Structure, function and floristic relationships of plant communities in stressful habitats marginal to the Brazilian Atlantic rainforest.

The Brazilian Atlantic rainforest consists of a typical tropical rainforest on mountain slopes, and stands out as a biodiversity hotspot for its high species richness and high level of species endemism. This forest is bordered by plant communities with lower species diversity, due mostly to more extreme environmental conditions than those found in the mesic rainforest. Between the mountain slopes and the sea, the coastal plains have swamp forests, dry semi-deciduous forests and open thicket vegetation on marine sand deposits. At the other extreme, on top of the mountains (>2000 m a.s.l.), the rainforest is substituted by high altitude fields and open thicket vegetation on rocky outcrops. Thus, the plant communities that are marginal to the rainforest are subjected either to flooding, drought, oceanicity or cold winter temperatures. It was found that positive interactions among plants play an important role in the structuring and functioning of a swamp forest, a coastal sandy vegetation and a cold, high altitude vegetation in the state of Rio de Janeiro. Moreover, only a few species seem to adopt this positive role and, therefore, the functioning of these entire systems may rely on them. Curiously, these nurse plants are often epiphytes in the rainforest, and at the study sites are typically terrestrial. Many exhibit crassulacean acid metabolism. Conservation initiatives must treat the Atlantic coastal vegetation as a complex rather than a rainforest alone.

[1]  C. Holzapfel,et al.  BIDIRECTIONAL FACILITATION AND INTERFERENCE BETWEEN SHRUBS AND ANNUALS IN THE MOJAVE DESERT , 1999 .

[2]  W. Powell,et al.  High genetic differentiation among remnant populations of the endangered Caesalpinia echinata Lam. (Leguminosae–Caesalpinioideae) , 1998 .

[3]  F. Scarano,et al.  ANATOMICAL FEATURES OF GROWTH RINGS IN FLOOD-PRONE TREES OF THE ATLANTIC RAIN FOREST IN RIO DE JANEIRO, BRAZIL , 2001 .

[4]  M. Liebig,et al.  Ecophysiological and floristic implications of sex expression in the dioecious neotropical CAM tree Clusia hilariana Schltdl. , 2001, Trees.

[5]  R. Hampp,et al.  The Genus Clusia L.: Molecular Evidence for Independent Evolution of Photosynthetic Flexibility , 2002 .

[6]  G. Fonseca The vanishing Brazilian Atlantic forest , 1985 .

[7]  D. Young,et al.  Spatial and temporal growth dynamics of Barrier Island shrub thickets , 1995 .

[8]  E. Maarel Dry coastal ecosystems : Africa, America, Asia and Oceania , 1993 .

[9]  J. Brulfert,et al.  Four sites with contrasting environmental stress in southeastern Brazil: relations of species, life form diversity, and geographic distribution to ecophysiological parameters , 2001 .

[10]  S. Davis,et al.  Centres of plant diversity : a guide and strategy for their conservation , 1996 .

[11]  F. Fernandez,et al.  Use of space by the marsupial Micoureus demerarae in small Atlantic Forest fragments in south-eastern Brazil , 1999, Journal of Tropical Ecology.

[12]  P. Nobel,et al.  Effect of Nurse Plants on the Microhabitat and Growth of Cacti , 1989 .

[13]  F. Scarano,et al.  Leaf anatomical variation in Alchornea triplinervia (Spreng) Müll. Arg. (Euphorbiaceae) under distinct light and soil water regimes , 2001 .

[14]  Araújo Ds,et al.  Análise florística e fitogeográfica das restingas do estado do Rio de Janeiro , 2000 .

[15]  T. Wendt,et al.  Selfing facilitates reproductive isolation among three sympatric species of Pitcairnia (Bromeliaceae) , 2002, Plant Systematics and Evolution.

[16]  W. Barthlott,et al.  Diversity and ecology of saxicolous vegetation mats on inselbergs in the Brazilian Atlantic rainforest , 1998 .

[17]  C. Pittendrigh THE BROMELIAD–ANOPHELES–MALARIA COMPLEX IN TRINIDAD. I–THE BROMELIAD FLORA , , 1948 .

[18]  C. Joly,et al.  The vegetation of granite rock outcrops in Rio de Janeiro, Brazil, and the need for its protection , 1999, Environmental Conservation.

[19]  F. Scarano,et al.  Plant establishment on flooded and unflooded patches of a freshwater swamp forest in southeastern Brazil , 1997, Journal of Tropical Ecology.

[20]  H. Safford Brazilian Páramos II. Macro‐ and mesoclimate of the campos de altitude and affinities with high mountain climates of the tropical Andes and Costa Rica , 1999 .

[21]  Ary T. Oliveira-Filho,et al.  Patterns of Floristic Differentiation among Atlantic Forests in Southeastern Brazil and the Influence of Climate1 , 2000 .

[22]  A. Gentry,et al.  Neotropical Floristic Diversity: Phytogeographical Connections Between Central and South America, Pleistocene Climatic Fluctuations, or an Accident of the Andean Orogeny? , 1982 .

[23]  U. Lüttge,et al.  Habitat segregation of C3 and CAM Nidularium (Bromeliaceae) in response to different light regimes in the understory of a swamp forest in southeastern Brazil , 1999 .

[24]  M. Ledru,et al.  Vegetation dynamics in southern and central Brazil during the last 10 , 1998 .

[25]  T. Wendt,et al.  Reproductive biology and natural hybridization between two endemic species of Pitcairnia (Bromeliaceae). , 2001, American journal of botany.

[26]  H. Behling Late Quaternary vegetational and climatic changes in Brazil , 1998 .

[27]  L. Martin,et al.  As flutuações de nível do mar durante o quaternário superior e a evolução geológica de "deltas" brasileiros , 1993 .

[28]  R. Mittermeier,et al.  Biodiversity hotspots for conservation priorities , 2000, Nature.

[29]  E. Medina DARK CO2 FIXATION, HABITAT PREFERENCE AND EVOLUTION WITHIN THE BROMELIACEAE , 1974, Evolution; international journal of organic evolution.

[30]  J. M. Wilson,et al.  Gradation in Nutrient Composition and Photosynthetic Pathways Across the Restinga Vegetation of Brazil , 1997 .

[31]  Christopher J. Schneider,et al.  Biodiversity hotspots and beyond: the need for preserving environmental transitions , 2001 .

[32]  F. Scarano,et al.  Periodicity of growth rings in some flood-prone trees of the Atlantic Rain Forest in Rio de Janeiro, Brazil , 2001, Trees.

[33]  U. Lüttge,et al.  Comparative study of the C3/CAM-intermediate species Clusia parviflora Saldanha et Engl. and the obligate CAM-species Clusia hilariana Schlecht.growing sympatrically exposed and shaded in the coastal restinga of Brazil , 1999 .

[34]  U. Lüttge One Morphotype, Three Physiotypes: Sympatric Species of Clusia with Obligate C3 Photosynthesis, Obligate CAM and C3-CAM Intermediate Behaviour , 1999 .

[35]  J. A. Ratter,et al.  A study of the origin of central Brazilian forests by the analysis of plant species distribution patterns , 1995 .

[36]  C. Pittendrigh The bromeliad-Anopheles-malaria complex in Trinidad; the bromeliad flora. , 1948, Evolution; international journal of organic evolution.

[37]  B. Groombridge Global biodiversity: status of the earth's living resources. , 1992 .

[38]  H. Safford Brazilian Páramos. I. An introduction to the physical environment and vegetation of the campos de altitude , 1999 .

[39]  F. Scarano,et al.  Resprouting and growth dynamics after fire of the clonal shrub Andira legalis (Leguminosae) in a sandy coastal plain in south‐eastern Brazil , 2001 .

[40]  F. Scarano,et al.  HABITAT CHOICE IN TWO FACULTATIVE EPIPHYTES OF THE GENUS NIDULARIUM (BROMELIACEAE) , 1998 .

[41]  R. Crawford,et al.  Studies in Plant Survival. , 1989 .

[42]  F. Fernandez,et al.  Frequency of movements of small mammals among Atlantic Coastal Forest fragments in Brazil , 2002 .

[43]  L. Morellato,et al.  Introduction: The Brazilian Atlantic Forest1 , 2000 .