Table 14.1
Estimated median dispersal distances, fecundity, and seed,
source, and dispersal limitation for pioneer species varying in
dispersal mode, seed mass,
and abundance on the BCI 50 ha forest dynamics plot.Seed limitation Source limitation Dispersallimitation1 year 2 years 1 year 2 years 1 year2 yearsSeedmass(mg)nMediandispersal(m)Fecundity(seedscm−2 )Seedbank(years)Wind dispersalAlseis blackiana0.17843.2907.2<20.680.47<0.01<0.010.680.47Cordia alliodora12.5547.018.100.900.860.410.160.820.83Jacaranda copaia4.719321.267.3<20.390.030.22<0.010.250.03Luehea seemannii1.9648.2273.7<20.240.06<0.01<0.010.260.06Terminalia amazonia3.82083.161.3N/A0.290.100.100.010.210.09Animal dispersalAlchornea costaricensis38.51351.333.5N/A0.960.930.01<0.010.960.93Apeiba aspera14.21413.27.8>20.960.940.190.040.950.94Cecropia insignis0.51820.8225.6<20.930.890.230.170.770.73Palicourea guianensis14.310555.650.5N/A0.950.910.740.550.520.67Zanthoxylumspp.11–361080.822.7>300.920.860.500.250.700.81Ballistic dispersalCroton billbergianus24.03672.22.6>400.990.990.940.890.410.61Notes: For each species,nis the number of reproductive-sized individualsin the plot. Seed, source, and dispersal limitation aredefined in the text, and are mean captures to twohundred 0.5 m2traps calculated over 12 years. Mean values forlimitation metrics are presented for 1 or 2 consecutive years. Seed bank data provide the longest reportedperiod ofseed persistence in the soil. Data are presentedfor 11 of 24 pioneer taxa commonly encountered intreefall gaps on BCI (Dallinget al. 1998), and for which sufficient seed captures
to traps allow dispersal parameters to be calculated.Data from Dallinget al. (1997, 2002) and Dalling and Brown (unpub
lished data). N/A=data not available.