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NFT HighlightsNFTA 94-03, April 1994A quick guide to useful nitrogen fixing trees from around the world |
Alnus acuminata: Valuable Timber Tree for Tropical Highlands
Alnus acuminata is a fast-growing species valued for its wood,
watershed protection and soil improvement. Native from Mexico to Northern
Argentina, it is known as: aliso (Mexico, Argentina, Colombia, Ecuador
and Peru); aile, ilite (Mexico); ramrám, lambdn (Guatemala, Costa
Rica and Peru); jaúl (Costa Rica); palo de lama (Guatemala) and;
cerezo and chaquiro (Colombia). Easily propagated from seed or by natural
regeneration, A.acuminata is a popular agroforestry species in its
native range. It has been successfully introduced into southern Chile and
southern New Zealand.
| Botany
Alnus acuminata ssp. arguta (Schlectendal) Furlow (Betufaceae) grows to 30 m in height and to 50 cm in diameter (after 30 years) in natural conditions. Maximum age may be 60 years (L Fournier, personal communication). The leaves are simple, alternate, elliptical, 6 to 15 cm long, 3 to 8 cm wide, border double dentate, deciduous or semideciduos. The upper leaf surface is dark green and the lower surface is pale, whitish to light green. The bark is light-grey or silvery with yellowish lenticels. Crown shape is open rounded to pyramidal. Male and female flowers occur in separate catkins on the same branch. Inflorescences are cone-like with lignified scales, dark brown when ripened, and bearing more than 100 fruits per cone. The fruit is a small membranous-winged samara, 2 to 3 mm long that contains one seed. Dispersal is mainly by the wind. Seeds ripen in February, March and August in South America (NAS, 1980), and from September to January in Costa Rica (Rajas et al., 1991). |
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Distribution and ecology
Alnus acuminata is native to the American continent ranging
from Mexico to Northern Argentina in elevations between 1,200 and 3,200
m.a.s.l. where annual rainfall is 1,000 to 3,000 mm or more. The species
occurs where mean annual temperature ranges between 4o, and
27oC; however it can withstand temperatures dipping briefly
below 0o C (NAS, 1980).
Alnus acuminata is a fast-growing pioneer species that regenerates
naturally in open, disturbed areas. It grows in moist soil environments,
usually along the banks of streams, rivers, ponds, and swamps where it
typically forms dense pure stands.
It also can be associated with wet flood plains, or moist mountain
slopes, although it may be adapted to somewhat drier conditions. However,
it is usually restricted to zones with extra soil moisture such as cool,
tropical highlands, and cool, high-latitude regions with abundant rainfall
where mist and cloud cover can be a source of fog-drip precipitation. In
tropical highlands of Central and South America, clouds and mist am important
in supporting Alnus acuminata and grass, when associated, through
the dry season.
Alnus acuminata prefers deep, well-drained soils with high organic matter content. However, it is commonly found growing on shallow soils, such as landslides. Rojas et al. (1991) report that it will grow in soil with pH as low as 4.5.
Uses
Timber. Alnus acuminata wood is light brown-yellow to
pink, odorless, and tasteless, without differences between the heartwood
and the sapwood. Reports on specific gravity vary from 0.34 to 0.39 (Tuk,
1980) and 0.5 to 0.6 (NAS, 1980). The calorific value is 19,250 kJ/kg (CATIE
1986). The wood dries easily and preserves well. It has even grain, seasons
fairly well, and is easy to work and finish by hand or machine. Despite
its light weight it is tough and strong, and is sometimes used for construction.
Timber is also used for fuelwood, posts poles, light lumber, boxes, broom
handles, domestic implements, plywood cores, particle board, and musical
instruments. A match company in Colombia evaluated more than 20 native
species and found Alnus acuminata wood best suited for making stick
matches (Ing. R. Arismendi, Personal Communication).
Agroforestry. Farmers in Costa Rica have grown Alnus acuminata in pastures and as a shade tree for coffee crops for more than 90 years. Trees are regenerated naturally or planted from nursery stock at spacings of 8 to 14 m (about 100 trees/ha).
One benefit of including trees in cattle pastures is greater milk production--cows on pastures with Alnus acuminata produce more than cows on pastures without it (Budowski, 1983). Farmers in Costa Rica sometimes construct crude fences around individual seedlings to protect them from livestock-protection is needed until trees grow tall enough that livestock can not browse new growth.
Silviculture
Propagation. Alnus acuminata is propagated by seeds (more
than 2 million pure seeds/kg). Seeds are recalcitrant and must be planted
quickly-viability decreases from 70% to 20% in a few months. Seed viability
can be extended by storing seed in airtight containers at 5oC-viability
is 50% and 31 % after 2 and 3 months, respectively (Rojas et al., 1991).
No seed pre-treatment is necessary. Rojas et al. (1991) recommend broadcasting seed in germination beds (15 to 20 g of seed per ml of bed) and covering them with a very thin layer of mixed soil and sand. The germination bed should be a 1:1:2 mixture of fine soil, sand and organic material. Seeds should be watered twice daily with a very fine mist to maintain soil humidity. Overwatering may cause darnping-off. Germination starts 6 to 7 days after sowing and is complete within 15 days. The most vigorous seedlings should be transplanted to pots or back plastic bags 20 days after germination. Seedlings may be planted out when they are 20 cm tall (in about four months). Bare-root seedlings and stump cuttings are possible alternatives to container-grown seedlings. Seedlings do not compete well with weeds so frequent weeding is important (Rojas et al., 1991).
Management. Alnus acuminata is grown in plantations mainly in Colombia and Costa Rica, but in other countries as well. In Colombia, an initial spacing of 2.6 x 2.6 m (1,480 trees/ha) is common (Sieco Smit, 1971). In Costa Rica, an initial spacing of 3 x 3 m is preferred. At least two thinnings are recommended, the first after the third year and the second after 10 to 15 years, leaving 250 to 350 trees per hectare. Trees are harvested in rotations of about 20 years. Average annual wood production is 15 to 20 M3 per hectare. According to Canet (1985), a stand of 30-year-old trees with a density of 35 trees/ha yielded 70 m3/ha of timber, 18.3 ton/ha of dry fuelwood, and 3.6 ton/ha of leaves and fine branches. Alnus acuminata resprouts vigorously from the stump after cutting.
Symbiosis
Alnus acuminata, like other Alnus species, forms a symbiosis
with actinomycetes of the genus Frankia. Rojas et al. (1991) report
that nodules begin to grow on 13-day-old nursery seedlings. Estimates of
nitrogen fixation for Alnus species vary widely between 62 kg/ha/yr for
A. sinuata in Alaska and 125 kg/ha/yr for A. glutinosa to
320 kg/ha/yr for A. rubra in Oregon (Carlson and Dawson, 1985). In a 2-year-old
A. acuminata plantation in the Colombian highlands (1200 trees/ha),
Carlson and Dawson (1985) estimate an annual increase in soil nitrogen
of 279 kg/ha. Acetylene reduction values for 120-day-old A. acuminata greenhouse
seedlings inoculated with a crushed nodule suspension were between 32.5
and 86.4 pmol of ethylene produced per gram of nodule dry weight
per hour (Russo and Berlyn, 1988).
Pests and diseases
Alnus acuminata is susceptible to attack by defoliators (Nodonota
irazuensis and Nodonota ca. parvula, Coleoptera, Chrysomelidae).
A stem borer Scolytoes alni, (Coleoptera, Scolytidae) has been observed
in Costa Rica during the dry season. Vertebrates such as Sciurus
sp. (Rodentia, Sciuridae) may cause debarking and Sylvilagus brasiliensis
(Lafomorpha, Leporidae) may destroy seedlings. Fungi such as Fusarium
sp. and Trichoderma sp. may damage seeds; Colletotrichum
Sp. and Phomopsis sp. may affect leaves; and Rosellinia sp.
may affect stems and roots in mature trees (CATIE, 1991).
References
Budowski, G. 1983. An attempt to quantify some current agroforestry
practices in Costa Rica. In Huxley, P.A. ed. Plant Research in Agroforestry.
Nairobi, Kenya, ICRAF. Pp. 43-62.
Canet, G.C. 1985. Caracteristicas del sistema silvo-pastoril jaúl ( Alnus acuminata) con lecheria de altura en Costa Rica. In R. Salazar ed. Técnicas de producción de leña en fincas pequenas. Actas de los simposios. CATIE, Turrialba, 24-28 de junio, 1985. pp. 241-249.
Carlson, PJ. and J.0. Dawson. 1985. Soil nitrogen changes, early growth, and response to soil internal drainage of a plantation of Alnus jorullensis in the Colombian highlands. Turrialba 35(2):141-150.
CATIE. 1986. Silvicultura de especies promisorias para producción de leña en América Central. CATIE, Turrialba, Costa Rica. p. 51.
CATIE- 1991. Plagas y enfermedades forestales en América Central:
guía de campo. CATIE, Turrialba, Costa Rica.
185 p.
Furlow, JJ. 1977. Betulaceae.. In Burger, W. Flora Costaricensis. Fieldiana: Botany 40-56-58.
Furlow, JJ. 1979. The systematics of the American species of Alnus (Betulaceae). Rhodora 81(825):1-121.
Holdridge, L.R. 1951. The alder, Alnus acuminata, as a farm timber tree in Costa Rica. Caribbean Forester 12(2):47-57.
National Academy of Sciences. 1980. Firewood crops: shrub and tree species for energy production Vol. 1. National Academy of Sciences, Washington, D.C.
Rojas, F., G. Torres, E. Arnáez and I, Moreira. 1991. Jaúl cuademos cientificos y tecnológicos, especies forestales tropicales, No. 1. Instituto Tecnológico de Costa Rica, Cartago, Costa Rica. 9 p.
Russo, R.O. and G.P. Berlyn. 1989. The effect of a new growth biostimulant on acetylene reduction in modulated seedlings of Alnus acuminata. Nitrogen Fixing Conference Abstracts. Ames, Iowa. July 30-August 3, 1989.
Sicco Smit, G. 1971. Notas silviculturales sobre Alnus joti;;rmdods de Caldas, Colombia. Turrialba 21:83-88.
Tuk, J. 1980. Informe general del proyecto: Clasiflcación
y normalización de maderas para uso estructural.. Instituto
Tcnológico de Costa Rica, Cartago, C.R.
A publication of the Forest, Farm, and Community Tree Network (FACT Net)
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