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Roble Blanco

Light green lobes with white edges
Other Common Names
White-Cedar
Trumpet
Published
December 1, 1990

Authors
  • 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.

Distribution

Current Distribution

Roble is native to Puerto Rico and widely distributed through the West Indies from Hispaniola to Grenada and Barbados. It is also naturalized in Bermuda and planted in southern Florida (16).

In Puerto Rico, it is widespread in abandoned pastures and secondary forests and found in dry or wet natural forests, except for the highest elevations in the Luquillo Mountains and the Cordillera Central. Elsewhere in the Caribbean, roble is particularly common in dry, coastal woodlands and in secondary forests.

Environmental Associations

Climate and Elevation

In Puerto Rico, roble is found principally in the Subtropical Dry, Subtropical Moist, and Subtropical Wet life zones (12,15) where the annual rainfall varies from about 850 to 2500 mm (33 to 98 in). Temperature ranges from a mean minimum in January of 16° C (61° F) to a mean maximum of 31° C (88° F) in August (5). Potential evapotranspiration over the same regions varies between 1400 and 1900 mm (55 and 75 in) annually, with the lowest measurements in the mountainous interior.

Throughout the West Indies, roble is found predominately in areas where the annual rainfall varies between about 1000 and 2500 mm (39 and 98 in) (table 1). All sites are frost free.

Table 1- Presence of roble blanco (Tabebuia heterophylla) in tropical forests of the Western Hemisphere.

IslandsForest types¹

Puerto RicoDry Evergreen Forest
Lower Montane Rain Forest
NevisDry Evergreen Forest
St. KittsDry Evergreen Forest
DominicaDry Scrub Woodlands
Fire grassland and standards
St. LuciaLittoral Woodland
Dry Scrub Woodlands
Secondary Woodlands
St. VincentDry Scrub Woodlands
GrenadinesDry Scrub Woodlands
GrenadaDry Scrub Woodlands
AntiguaSecondary Woodlands
BarbudaBush land
AnguillaBush land
BarbadosDry Scrub Woodlands
MartiniqueSeasonal Forests
Dry Scrub Woodlands
GuadeloupeDry Scrub Woodlands
Littoral Woodland
British Virgin IslandsDry Scrub Woodland
Xerophytic Rain Fore

¹Roble is found throughout the Windward and Leeward Islands as a component of the Dry Zone Flora with rainfall between 900 to 1700 mm/yr (35 to 65 in/yr). In all instances, classification is according to Beard (1,2,3).


 

Soils and Geology

In Puerto Rico, roble is found on sand, limestone, and heavy clay soils, acid or alkaline in reaction, and residual, alluvial, or colluvial in origin. It appears to grow best, however, on deep clays. Roble is a cosmopolitan species and is found on all soils presently identified in Puerto Rico. The most common soil order on the island is Inceptisols. Physiographically, it is most common on slopes and ridges (19) but is also found on flats adjacent to river beds (9). In general, it is tolerant of degraded sites and abandoned farm lands where it tends to form nearly pure stands.

In Puerto Rico, roble is planted on poor sites to provide cover and to improve the soil. It is recommended for planting on uniform and convex slopes and ridges, where trials have shown it to be a promising species for reforestation (20). It has also done well on humid, waterlogged sites.

Sexual Reproduction

Flowers, Pollination, and Fruit

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).

Seed Production and Dissemination

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.

Germination Requirements

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.

Asexual Reproduction

Vegetative Types

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.

Plant Associations and Site Conditions

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.

Successional Stages and Structural Development

The mature roble in Puerto Rico is easily identified by its opposite, palmately compound leaves, furrowed bark, and narrow, columnar crown. It is a small- to medium-size tree attaining a height of 18 In (60 ft) and a diameter of 60 cm (25 in). In the seedling and sapling stages, roble is an aggressive pioneer.

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).

Growth Rates and Yield Across Stages

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 characteristicsStandMean annual increment
 


LocationElevationAnnual rainfallSoilAge¹DensityHeightD.b.h.Basal area

 mmm yrstems/hamcmm²/ha
Plantations        
Puerto Rico        
Luquillo² (25)3003050residual clay11NA³1.31.181.82
Luquillo² (25)2502550residual clay14100010.931.29
Luquillo (19)3602700eroded ridge54000.50.710.32
Hawaii (28)30 to 6252250 to 5600stoney muck5.3NA0.6 to 0.7NANA
Hawaii (28)180700stoney clay5.6NA0.3NANA
Natural forest        
Puerto Rico        
Sabana (10)180 to 3602300deep acid clay17NANA0.28NA
Rio Grande (10)420 to 6003300deep acid clay17NANA0.35NA
Cubuy300 to 5502000clay loam17NANA0.3NA
St. Just (27)601900shallow clay22150NA0.38NA
Cambalache (27)601400limestone ridge254350NA0.13NA
El Verde (24)4503000acid clay2NANA0.38NA
Luquillo Foothills (24)2002500acid clay112420NA0.39NA
Luquillo Foothills (24)2002500acid clay112700NA0.28NA
 ftin  yrstems/acreftinft²/acre
Plantations        
Puerto Rico        
Luquillo²984120residual clay11NA4.260.467.93
Luquillo²820100residual clay144053.280.375.62
Luquillo1,130106eroded ridge51621.640.281.4
Hawaii98 to 62398 to 220stoney muck5.3NA1.97 to 2.30NANA
Hawaii59028stoney clay5.6NA0.98NANA
Natural forest        
Puerto Rico        
Sabana590 to 1,18090deep acid clay17NANA0.11NA
Rio Grande1,378 to 1,968130deep acid clay17NANA0.14NA
Cubuy984 to 1,80478clay loam17NANA0.12NA
St. Just19775shallow clay2870NA0.15NA
Cambalache19755limestone ridge251,760NA0.05NA
El Verde1,476118acid clay2NANA0.15NA
Luquillo Foothills25698acid clay111,093NA0.15NA
Luquillo Foothills25698acid clay111,093NA0.11NA

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.

Management with Natural Regeneration

Silvicultural Systems

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.

Taxonomy

Tabebuia heterophylla is a variable species that has been classified into subspecies, or related species, by several authors. Synonyms considered by some as varieties include T. pallida (Lindl.) Miers and T. dominguensis Urban (18).

Roble in Puerto Rico typically has five leaflets. In dry areas and coastal thickets in the Lesser Antilles, trees are shorter, fruits and seeds smaller, and leaflet number declines to three, or at times to a single leaflet. Another variation found in Guadeloupe, Dominica, and Martinique has a single, broadly elliptic leaf (16).

Dominant Insects and Diseases

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).

Goods

Wood Products

The heartwood is light brown or golden and not easily separated from the sapwood. The grain is straight to interlocked, and the specific gravity is about 0.55. The wood seasons rapidly with little warping and is fairly easy to work, rating fair for planing, excellent for boring, mortising, and sanding, and good for turning. Penetration and absorption of preservatives is low, even in the sapwood (6,16,17,18). The wood is tough and strong for its weight.

Roble's appearance and technical properties resemble both oak and ash. The wood is widely used for flooring, furniture, cabinetwork, interior trim, tool handles, decorative veneers, boatbuilding, ox yokes, millwork, and sporting goods. Less valuable grades are suitable for boxes, crates, concrete forms and similar items, and occasionally for posts and poles (16,17,18).

Nonwood Products

Roble is also classed as a honey plant.

Ecosystem Services

Forest Carbon and Nutrient Dynamics

The tree comes in readily on abandoned farm soils and is particularly adapted to degraded sites. Foresters have planted it on abandoned farmlands where its growth has been slow, but satisfactory.

Other (Additional Considerations)

Roble's large flowers and narrow, columnar crown have made it a favorite ornamental in yards and along roadsides throughout Puerto Rico. Flowering in many instances has been observed a few years after planting (22).

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  2. Beard, J. S. 1949. The natural vegetation of the Windward and Leeward Islands. Oxford Forestry Memoirs 21. Clarendon Press, Oxford. 192 p.
  3. Beard, J. S. 1955. The classification of tropical American vegetation-types. Ecology 36(l):89-100.
  4. Briscoe, C. B., and F. H. Wadsworth. 1970. Stand structure and yield in tabonuco forests of Puerto Rico. In A tropical rain forest. H. T. Odum, and R. F. Pigeon, eds. B79-89. U.S. Atomic Energy Commission, TID-24270. Washington, DC. (Available from National Technical Information Service, Springfield, VA.)
  5. Calvesbert, R. J. 1970. Climate of Puerto Rico and U.S. Virgin Islands. Rev. U.S. Department of Commerce, Environmental Science Services Administration, Washington, DC. 29 p.
  6. Chudnoff, Martin. 1984. Tropical timbers of the world. U.S. Department of Agriculture, Agriculture Handbook 607. Washington, DC. 464 p.
  7. Ciferri, R. 1949. La escoba de bruja de Algunos arboles de sombrio del cacao (Erythrina y Tabebuia) en Venezuela. Una enfermedad de origen no criptogámico. Revista de la Facultad Nacional de Agronomía 10(34):143-147. Medellin, Colombia.
  8. Cook, M. T. 1938. The witches' broom of Tabebuia pallida in Puerto Rico. Journal of Agriculture of University of Puerto Rico 22:441-442.
  9. Crow, T. R., and D. F. Grigal. 1979. A numerical analysis of arborescent communities in the rain forest of the Luquillo Mountains, Puerto Rico. Vegetatio 40(3):135-146.
  10. Crow, T. R., and P. L. Weaver. 1977. Tree growth in a moist tropical forest of Puerto Rico. USDA Forest Service, Research Paper ITF-22. Institute of Tropical Forestry, Rio Piedras, PR. 17 p.
  11. Estrada Pinto, Alejo. 1970. Phenological studies of trees at El Verde. In A tropical rain forest. H. T. Odum, and R. F. Pigeon, eds. D237-269. U.S. Atomic Energy Commission, TID-24270. Washington, DC.
  12. Ewel, J. J., and J. L. Whitmore. 1973. The ecological life zones of Puerto Rico and the U.S. Virgin Islands. USDA Forest Service, Research Paper ITF-18. Institute of Tropical Forestry, Rio Piedras, PR. 72 p.
  13. Flake, H. W. 1980. Tropical Report-Puerto Rico, January 13-19, 1980. USDA Forest Service, Forest Insect and Disease Management, Asheville, NC. 21 p.
  14. Flavell, T. H., and W. R. Phelps. 1973. Evaluation of tree insect and disease pests in Puerto Rico and the Virgin Islands. USDA Forest Service, Forest Pest Management Group Report 74. Southeastern Area State and Private Forestry, Atlanta, GA. 19 p.
  15. Holdridge, L. R. 1967. Life zone ecology. Rev. Tropical Science Center, San José, Costa Rica. 206 p.
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  18. Longwood, Franklin R. 1962. Present and potential timbers of the Caribbean. U.S. Department of Agriculture, Agriculture Handbook 207. Washington, DC. 167 p.
  19. Marrero, José. 1947. A survey of the forest plantations in the Caribbean National Forest. Thesis (M.S.), University of Michigan, Ann Arbor. 167 p.
  20. Marrero, José. 1950. Results of forest planting in the insular forests of Puerto Rico. Caribbean Forester 11:107-147.
  21. Marrero, José. 1950. Reforestation of degraded lands in Puerto Rico. Caribbean Forester 11:3-15.
  22. Schubert, Thomas H. 1979. Trees for urban use in Puerto Rico and the Virgin Islands. USDA Forest Service, General Technical Report SO-27. Southern Forest Experiment Station, New Orleans, IA. (Institute of Tropical Forestry, Rio Piedras, PR.) 91 p.
  23. Smith, Robert Ford. 1970. The vegetation structure of a Puerto Rican rain forest before and after short-term irradiation. In A tropical rain forest. H. T. Odum, and R. F. Pigeon, eds. D103-140. U.S. Atomic Energy Commission, TID-24270. Washington, DC.
  24. Tropical Forest Experiment Station. 1950. Tenth annual report. Caribbean Forester 11(2):59-80.
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  26. Wadsworth, Frank H. 1981. Personal communication. Institute of Tropical Forestry, Rio Piedras, PR.
  27. Weaver, Peter L. 1979. Tree growth in several tropical forests of Puerto Rico. USDA Forest Service, Research Paper SO-152. Southern Forest Experiment Station, New Orleans, LA. (Institute of Tropical Forestry, Rio Piedras, PR.) 15 p.
  28. Whitesell, Craig D., and G. A. Walters. 1976. Species adaptability trials for man-made forests in Hawaii. USDA Forest Service, Research Paper PSW-118. Pacific Southwest Forest and Range Experiment Station, Berkeley, CA. 30 p.
  29. Wolcott, G. N. 1957. Inherent natural resistance of woods to the attack of the West Indian dry-wood termite, Cryptotermes brevis Walker. Journal of Agriculture of the University of Puerto Rico 41:259-311.
Citations
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