Structure and Demography of Tree Communities in Tropical Secondary Forest Recovering From Logging Keala Cummings and Dr. Diane Thomson 2007 Conclusions Forest not very developed even after 15 years Mature forests: up to 200-250 species/ha (Phillips, 1994) Small tree size Domination of pioneer species Biomass within range of literature values QuickTime™ and a TIFF (Uncompressed) decompressor are needed to see this picture. Literature values very variable Proximity to mature forest? Wind direction? Animal seed vectors? Rainfall? Other environmental factors? Background 60% of all tropical forests are secondary or degraded (ITTO 2002). As mature forest is destroyed, secondary forests become increasingly important in maintaining biodiversity (Dunn, 2004) and in carbon sequestration (Silver, 2000). Future conservation efforts may need to be primarily directed towards secondary forests. Tropical secondary forest recovery is not well understood or studied. Background Firestone Center for Restoration Ecology Located in Dominical, Costa Rica Donated to Pitzer College by Diane Firestone in 2005 QuickTime™ and a TIFF (Uncompressed) decompressor are needed to see this picture. Property previously used for cattle ranching Secondary forest stands 15 years old Project goals Long term goals QuickTime™ and a TIFF (Uncompressed) decompressor are needed to see this picture. To better understand: the processes that affect/influence recovery of secondary forest Their value as habitat for other species Their contribution to carbon uptake and sequestration Project goals Short term goals Establish long-term monitoring plots Characterize baseline tree community Species composition, abundance and distribution Estimate rates of mortality growth biomass biomass accumulation Established two new 30 x 30 m plots in secondary forest. Methods Tagged, mapped and identified all trees (n=530) over 2.0 cm diameter at breast height (dbh). Measured dbh (size) QuickTime™ and a TIFF (Uncompressed) decompressor are needed to see this picture. Remeasured all trees tagged in third plot during 2006. Estimated tree biomasses and basal area using published allometric relationships with dbh. Results Distribution of Tree Sizes 35 25 20 15 10 5 Tree dbh (cm) Plot 1 90 M or e 80 70 60 50 40 30 20 0 10 Number trees Number of trees 30 Results 140 120 120 100 Tree dbh (cm) Plot 2 Tree dbh (cm) Plot 3 • Very few mature trees, lots of saplings. 90 M or e 80 70 60 50 90 M or e 80 70 60 50 40 0 30 0 20 20 10 20 40 40 30 40 60 20 60 80 10 80 0 Number trees 100 0 Number trees Number of trees Distribution of Tree Sizes Plot maps 30 30 25 25 20 20 15 15 10 10 5 5 0 0 0 5 10 15 20 (m) Plot 2 25 30 0 5 10 15 (m) Plot 3 20 25 30 Species diversity Red= Psidium, Green= Piper, Blue= Other 30 30 25 25 20 20 15 15 Figure 3: Plot 2 map showing common species. Red = Psidium, green = Piper. 10 10 5 5 0 0 0 5 10 15 (m) Plot 2 20 25 30 0 5 10 15 20 25 (m) Plot 3 • Total diversity= 17 spp. (most individuals from a few dominants). 30 Species diversity 30 30 25 25 20 20 15 15 10 10 5 5 0 0 0 5 10 15 (m) Plot 2 20 25 30 0 5 10 15 20 25 30 (m) Plot 3 • Other species- clustered due to limited dispersal? Note: Red = Psidium, green = Piper, black = Cecropia, sea green = Miconia (#1), blue= Miconia (#2), sky blue = Miconia (#3), lime = Miconia (#4), orange = Tuete, plum = Guanacaste, pink = tree 1, gold = tree 2, tan = tree 3, brown = tree 4, grey = tree 5, rose = tree 6, blue grey = tree 7, white = collective unknowns. Species Composition 80 70 Blue= Plot 1 60 Red= Plot 2 50 Yellow= Plot 3 40 30 20 10 0 n ow kn Un 7 ee Tr 6 ee Tr 5 ee Tr 4 ee Tr 3 ee Tr 2 ee Tr 1 ee te Tr as ac an Gu e et 4) Tu (# nia 3) co Mi (# nia 2) co Mi (# nia 1) co Mi (# nia co Mi pia cro Ce er Pip ium id Ps • Individual plots have fairly different compositions. Stand Characteristics T able 1 . S tand c harac teris tic s of F ires t one plots . M eas urements are for trees • 5 c m. ____________________________________________ C harac teris tic s P lot 1 P lot 2 P lot 3 15 11 1100 3 2 .6 2 176 162 15 16 15 14 1756 2 1 .3 4 117 - __________________________________________________________________________________________________ S tand age at time of c ens us (yr) S pec ies dens ity (no. s pec ies /9 02)0 m D ens ity of trees • 5 c m dbh (no. s tems /ha) 2 B as al area (m/ha) B iomas s 2 0 0 7 (M g/ha) B iomas s 2 0 0 6 (M g/ha) 1733 2 4 .3 2 128 - __________________________________________________________________________________________________ N ote: V alues of biomas s for s imilar fores ts in literature review: 1 0 - 2 4* 2 M g/ha *Silver et al. (2000) Future Questions: What limits recovery? Seeds? Site conditions? Species composition? Acknowledgements I would like to thank the Andrew W. Mellon Foundation for their grant to the Joint Science Department, Scripps. I would also like to thank my advisor and project supervisor, Dr. Diane Thomson, The Firestone Center for Restoration Ecology, Emily Schultz, Sam Scott, Alicia Hill and Al Binder for an amazing summer. Literature cited Chazdon, Robin L., Alvaro Redondo Brenes, and Braulio Vilchez Alvarado. 2005. Effects of Climate and Stand Age on Annual Tree Dynamics in Tropical Second-Growth Rain Forests. Ecology 86(7):1808-1815. Dunn, Robert R. 2004. Recovery of Faunal Communities During Tropical Forest Regeneration. Conservation Biology 18 (2):302-309. ITTO, Guidelines for the restoration management and rehabilitation of degraded and secondary tropical forests, International Tropical Timber Organization, Yokohama (2002). Philips, 0. L., P. Hall, A. H. Gentry, S. A. Sawyer, and R. Vasquez. Dynamics and species richness of tropical rain forests. Ecology 91:2805-2809. Silver, W. L., R. Ostertag, and A.E. Lugo. The Potential for Carbon Sequestration Through Reforestation of Abandoned Tropical Agricultural and Pasture Lands. Restoration Ecology 8(4):394-407.