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The importance of small gallery forest strips as biological corridors for forest species in a human-dominated landscape in southern Costa Rica Florian Hofhansl, Benjamin S. Seaman, Hellena Binz, Isabell Riedl, Stefan Schneeweihs, Christian H.


  1. The importance of small gallery forest strips as biological corridors for forest species in a human-dominated landscape in southern Costa Rica Florian Hofhansl, Benjamin S. Seaman, Hellena Binz, Isabell Riedl, Stefan Schneeweihs, Christian H. Schulze

  2. Gallery Forest • Costa Rican forestry law protects forest strips of 30-100 m width along every stream and river. • Network of linear forest strips that cross the agricultural matrix of open land. • Some strips are connected to closed forest, while others are entirely isolated.

  3. Gallery Forest

  4. Gallery Forest

  5. Gallery Forest

  6. Habitats • Forest (F): large patches of closed primary or secondary forest. • Connected gallery forest (GC): directly connected to closed forest. • Isolated gallery forest (GI): without canopy connection to closed forest; 300–600 m distance from forest.

  7. Questions • Difference in richness and composition of forest species between habitat types? à Conservation relevance of gallery forest? • Difference between connected and isolated gallery forests? à Importance of connectivity? • Correlation of species richness ( α -diversity ) and species composition ( β -diversity ) of different species groups. à Which measure is better suited for comparing species’ response to habitat change?

  8. Study Sites Forest Connected GF Isolated GF Birds Butterflies Dragonflies Underst. Birds

  9. Sampling Methods Birds (103 forest species; 71.53 % of total): • 33 sites (11 F, 11 GC, 11 GI) • 10 min point counts, 25 m radius • visual and acoustic identification • 10-12 times per site Dragonflies (18 forest species; 34.62 % of total): • 19 sites (5 F, 7 GC, 7 GI) • sweep-netting for 1 hour within 50 metres of shoreline • 3-4 times per site

  10. Sampling Methods Butterflies (53 forest species; 70.67 % of total): • 30 sites (10 F, 10 GC, 10 GI) • sweep-netting and visual identification along 50 m transects • 15 min per transect • 6 times per site Understory Birds (73 forest species; 81.11 % of total): • 12 sites (4 F, 4 GC, 4 GI) • mist-netting with 4 mist-nets per site (12 x 2.5 m, 16 mm mesh) • 3-4 days of mist-netting per site, ca 7 hours per day

  11. Species Richness Number of species 100 F 40 90 GC GI 35 80 Birds & Understorey birds Butterflies & Dragonflies 70 30 60 25 50 20 40 15 30 F 10 20 GC 5 GI 10 Chao 2 esti 0 0 recorded Birds Understorey Birds Butterflies Dragonflies

  12. Species Richness GC 100 % F equivalent GI 100 % F equivalent GI 100 % GC equivalent Birds Understorey Butterflies Dragonflies Chao 2 estimates Birds

  13. Alpha Diversity Spearman rank correlation (of recorded number of species per site): Understorey Birds Butterflies Dragonflies Birds Birds R = -0.02, Understorey N = 12, Birds p = 0.953 R = -0.1, R = -0.04, N = 30, N = 12, Butterflies p = 0.584 p = 0.909 R = 0.17, R = 0.28, R = 0.27, N = 17, N = 6, N = 17, Dragonflies p = 0.512 p = 0.536 p = 0.275 à N = refers to number of sites where both taxa were found à No significant effects - No correlation between taxa! à α -diversity no indicator of changes over habitat types across taxa!

  14. Species Composition Birds Butterflies Dimension 2 * F ≠ GC ≠ GI Stress: 0.19 Stress: 0.14 * F ≠ GC & GI Dragonflies Understorey Birds F GC GI * F ≠ GC ≠ GI Stress: 0.08 * F ≠ GI Stress: 0.22 Dimension 1

  15. Beta Diversity Spearman matrix rank correlation (of Bray-Curtis matrices) : Understorey Birds Butterflies Dragonflies Birds Birds Rho = 0.726, Understorey N = 12, Birds p = 0.001 Rho = 0.661, Rho = 0.452, N = 30, N = 12, Butterflies p = 0.001 p = 0.008 Rho = 0.062, Rho = 0.684, Rho = 0.083, N = 17, N = 6, N = 17, Dragonflies p = 0.302 p = 0.003 p = 0.245 à Based on randomization – significant pattern is NOT incidental! à Changes in composition are similar between taxa à β -diversity as indicator of changes over habitat types across taxa

  16. Conclusions • Species richness: – Highest in forest but substantial number of forest species occur in gallery forests as well. – Conservation value of gallery forests: connected >>> isolated • Species composition: – Forest interior set apart from gallery forests for birds and butterflies but not dragonflies – Distinct species assemblages of understorey birds at connected and isolated gallery forest sites.

  17. Conclusions • No congruency of species richness between taxa. • But: similar changes of species composition . à β -diversity represents better measure for comparing changes over habitat types between species groups than α -diversity . • Conservation implication: (1) gallery forests are important habitat patches for forest species in human-dominated landscapes (2) increase landscape permeability for forest species (3) act as biological corridors for additional forest species (?)

  18. Acknowledgements Ministerio de Costa Rica: MINAE (Ministerio Nacional de Ambiente y Energia) Tropical Research Station La Gamba: Anton Weissenhofer, Werner Huber Victor Cruz-Garcia, Luis Sanchez-Jimenez, Eduardo Arauz-Suarez www.univie.ac.at/bdef

  19. Tropical Research Station La Gamba http://www.lagamba.at

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