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Puerto Rico Northern Karst
Belt Forest Inventory
Additional inventory plots are being installed in
forest areas of special interest on the island of Puerto Rico by
intensifying the USDA Forest Service’s
island-wide Forest Inventory and Analysis (FIA) sampling grid.
One such area is the northwest portion of the island where the forests
grow on limestone bedrock weathered by the tropical climate into
karst landforms (Monroe 1976) . These processes have formed spectacular
landscapes of steep conical hills (“mogotes”), sinkholes (“sumideros”),
and caverns in Puerto Rico. The largest area of karst landscape
(142,544 ha) is found in the northwestern part of the island and
is referred to as the northern karst belt (Lugo et al. 2001) (Fig.
1).
Figure 1. Puerto Rico’s Northern Karst Belt
Generations of agricultural activity left the
northern karst belt largely deforested. Farming of both subsistence
and cash crops took place in the flatter depressions between the
hills where soils were deeper, while steeper hillsides were used
for grazing and fuelwood cutting (Rivera and Aide 1998, Lugo et al. 2001) .
Only small, isolated patches of heavily degraded forest remained
in less accessible or less productive as late as the 1950’s. Subsequent
changes in the Puerto Rican economy and migration to urban areas
resulted in the abandonment of much agricultural land across the
entire island (Rudel et al. 2000) . This trend was also true
for the karst region, and forest has returned to many of the abandoned
fields and pastures (Rivera and Aide 1998) . This newly reforested
region now has some of the largest contiguous blocks of forest remaining
on the island. However, these forests are now coming under pressure
from the needs of the more urbanized population. Karst forest is
now being cleared for urban expansion, such as highway construction
and housing developments (Rivera and Aide 1998, Lugo et al. 2001) .
The forests that grow in the northern karst
belt have many unique features. They provide habitat for over 200
species of birds (16 endemic to the area), and 34 endangered species
(Lugo et al. 2001) . (Download Puerto
Rican Karst-A Vital Resource and the Puerto Rican Karst fact sheet
from the USFWS). These karst forests also have the highest tree
species diversity on the island with over 100 species/ha found (Lugo
et al. 2001) . The northern karst belt’s biological and geological
importance and uniqueness has been recognized, and conservation
efforts are underway. There is a proposal to transfer significant
portions to the public domain, making a comprehensive inventory
of the forest resources especially timely and relevant.
In a collaborative effort of the
USDA Forest Service’s International Institute of Tropical Forestry,
the NGO Citizens for the Karst, and the Puerto Rican Conservation Foundation, an intensified
forest inventory is being completed by intensifying the island-wide
FIA base sampling grid (Brandeis 2003) (or view on-line summary at Puerto
Rico’s Forest Inventory: Adapting the USDA Forest Service’s Forest
Inventory and Analysis Program to a Caribbean Island).
The northern karst belt forest inventory is a regional intensification
of the island-wide Forest Inventory and Analysis (FIA) sampling
grid installed over Puerto Rico. (For more information on FIA,
visit the About Forest
Inventory & Analysis library webpage and the Forest Health Monitoring
website). First, the standard FIA hexagonal grid was
decomposed three times (triple-intensity sampling) and points generated
at the centers of each new hexagonal cell. Then, the study area
was defined using a geological map that shows the locations of the
island’s limestone formations. In a GIS, points from the triple-intensity
grid that fell on limestone formations were chosen as locations
for field sampling points (Fig. 2). Only points that fell on karst
geology within the subtropical moist, wet and rain forest life zones
were chosen for this inventory (See Ewel and Whitmore 1973 for life
zone definitions) . Points that fell on karst geology within the
dry subtropical forest life zone in the southern western area of
the island were excluded.
Figure 2. Northern karst belt inventory and monitoring
sampling grid
This sampling scheme produced 158 sampling points within the northern
karst belt. Of these points, 55 were FIA sampling points. FIA
sampling points are being visited separately as part of the island-wide
inventory. A standard FIA subplot cluster, (for details see: USDA
Forest Service FIA Field data collection procedures for Phase 2
plots. Manual Version 1.6), was installed in areas that met
the Caribbean FIA criteria for forested land (a contiguous area
> 0.4 ha, or > 30 m wide for forested strips, with >10%
canopy coverage in trees). Non-forest plots were located and briefly
described without any further data collection.
A standard FIA subplot cluster, (for details see USDA Forest Service FIA Field Data Collection
Procedures for Phase 2 Plots, Version 1.6), was installed in
areas that met the Caribbean FIA criteria for forested land (a contiguous
area > 0.4 ha, or > 30 m wide for forested strips, with >10%
canopy coverage in trees). Non-forest plots were located and briefly
described without any further data collection.
For each tree within the plot, the following data are recorded:
- Azimuth from plot center to the tree
- Distance to tree from plot center
- Species
- Diameter at breast height (1.37 m)
- Height to top of tree
- Height to base of live crown
- Crown width (average width based on two measurements: N-S and
E-W widths)
- Percent of normal live crown that is in leaf
1)
Quantify forest cover in the northern karst belt
2)
Describe northern karst forest structure in terms
of:
a) Tree
cover and density
b) Species
composition (exotic and native)
c) Tree
health, damage, and potential for pests and disease
d) Leaf
area and canopy coverage
e) Woody
aboveground biomass and carbon
I would like to acknowledge the valuable contributions of this project’s
many collaborators: Dr. Ariel Lugo (IITF), Abel Vale (CdelK) and
Terry Hoffman (USDA-FS NE) for their work on agreements and funding;
Joseph McCollum (SRS-FIA) for the sampling grid; Dr. Eileen Helmer
(IITF) for plot location selection; Olga Ramos (IITF), Wilmarie
Díaz (IITF) and Maya Quiñones (IITF) for GIS mapping; Carlos Rodríguez
(IITF) for GPS support; Esther Rojas (FPC) for project administration;
Ivan Vícens (field work) of the IITF; Orlando Diaz (CdelK), Luis
Ortíz (CdelK), Humfredo Marcano (FPC), Humberto Rodríguez (FPC),
Omar Monsegur (FPC), Ivan Vícens (IITF) for field work and botanical
expertise, Dr. Armando Rodríguez (Univ.
Interamericana) for use of the Mata de Platano Field Station; and
Consuelo Brandeis (FPC) for data entry.
Brandeis, T. J. 2003. Puerto Rico's Forest
Inventory: Adapting the Forest Inventory and Analysis Program to
a Caribbean Island. Journal of Forestry 101:8-13.
Ewel, J. J., and J. L. Whitmore. 1973.
The ecological life zones of Puerto Rico and the US Virgin Islands.
ITF-18, USDA Forest Service Institute of Tropical Forestry, Rio
Piedras, Puerto Rico.
Lugo, A. E., L. Castro-Miranda, A. Vale,
T. del Mar-López, E. Hernández-Prieto, A. García-Martinó, A. R.
Puente-Rolón, A. G. Tossas, D. A. McFarlane, T. Miller, A. Rodríguez,
J. Lundberg, J. R. Thomlinson, J. Colón, J. H. Schellekens, O. Ramos,
and E. H. Helmer. 2001. Puerto Rican Karst - A Vital Resource. General
Technical Report WO-65, USDA Forest Service, Washington, D.C.
Monroe, W. H. 1976. The karst landforms
of Puerto Rico. United States Government Printing Office, Washington,
D.C.
Rivera, L. W., and T. M. Aide. 1998. Forest
recovery in the karst region of Puerto Rico. Forest Ecology and
Management 108:63-75.
Rudel, T. K., M. Perez-Lugo, and H. Zichal.
2000. When fields revert to forest: development and spontaneous
reforestation in post-war Puerto Rico. Professional Geographer 52:386-397.
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