Regeneration and stand dynamics of Fitzroya cupressoides (Cupressaceae) forests of southern Chile’s Central Depression
Introduction
Fitzroya cupressoides (Mol.) Johnst. (Cupressaceae, common name “alerce”) is a threatened, long-lived conifer endemic to the temperate rain forests of southern Chile and adjacent portions of Argentina. It can attain a size of up to 5 m in diameter and 50 m in height, often appearing as an emergent when mixed with other species (Lara, 1991). With a lifespan greater than 3600 years (Lara and Villalba, 1993), it is one of the longest-lived tree species worldwide. Historically, Fitzroya was found in a variety of forest types and site conditions at elevations ranging from sea level to over 1200 m. The over-exploitation of Fitzroya, owing to the beauty and decay-resistance of its wood, has left extensive areas degraded and has significantly reduced its original abundance. In addition, many former Fitzroya forests have been intentionally burned and converted to agricultural land. Fitzroya re-establishment on harvested sites, as well as on most burned sites, has been scarce or nonexistent. Because of these threats, in 1975 Fitzroya was listed on Appendix I of the Convention on International Trade in Endangered Species (CITES), which reduced harvesting pressure on the species by banning its commercial international trade. In 1976, the Chilean government declared every living Fitzroya a “national monument”, which provided in-country protection against further harvesting. More recently, the World Conservation Union, IUCN, has listed Fitzroya as endangered on their Red List of Threatened Plants (Oldfield et al., 1998).
In Chile, Fitzroya occurs in the Coastal Cordillera from ca. latitude 39°50′ to 42°35′, and in the Andean Cordillera from ca. 41° to 43°30′. It was once abundant in Chile’s Central Depression (which lies between the two Cordilleras, south and west of Llanquihue Lake; Fig. 1) before extensive logging began there in the mid-1800s. Over the last decade, several remnant Fitzroya populations have been located in Chile’s Central Depression, where the species was thought to have been extirpated (Veblen et al., 1976, Golte, 1996).
The current study was generated by field observations that Fitzroya has not re-established on much of its former habitat in the Depression, and on those sites where it currently exists, it exhibits a large amount of within- and between-site variability in seedling density. Compared to either Cordillera where Fitzroya occurs, the Depression has much lower rainfall, lower elevation, a longer growing season, and drastically different soils, which led us to speculate that its regeneration and stand dynamics may differ accordingly. Our objective was to determine the regeneration mode (Veblen (1992), the regeneration behavior in relation to disturbance), regeneration niche (Grubb (1977), the micro-environmental conditions under which a species becomes established), and regeneration mechanism (by seed or vegetative regeneration) of Fitzroya populations in the Central Depression. Given that these stands were only recently discovered, this is the first study of Fitzroya regeneration and stand dynamics in the Central Depression.
Section snippets
Study area
Chile’s Central Depression ranges between 50 and 75 km in width, and reaches nearly 200 m in elevation in its northern extreme. From Llanquihue Lake, it gradually descends southward until reaching sea level in the Gulf of Ancud. The Depression is characterized by an oceanic cool temperate climate. The nearest weather station in Puerto Montt registers a mean annual temperature of 11.5 °C and an annual rainfall of 1912 mm, with the winter months (June–August) receiving the most rain (300 mm per month
Age-class distributions
All stands except Fundo Nuñez showed single-cohort age-class distributions of Fitzroya (Fig. 2), indicating that the populations became established in one wave of regeneration that likely followed a catastrophic disturbance. Thus, Fitzroya’s regeneration mode in the Depression can be considered “catastrophic” (Veblen, 1992). The distinct cohort structure of Fitzroya results from its shade intolerance: once a stand matures and the canopy closes, recruitment of new individuals drops off
Conclusions
Earlier authors interpreted the lack of Fitzroya regeneration under its own canopy or in clear-cut areas as regeneration failure of this species (see Veblen et al. (1976) and Veblen and Ashton (1982) for discussion). More recent research has demonstrated adequate regeneration of Fitzroya in the Coastal and Andean Cordilleras given the appropriate site conditions (Veblen and Ashton, 1982, Lara, 1991, Donoso et al., 1993, Parker and Donoso, 1993, Lara et al., 1999). The results of this current
Acknowledgements
This research was funded by a UK Darwin Initiative grant administered through the Conifer Conservation Programme of the Royal Botanic Garden, Edinburgh, and the University of Edinburgh, Scotland. We thank Nelson Garcı́a, José Camilo Gómez, Alfredo Núñez, and Nelson Velázquez for granting access to their properties, Bernardo Escobar, Sebastián Dı́az, Oscar Larraı́n, Carlos Lehnebach, and Rodrigo Vergara for assistance in the field, Alexia Wolodarsky-Franke for her assistance with the processing
References (38)
- et al.
Natural regeneration of Fitzroya cupressoides in Chile and Argentina
For. Ecol. Manage.
(1993) - et al.
The regeneration status of Fitzroya cupressoides in the Cordillera Pelada, Chile
Biol. Conserv.
(1982) - et al.
Genetic variation in Fitzroya cupressoides cultivated in the British Isles, assessed using RAPDs
Edinb. J. Bot.
(1998) - et al.
Genetic variation in Fitzroya cupressoides (alerce), a threatened South American conifer
Mol. Ecol.
(1999) - et al.
A comparison of spatial patterns of trees in some tropical and temperate forests
Biotropica
(1986) - Barker, P.C.J., 1992. Autecology of Phyllocladus and Anodopetalum in Tasmania. Tasmania NRCP Technical Report 10,...
- Besoain, E., 1985. Los suelos. In: Tosso, J. (Ed.), Suelos volcánicos de Chile. Instituto de Investigaciones...
- et al.
Silica gel: an ideal material for field preservation of leaf samples for DNA studies
Taxon
(1991) - Diggle, P.J., 1983. Statistical Analysis of Spatial Point Patterns. Academic Press, New...
- et al.
Dynamics of Fitzroya cupressoides forests in southern Chile
J. Veg. Sci.
(1993)
An evaluation of errors in tree age estimates based on increment cores in kahikatea (Dacrycarpus dacrydioides)
N.Z. Nat. Sci.
Composition and structure of remnant Fitzroya cupressoides forests of southern Chile’s Central Depression
J. Torrey Bot. Soc.
The ecology of Lagarostrobos franklinii (Hook. f.) Quinn (Podocarpaceae) in Tasmania. 2. Population structure and spatial pattern
Aust. J. Ecol.
The maintenance of species richness in plant communities: the importance of the regeneration niche
Biol. Rev.
Tree dispersion, abundance, and diversity in a tropical dry forest
Science
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Present address: Departamento de Ecologı́a, Universidad de Salamanca, Salamanca, Spain.
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Present address: Applied Genetics, John Innes Centre, Norwich, NR3 7UH, UK.
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Present address: UNEP, World Conservation Monitoring Centre, 219 Huntingdon Road, Cambridge CB3 0DL, UK.