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How to Use the Template Biodiversity influences on mangrove forest ecosystem services delivery Clare Duncan1,2, Jurgenne H. Primavera3,4, Heather J. Koldewey3,5, Julian R. Thompson2, Nathalie Pettorelli1 1 Institute of Zoology, ZSL, Regent’s Park, London NW1 4RY UK 2 UCL Department of Geography, Gower Street, London WC1E 6BT UK 3 ZSL Conservation Programmes, Regent’s Park, London NW1 4RY UK 4 ZSL-Philippines, 43-E Burgos Street, Barangay Magdalo, La Paz, 5000 Iloilo City, Philippines 5 Centre for Ecology and Conservation, University of Exeter, Penryn, Cornwall TR10 9EZ UK Current state of play… • Mangroves are in global decline FAO (2005). Richards & Friess (2016). Current state of play… • Loss of climate change mitigation & adaptation (CCMA) ES International Labour. Martine Perret. Current state of play… • Diversity is also declining Polidoro et al. (2010). DISTRIBUTION OF THREATENED SPECIES • Mid- to upper-intertidal; selective cutting Current state of play… • Rehabilitation efforts often species-poor or monoculture Jurgenne H. Primavera. What does this mean for mangrove ES? Does floristic diversity drive climate change mitigation and adaptation ecosystem services (ES) of mangrove forests? Biodiversity & ES • Terrestrial forests: flora richness can increase ecosystem functioning Gamfeldt et al. (2013). • Mechanism = functional differences (complementarity in resource use or facilitation) • Species richness not important? Biodiversity & ES • Terrestrial forests: saturating or mixed relationships Gamfeldt et al. (2013). • Mechanism = functional identity of the most dominant species • Could these mechanisms = ES trade-offs? Complementarity in Mangroves…? • Species-poor systems – complementarity/facilitation may be strong?1 1: Leitão (2016). Complementarity in Mangroves…? • Species-poor systems – complementarity/facilitation may be strong?1 Lang’at et al. (2011). 1: Leitão (2016). Complementarity in Mangroves…? • Species-poor systems – complementarity/facilitation may be strong?1 • Many forests monospecific & still function fine – dominant species? Huxham et al. (2010). 1: Leitão (2016). Complementarity in Mangroves…? • Species-poor systems – complementarity/facilitation may be strong?1 • Many forests monospecific & still function fine – dominant species? • Narrow niche space & water constraints = morphological convergence 1: Leitão (2016). Complementarity in Mangroves…? • Species-poor systems – complementarity/facilitation may be strong?1 • Many forests monospecific & still function fine – dominant species? • Narrow niche space & water constraints = morphological convergence • Species-poor mangroves: genetic diversity - plasticity? 1: Leitão (2016). Complementarity in Mangroves…? • Species-poor systems – complementarity/facilitation may be strong?1 • Many forests monospecific & still function fine – dominant species? • Narrow niche space & water constraints = morphological convergence • Species-poor mangroves: genetic diversity - plasticity? • Hyperdiverse mangroves: functional traits vary between and within zones2 1: Leitão (2016).; 2: Balun (2011). CCMA ES in Diverse Mangroves… • Does species richness matter for C stocks & storm surge attenuation? • Does complementarity or dominant functional identity drive these? • Are there mechanism- or functional trait-based trade-offs between delivery of different mangrove CCMA ES? Methodology - Which Traits? RESOURCE USE STRATEGY Specific leaf Wood density Maximum height area (SLA) Aerial roots Growth form Methodology - Which Traits? RESOURCE USE STRATEGY Specific leaf Wood density Maximum height area (SLA) Aerial roots Growth form STRUCTURAL Methodology – Study Sites 7 species Methodology – Study Sites 7.8 ha 9 species 7.7 ha 19 species 75.5 ha 9 species 27.5 ha 6 species 3.2 ha 7 species Methodology – Study Sites 7.8 ha 9 species 7.7 ha 19 species 75.5 ha 27 species 72 ha 9 species 27.5 ha 6 species 3.2 ha Methodology – Field + Lab • Temporary field plots – N = 79 • C stock & veg structure1-3 • Storm surge attenuation = Le4 at 2.7 m • Species-specific wood density, SLA, max height, growth form, aerial roots5-7 • SR & functional trait indices8,9 • Control for site & zonation • Model averaging – relative variable importance 1: Kauffman & Donato (2010); 2: Komiyama et al. (2005); 3: Fu & Wu (2011); 4: Mazda et al. (1997); 5: Kattge et al. (2011); 6: Zanne et al. (2009); 7: Primavera et al. (2004); 8: Laliberté & Legendre (2010); 9: Conti & Díaz (2013). Results • DOMINANCE of taller species = increased carbon stock VEGETATION C SEDIMENT C Wi = 1.00 Wi = 0.83 R2 M = 0.21 R2 M = 0.07 R2 C = 0.45 R2 C = 0.56 Results • DIVERSITY of height & all traits = increased storm surge attenuation potential Wi = 0.51 Wi = 0.49 R2 M = 0.30 R2 M = 0.25 R2 C = 0.49 R2 C = 0.41 Results • DIVERSITY of height & all traits = increased storm surge attenuation potential Wi = 0.51 Wi = 0.49 R2 M = 0.30 R2 M = 0.25 R2 C = 0.49 R2 C = 0.41 Results • No correlation between storm surge attenuation potential & C stocks • Real trade-off in mechanisms driving CCMA ES? Summary IMPLICATIONS: • No evidence species richness is important for mangrove CCMA ES Summary IMPLICATIONS: • No evidence species richness is important for mangrove CCMA ES • Functional diversity in structural traits may be key for coastal protection Summary IMPLICATIONS: • No evidence species richness is important for mangrove CCMA ES • Functional diversity in structural traits may be key for coastal protection • Monoculture may be sufficient for high C stocks? Summary IMPLICATIONS: • No evidence species richness is important for mangrove CCMA ES • Functional diversity in structural traits may be key for coastal protection • Monoculture may be sufficient for high C stocks? • Trade-off between C stocks & storm surge attenuation due to traits? Summary IMPLICATIONS: • No evidence species richness is important for mangrove CCMA ES • Functional diversity in structural traits may be key for coastal protection • Monoculture may be sufficient for high C stocks? • Trade-off between C stocks & storm surge attenuation due to traits? • Greenbelt rehabilitation to maintain functional diversity (MIT focus?) Summary IMPLICATIONS: • No evidence species richness is important for mangrove CCMA ES • Functional diversity in structural traits may be key for coastal protection • Monoculture may be sufficient for high C stocks? • Trade-off between C stocks & storm surge attenuation due to traits? • Greenbelt rehabilitation to maintain functional diversity (MIT focus?) QUESTIONS: • Are these the right traits? Summary IMPLICATIONS: • No evidence species richness is important for mangrove CCMA ES • Functional diversity in structural traits may be key for coastal protection • Monoculture may be sufficient for high C stocks? • Trade-off between C stocks & storm surge attenuation due to traits? • Greenbelt rehabilitation to maintain functional diversity (MIT focus?) QUESTIONS: • Are these the right traits? • Plasticity in low diversity mangroves? Summary IMPLICATIONS: • No evidence species richness is important for mangrove CCMA ES • Functional diversity in structural traits may be key for coastal protection • Monoculture may be sufficient for high C stocks? • Trade-off between C stocks & storm surge attenuation due to traits? • Greenbelt rehabilitation to maintain functional diversity (MIT focus?) QUESTIONS: • Are these the right traits? • Plasticity in low diversity mangroves? • Wider trophic interactions? Thanks! Municipalities of Dumangas, Ajuy, Panay, Ivisan, Kalibo and Ibajay Field assistants Bureau of Soils & Water Management, Cebu TRY Initiative Global Database on Plant Traits – DIVERSITAS/GBP & Max Planck ZSL-Philippines Funding: The Rufford Foundation & The Darwin Initiative.
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