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Conservation strategies in coastal wetland: compromise based on habitat conflicts between mangroves and the fiddler crab, Uca formosensis in Taiwan Hwey-Lian Hsieh, Po-Fen Lin*, Chang-Po Chen Institute of Zoology, Academia Sinica, Taipei, Taiwan Research Center for Biodiversity, Academia Sinica, Taipei, Taiwan
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Outline 1.Taiwanese fiddler crab, Uca formosensis. 2.Why mangrove is important to Taiwan coastal zone? 3.The habitat characteristics of mangroves and Uca formosensis. 4.How mangroves could change the habitat of Uca formosensis? 5.Conservation Strategies
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Introduction The fiddler crab Uca formosensis is endemic to Taiwan Uca formosensis Other Uca species
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The habitats of Uca formosensis : Non-vegetated, high tidal zones in firm mud intertidal flats
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Life history stage Zoea and Megalop stage Spread/distribution Juvenile Feeding/ growth Adult Burrowing/ breeding Competition between fauna Aspect of organism Micro- habitat Temperature, humidity, sediment salinity, oxygen content, water content, quantity and quality of food, toxic materials, etc. Coastal environments erosion/siltation emerging/sinking Macro- habitat support Aspect of habitat Sediment particle size topography elevation mangrove benthic microalgae Vegetation Water influence estuary tide flow tidal level Water column influence Benthic environment
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120°E 121°E 122°E 25°N 24°N 23°N Distributional records of Uca formosensis (from 1918 to 1997) Black stars represent areas with active population of U. formosensis Open stars represent areas where the population of U. formosensis has extinguished. (Shih,1999)
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Threats to fiddler crabs: Land reclamation, dike and road construction
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Another threat to fiddler crabs: Improper planting of mangroves on the Uca formosensis habitats
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Goals of this study: To examine the habitat characteristics of both U. formosensis and mangroves To provide a scientific basis for conserving the diversity of intertidal habitats and populations of U. formosensis To propose conservation strategies for the protection of intertidal habitats in coastal wetlands of Taiwan
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Material and Methods
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Hsinchu City Taipei City Changhua County Kuantu (KT) Tachuang mangrove (TCS) Haishanku Mangrove (HS) Tatu (TT) Jenchang Lake (JCL) Tachuang Creek North Shore (TCN) Haishanku-1 (HSI) Haishanku-2 (HSII) Haishanku-3 (HSIII)
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Sedimentary substrates of microhabitats Grain size (Silt/Clay content) Total organic carbon and nitrogen content Water content pH Salinity of interstitial water Depth of the oxidation layer Benthic macroinvertebrates Depth of the oxidation layer
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Results and Discussion ○ The habitat of Uca formosensis ( △ mean±S.E.) ● The habitat of mangroves( ▲ mean±S.E.) TT JCL TCNHSIHSIIHSIIIHSTCSKT TT JCL TCNHSIHSIIHSIIIHSTCSKT
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○ The habitat of Uca formosensis ( △ mean±S.E.) ● The habitat of mangroves( ▲ mean±S.E.) TT JCL TCNHSIHSIIHSIIIHSTCSKTTT JCL TCNHSIHSIIHSIIIHSTCSKT
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TT JCL TCNHSIHSIIHSIIIHSTCSKT TT JCL TCNHSIHSIIHSIIIHSTCSKT ○ The habitat of Uca formosensis (mean±S.E.) (including polychaetes, insects and crabs ) ● The habitat of mangroves (mean±S.E.) (including polychaetes, insects, crabs and oilgocheates)
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Potential negative impacts on U. formosensis caused by mangrove intrusion A. Alternation of sediment characteristics Siltation increases Depth of oxidation layer decreases pH decreases
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B. Direct effects by mangrove trees Shading effects (Hsieh,1999; Hsieh et al.,2002; Wainright et al., 2000) Productivity of benthic microalgae declines Aboveground structures Stems and branches block crabs’ view and movement Leaves shaken by wind may scare crabs Underground structures Roots become obstacles to crabs’ burrowing
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C. Benthos changes (Shih,1999; Hsieh et al.,2002) Helice formosensis, H. wuana, U. arcuata prefer mangrove habitats Helice formosensisU. arcuata
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Accelerate studies on the habitat characteristics of each stage of the life history of U. formosensis Apply ecological engineering practices to restore habitats of U. formosensis Monitor the impacts of mangroves on estuarine ecosystems and manage mangroves accordingly Conservation Strategies
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Conserve coastal wetlands which 1) retain those still sound function, 2) improve those that have been disturbed, and 3) restore those that have been destroyed. We try to connect these three types of habitats to form a “Coastal Wetlands Conservation Greenway along Taiwan’s Western Coastal Zone” (Hsieh et al., in press) Promote the wise use of coastal wetlands
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Mangrove trees Uca formosensis reserve Buffer zones Mangroves should be eliminated from U. formosensis reserve areas. For examples: remove mangroves from Uca formosensis reserve and buffer zones
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Carry out public education on biodiversity and habitat diversity. When U. formosensis encounters mangroves
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Summary The invasion of mangroves into U. formosensis habitats has a negative impact on the fiddler crab’s population. Mangroves on estuarine ecosystems and coastal zones should be managed properly in Taiwan. Future coastal management should emphasize on maintaining biodiversity and habitat diversity.
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Acknowledgements Funding agencies Institute of Zoology Academic Sinica Research Center for Biodiversity Academia Sinica Hsinchu City Government Assistants and Graduate students Yuan-Hsien Chen, Hsin-Yi Yeh, Hsiao-Hui Yang, Tai-An Chen, Song-Lin Wu, Wu-Hsiung Ou, Shu-Ting Lin, Feng-Lin Wang, Chang-Hao Hoa, Ming-Che Yang, Meng-Jeng Guo.
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Thanks!
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