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G846 Caribbean Montane Ruderal Forest Group

Type Concept Sentence: These Caribbean ruderal forests are dominated by Syzygium jambos, Guarea guidonia, Prestoea acuminata var. montana, and other pioneer or secondary forest trees. They occur in high rainfall montane and submontane areas which were landslides or were formerly used for coffee production, other agriculture, agroforestry, or grazing.


Common (Translated Scientific) Name: Caribbean Montane Ruderal Forest Group

Colloquial Name: Caribbean Montane Ruderal Forest

Hierarchy Level:  Group

Type Concept: This ruderal forest occurs in high rainfall montane and submontane areas on islands in the Caribbean. Montane ruderal forests mainly occur on sites which were formerly used for coffee production, other agriculture, agroforestry, or grazing. Some ruderal forests occur on montane landslide areas. Stands are dominated by native and exotic pioneer or secondary forest trees. The native palm Prestoea acuminata var. montana is a dominant tree species in areas formerly small clearings and in small regenerating patches of mature forest, especially on slopes. Guarea guidonia is a native tree species that was maintained for coffee shade; it has the ability to successfully regenerate in abandoned coffee shade and out-compete other species, and it has become very common. Syzygium jambos in an exotic tree which occurs in montane forests of Puerto Rico, especially in riparian areas. It appears to inhibit the regeneration of native forest species.

Diagnostic Characteristics: No Data Available

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: No Data Available

Similar NVC Types: No Data Available
note: No Data Available

Physiognomy and Structure: No Data Available

Floristics: Syzygium jambos in an exotic tree which occurs in montane forests of Puerto Rico, especially in riparian areas, but it is spreading into other montane sites. In the Luquillo Mountains of northeastern Puerto Rico, Syzygium jambos does not appear to be limited by topographic, soil nutrient, or elevational conditions (Brown et al. 2006). Guarea guidonia, Dendropanax arboreus, Coffea arabica, Inga vera, and Mangifera indica occur in areas which were formerly in coffee production (Aide et al. 2000). The native palm Prestoea acuminata var. montana is a dominant tree species in areas formerly small clearings and in small regenerating patches of mature forest, especially on slopes. Other common trees include the secondary forest species Casearia arborea, Casearia sylvestris, Psidium guajava, Inga laurina, Tabebuia heterophylla, Alchornea latifolia, and the pioneer or secondary forest species Cecropia schreberiana, Citrus x sinensis, Ochroma pyramidale, and Schefflera morototoni (Brandeis et al. 2009b, Comita et al. 2010).

Dynamics:  Hurricane disturbance tends to promote secondary forest tree species, both on sites with a history of high-intensity land use (agriculture, agroforestry or grazing), and on sites with more natural forest (Comita et al. 2010). In montane areas Coffea arabica was commonly grown with both native and exotic shade trees. Since the 1970s Coffea arabica production has declined and former Coffea arabica plantations with shade trees have become ruderal forests, dominated by the shade trees.

Guarea guidonia is a native tree species that was maintained for coffee shade along with native Inga laurina, Inga vera, and Erythrina poeppigiana. Guarea guidonia has increased in importance to become the second most important tree species in Puerto Rico; it has the ability to successfully regenerate in abandoned coffee shade and out-compete other species (Birdsey and Weaver 1982, Pascarella et al. 2000, Brandeis et al. 2007). Guarea guidonia is a native tree species which has responded to the regeneration opportunities provided by human forest management and disturbance that might have otherwise been taken by introduced species (Brandeis et al. 2009b). The importance of Guarea guidonia is a possible indication of how much the forests of Puerto Rico have been modified by former land uses, such as coffee cultivation (Brandeis et al. 2009b). Syzygium jambos has invaded riparian areas and old-growth forest stands and appears to inhibit the regeneration of native forest species. To recover native forest in areas that are dominated by Syzygium jambos, it will be necessary to reduce the abundance of this species (Aide et al. 2000).

Environmental Description:  This ruderal forest occurs in high rainfall montane and submontane areas on islands in the Caribbean. Some ruderal forests occur on montane landslide areas. Ruderal forests mainly occur on sites which were formerly used for coffee production, other agriculture, agroforestry, or grazing. Ruderal forests have higher soil bulk densities due to past soil compaction. Also there is much less leaf litter and soil organic matter than in mature native forests, but soil organic matter increases in ruderal forests over time following abandonment of agriculture or grazing (Weaver et al. 1987, Lugo and Helmer 2004).

Geographic Range: This group occurs on Caribbean islands with mountains above 600-700 m elevation and on different geologies and substrates, including Cuba, Dominican Republic, Jamaica, Puerto Rico and mountainous islands of the Lesser Antilles.

Nations: CU,DO,JM,PR,XD

States/Provinces:  No Data Available



Confidence Level: Low - Poorly Documented

Confidence Level Comments: No Data Available

Grank: GNA

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: > CasSyl/PsiGua (Brandeis et al. 2009b)
>< CecSch/CitSin (Brandeis et al. 2009b)
>< GuaGui/DenArb (Brandeis et al. 2009b)
> I.A.1.N.b. Cecropia peltata - Ochroma pyramidale Forest Alliance (Areces-Mallea et al. 1999)
>< I.A.1.N.b. Mangifera indica Forest Alliance (Areces-Mallea et al. 1999)
>< I.A.1.N.b. Syzygium jambos Forest Alliance (Areces-Mallea et al. 1999)
> I.C.1.N.b. Inga vera - Erythrina poeppigiana Forest Alliance (Areces-Mallea et al. 1999)
> Inga-coffee Forest - 75.1 (Dansereau 1966)
> Rose-apple Thicket -- 76.4 (Dansereau 1966)
>< Sierra-palm Forest - 88.1b (Dansereau 1966)
>< SyzJam (Brandeis et al. 2009b)
>< Trumpet-wood Forest - 43.1 (Dansereau 1966)

Concept Author(s): T.J. Brandeis, E. Helmer, H. Marcano Vega, and A.E. Lugo (2009b)

Author of Description: C.W. Nordman

Acknowledgements: No Data Available

Version Date: 10-11-16

  • Aide, T. M., J. K. Zimmerman, J. B. Pascarella, L. Rivera, and H. Marcano-Vega. 2000. Forest regeneration in a chronosequence of tropical abandoned pastures: Implications for restoration. Restoration Ecology 8(4):328-338.
  • Areces-Mallea, A. E., A. S. Weakley, X. Li, R. G. Sayre, J. D. Parrish, C. V. Tipton, and T. Boucher. 1999. A guide to Caribbean vegetation types: Preliminary classification system and descriptions. The Nature Conservancy, Arlington, VA. 166 pp.
  • Birdsey, R.A., and P.L. Weaver. 1982. The forest resources of Puerto Rico. USDA Forest Service, Southern Forest Experiment Station, New Orleans, LA. 56 pp.
  • Brandeis, T. J., E. H. Helmer, H. Marcano-Vega, and A. E. Lugo. 2009b. Climate shapes the novel plant communities that form after deforestation in Puerto Rico and the US Virgin Islands. Forest Ecology and Management 258(7):1704-1718.
  • Brandeis, T. J., E. H. Helmer, and S. N. Oswalt. 2007. The status of Puerto Rico''s forests, 2003. USDA Forest Service, Southern Research Station, Asheville, NC. 75 pp.
  • Brown, K. A., F. N. Scatena, and J. Gurevitch. 2006. Effects of an invasive tree on community structure and diversity in a tropical forest in Puerto Rico. Forest Ecology and Management 226:145-152.
  • Comita, L. S., J. Thompson, M. Uriarte, I. Jonckheere, C. D. Canham, and J. K. Zimmerman. 2010. Interactive effects of land use history and natural disturbance on seedling dynamics in a subtropical forest. Ecological Applications 20(5):1270-1284.
  • Dansereau, P. 1966. Studies on the vegetation of Puerto Rico. Part I. Description and integration of the plant-communities. University of Puerto Rico, Institute of Caribbean Sciences. Special Publication No. 1. Mayagüez, Puerto Rico. 287 pp.
  • Faber-Langendoen, D., J. Drake, S. Gawler, M. Hall, C. Josse, G. Kittel, S. Menard, C. Nordman, M. Pyne, M. Reid, L. Sneddon, K. Schulz, J. Teague, M. Russo, K. Snow, and P. Comer, editors. 2010-2019a. Divisions, Macrogroups and Groups for the Revised U.S. National Vegetation Classification. NatureServe, Arlington, VA. plus appendices. [in preparation]
  • Lugo, A. E., and E. Helmer. 2004. Emerging forests on abandoned land: Puerto Rico''s new forests. Forest Ecology and Management 190:145-161.
  • Pascarella, J. B., T. M. Aide, M. I. Serrano, and J. K. Zimmerman. 2000. Land-use history and forest regeneration in the Cayey Mountains, Puerto Rico. Ecosystems 3:217-228.
  • Weaver, P. L., R. A. Birdsey, and A. E. Lugo. 1987. Soil organic matter in secondary forests of Puerto Rico. Biotropica 19:17-23.