You are here
Species
Tabebuia heterophylla ssp. pallida auct. non (Miers) Stehl
IUCN
NCBI
EOL Text
In Puerto Rico, roble is associated with algarrobo (Hymenaea courbaril), laurel avispillo (Nectandra coriacea), guamá (Inga fagifolia), and laurel geo (Ocotea leucoxylon) in the Dry Evergreen Forest (classification according to Beard, 1,2,3). In the Lower Montane Rain Forest of the Luquillo Mountains, it is found associated with guamá, yagrumo macho (Didymopanax morototoni), palo de matos (Ormosia krugii), achiotillo (Alchornea latifolia) and various composites, all of which are constituents of the secondary vegetation (9).
In the Windward and Leeward Islands, roble is frequently found with the same species listed for the Dry Evergreen Forest of Puerto Rico. Beard (2) called this the dry zone flora, of which the Dry Evergreen Forests, Dry Scrub Woodland, and Littoral Woodland are the principal forest types.
In the natural forest, pathogens do not appear to be of any consequence. However, branches of city and roadside trees are often deformed into a witches' broom appearance, apparently by a virus possibly transmitted by the leaf hopper Protalebra tabebuiae (8). The insect also defoliates the tree or causes the leaves to turn yellow and fall prematurely (16,22). A similar disease on a closely related species, Tabebuia pentaphylla, was observed on trees grown for cacao shade on the Paria peninsula of Venezuela (7). Because of the numerous problems with pathogens, some authorities have recommended that closely related members of the same genus be used as substitutes in ornamental plantings.
A dieback disease was observed in 3 percent of potted trees in the Cambalache nursery on the north coast of Puerto Rico and was attributed to Botryodiplodia spp. (13). Transplants from a nearby wooded area to a golf course near the town of Dorado were infested by a shoot borer, probably Pachymorphus subductellus (14).
The heartwood is rated as moderately durable in contact with the ground, but susceptible to Cryptotermes brevis, the dry wood termite (6,29) and marine borers (16). Moreover, the wood rates only fair in weathering characteristics. Unpainted wood loses its smooth surface and develops considerable checking (17).
The silviculture of roble was also investigated by the staff of the Institute during the mid-1940's. Roble wildlings underplanted in an Australian beefwood (Casuarina equisetifolia) stand, a species used to provide a light shade, showed 80 percent survival after 18 months, but growth was very slow. In another experiment with nursery seedlings raised in sun vs. shade conditions, 40 percent greater height growth was ob served in the exposed conditions after 5 months. Shaded seedlings grew very little. In natural conditions, wildlings are capable of surviving shade for years with no appreciable growth (21).
Roble regenerates and forms pure stands on grasslands and degraded soils, in particular on exposed upper slopes and ridges, where competition from faster growing, larger, and more tolerant trees is lacking (19). Plantations of roble wildlings usually require weedings where grass is dense, one at 6 months and a second at about 18 months. Plantations should have close spacing, not greater than 1.8 by 1.8 m (6 by 6 ft), so that ground cover is provided rapidly (21).
Within the Lower Montane Rain Forest (1,2,3) of the Luquillo Mountains, roble was found on four of six permanent plots totaling 2.1 ha (5.2 acres), measured since the mid-1940's. Of the 30 species studied, it ranked 25th in density, 14th in basal area dominance, and 15th in volume (4). Moreover, on a scale of 1 (most tolerant) to 29 (most pioneer), roble ranked 20th in shade tolerance among tree species in the Luquillo Forest (23). The scale considered the presence of seed, seedlings, and understory trees within the forest. Overall, roble blanco is classed as intolerant of shade.
Roble's persistence in the natural forest, despite its slow growth, is largely attributable to its capacity to survive on poor sites where competition is minimized.
The use of wildlings as planting stock revealed that young roble develops a thick stem and well-developed root system at an early age (21).
Cuttings were tested on degraded heavy soils in Luquillo Forest and Carite, but only a few survived (19,20). Roble fence posts have been observed to sprout (26), but vegetative reproduction cannot be relied on for reforestation.
Germination of roble is epigeal. Experiments by staff of the Institute of Tropical Forestry established roble in two different regions by means of broadcast seeding, spot planting of seeds, and planting, on lands that had been burned, cleared in a swath 1 m (3.3 ft) wide, or planted without site treatment. Direct seeding proved unsuccessful. The nursery stock survived, although the seedlings suffered dieback and did not recover for 6 to 8 months. Site treatment did not influence survival because grass grew quickly on all areas under study and competed with the transplants. The seedlings, after recovery, grew slowly.
Transplanting of wildlings was found preferable to nursery stock because they are abundant and have better root systems (21). In some instances, however, dieback of the leader was observed. Pruned wildlings and shelterwood plantings of wildlings were then tested, but neither gave better results. Survival remained good, but growth was not improved.
The lesson learned from testing of roble wildlings was that survival is high, even on waterlogged soils and exposed ridges. Leaves are lost after transplanting and the wildlings require about 6 to 8 months to recover, if rainfall is adequate. Of the size classes tested ranging through 60 cm (24 in), the best results were attained with the largest wildlings. Subsequent growth in all instances was slow and averaged about 1.8 m (6 ft) in 2 years.
The fruits are pods, about 8 to 20 cm (3 to 8 in) long and 6.5 mm (0.25 in) in diameter. The pods contain many winged seeds each about 2 cm (0.79 in) long. The capsule splits along two lines and seeds are dispersed varying distances from the parent tree, ranging up to 100 m (330 ft) or more, depending upon weather conditions. Dispersal is by wind. The seeds germinate in open areas and form dense stands of seedlings.
Several seed experiments were conducted at the Institute of Tropical Forestry during the mid-1940's. About 70,000 air-dried seeds were counted per kilogram (31,750/lb), and these had a mean moisture content of 31 percent, based on the dry weight of the seeds. Seeds sown directly in seedbeds after collection in the field showed germination rates of 90 percent within 2 weeks. A 3-week delay in sowing seeds reduced viability to about 55 percent and after 5 weeks, no seeds germinated. Attempts were made to store seeds for long periods using seed moisture contents of 100, 75, 50, and 25 percent at room temperature and at 4' C (40' F). The best germination after 25 months, nearly 55 percent, was attained with the lowest moisture content and temperature combination.
Large white to light purple perfect flowers are borne few to several in terminal and lateral clusters, or occasionally as individuals. In Puerto Rico, flowering is chiefly in the spring, or dry season, and is accompanied by complete leaf drop (11,16). Sporadic flowering occurs at other times. Fruits are borne in May and June with fruit fall varying from July through September. Mature fruits, dark brown cigarlike pods, may be found on the tree during most of the year (16).
At 55 randomly placed collection stations comprised of 0.5 m² (5.4 ft²) screen baskets in the Subtropical Wet Forest of Puerto Rico, roble dropped 39 fruits in 39 months. Of the 38 species observed, roble ranked 37th in the number of fruits collected (11).
Roble regenerates well in open fields and develops into a dense stand of seedlings, after which it appears to stagnate. This phenomenon may be partially attributable to the shallow, infertile soils and to exposure. The density of the seedling stands may also be a contributing factor.
Plantations established in Puerto Rico show that the dominant and codominant stems averaged about 1 in (3.3 ft) in height growth and I cm (0.4 in) in diameter growth annually over a period of 11 to 14 years (table 2). Annual basal area growth was about 1.5 m² /ha (6.5 ft² /acre). Height growth in Hawaii was less, but the measurements were for smaller trees over a shorter period of time.
Within natural forest, diameter increment varies between 0.28 to 0.39 cm (0.11 to 0.15 in) annually for all sites with the exception of limestone ridges where growth was only 0.13 cm (0.05 in) (table 2). In a study of several crop trees within the Sabana compartment of the Luquillo Forest, roble was found to grow significantly slower than the remaining species (10). Differences by crown class were evident. On more than 435 trees within the Sabana 8 compartment, annual diameter growth for dominants was 0.38 cm (0.15 in), codominants 0.32 cm (0.13 in), intermediates 0.21 cm (0.08 in), and suppressed stems 0.09 em (0.03 in). Moreover, diameter growth increased with increasing diameter class, perhaps due to a more favorable competitive position within the canopy (10).
Table 2- Growth information for roble blanco (Tabebuia heterophylla) in the Western Hemisphere Site characteristics Stand Mean annual increment Location Elevation Annual rainfall Soil Age¹ Density Height D.b.h. Basal area m mm yr stems/ha m cm m²/ha Plantations Puerto Rico Luquillo² (25) 300 3050 residual clay 11 NA³ 1.3 1.18 1.82 Luquillo² (25) 250 2550 residual clay 14 1000 1 0.93 1.29 Luquillo (19) 360 2700 eroded ridge 5 400 0.5 0.71 0.32 Hawaii (28) 30 to 625 2250 to 5600 stoney muck 5.3 NA 0.6 to 0.7 NA NA Hawaii (28) 180 700 stoney clay 5.6 NA 0.3 NA NA Natural forest Puerto Rico Sabana (10) 180 to 360 2300 deep acid clay 17 NA NA 0.28 NA Rio Grande (10) 420 to 600 3300 deep acid clay 17 NA NA 0.35 NA Cubuy 300 to 550 2000 clay loam 17 NA NA 0.3 NA St. Just (27) 60 1900 shallow clay 2 2150 NA 0.38 NA Cambalache (27) 60 1400 limestone ridge 25 4350 NA 0.13 NA El Verde (24) 450 3000 acid clay 2 NA NA 0.38 NA Luquillo Foothills (24) 200 2500 acid clay 11 2420 NA 0.39 NA Luquillo Foothills (24) 200 2500 acid clay 11 2700 NA 0.28 NA ft in yr stems/acre ft in ft²/acre Plantations Puerto Rico Luquillo² 984 120 residual clay 11 NA 4.26 0.46 7.93 Luquillo² 820 100 residual clay 14 405 3.28 0.37 5.62 Luquillo 1,130 106 eroded ridge 5 162 1.64 0.28 1.4 Hawaii 98 to 623 98 to 220 stoney muck 5.3 NA 1.97 to 2.30 NA NA Hawaii 590 28 stoney clay 5.6 NA 0.98 NA NA Natural forest Puerto Rico Sabana 590 to 1,180 90 deep acid clay 17 NA NA 0.11 NA Rio Grande 1,378 to 1,968 130 deep acid clay 17 NA NA 0.14 NA Cubuy 984 to 1,804 78 clay loam 17 NA NA 0.12 NA St. Just 197 75 shallow clay 2 870 NA 0.15 NA Cambalache 197 55 limestone ridge 25 1,760 NA 0.05 NA El Verde 1,476 118 acid clay 2 NA NA 0.15 NA Luquillo Foothills 256 98 acid clay 11 1,093 NA 0.15 NA Luquillo Foothills 256 98 acid clay 11 1,093 NA 0.11 NA ¹As used in natural forests, age refers to the duration of measurements.
²Growth increment recorded for dominant and codominant stems.
³Not available.
From a sample of 360 trees ranging in diameter from 9 to 40 cm (3.5 to 15.7 in) growing within a secondary, thinned stand, it was estimated that roble would attain the 40 cm (16 in) diameter class in about 100 years.
Bignoniaceae -- Bignonia family
P. L. Weaver
Roble blanco or white-cedar (Tabebuia heterophyl1a) is a small- to medium-size, mostly deciduous tree with showy pink flowers. It grows on any soil type and will adapt to poor or degraded soils if moisture is available. Valued as a timber tree, it has been widely planted for both reforestation and ornamentation. The tough strong wood is used for many products and is favored for boat building in the Lesser Antilles.