 未來可視需要新增監測物種，讓社頂部落有更多的物種進行監測保育。
2. 可增加監測頻度，減少誤差值。
3. 增加同物種不同的監測路線，讓監測人員更瞭解物種分布及移動的範圍。
4. 訓練新的監測人員，讓監測人員有變故時可以替補，避免監測資料的缺失。
5. 定期舉辦各監測物種培訓，不斷提升監測人員的監測能力。
計畫類別：[規劃]
英文摘要：1. Introduction
Kenting National Park Administration conducted a three-year community-based ecotourism project in 2005 with the Sheding community. In June 2006 residents in Sheding began to patrol at night. Then they began to join biological monitoring in July. Based on the accumulated experience of three years of patrol, Kenting National Park conducted a prior test to employ the community members to participate in the biological monitoring in 2009. In 2010 the work of monitoring are submited to community residents officially.
2. Research Method
The project selected five important species to monitor, including Luciola substriata, Cervus nippon taiouanus, Macaca cyclopis, Troides aeacus kaguya, Spilornis cheela. The project also employed Kenting National Park Conservation Volunteers to participate the work of monitoring. They had been trained by experts. The monitoring items are location, time, frequency, etc. Except the five species to monitor, the project also chooses secondary species to obtain more biological information.
3. Findings
Results show that, for Luciola substriata, they often appear in June to mid-October. The number achieves highest peak at August. Number of males are more than females; For Cervus nippon taiouanus, the number observed in two different routes are similar. For Macaca cyclopis, The number at the peak point of observation is in June and August. The number observed in the afternoon is higher then those in the morning; For Troides aeacus kaguya, Zeyi Pachliopta aristolochiae interposita is the largest number that cab observed, then is Troides aeacus kaguya, Byasa polyeuctes termessus is the species that has minimum number to observe; For Spilornis cheela, they appear at May to September. They also more easy to witness in the afternoon than in the morning.
The members of monitoring face the problem of not familiar with monitoring methods. However, through training, the members can identify species more professionally. And the data can be used to develop the ecotourism for their community.
4. Suggestions
A. It is need to add monitoring of species to obtain more information of the environment.
B. Monitoring frequency can be increased to reduce the error.
C. Increase monitoring routes to understand of the same species lines, so that monitoring personnel to better understand their moving patterns.
D. Training new monitor members to avoid the lack of monitoring personnel.
E. More training courses are needed to achieve better monitoring quality.
計畫屬性：本處委託辦理
執行年度：99
計畫主持人：陳美惠
中文關鍵字：墾丁國家公園、社頂、生物監測、社區參與監測
英文關鍵字：Kenting National Park, Sheding community, Biological monitoring, Community based monitoring