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Scientia Agricola

Print version ISSN 0103-9016

Sci. agric. (Piracicaba, Braz.) vol.69 no.1 Piracicaba Jan./Feb. 2012

http://dx.doi.org/10.1590/S0103-90162012000100009 

SOILS AND PLANT NUTRITION

 

Soil profile, relief features and their relation to structure and distribution of Brazilian Atlantic rain forest trees

 

 

Frederico Augusto Guimarães GuilhermeI, II; Tiago Osório FerreiraIII; Marco Antonio AssisV; Pablo Vidal TorradoIV; Leonor Patrícia Cerdeira MorellatoV, *

IUNESP - Programa de Pós-Graduação em Biologia Vegetal, Av. 24A, 1515 - 13506-900 - Rio Claro, SP - Brasil
IIUFG - Depto. de Ciências Biológicas - Campus Jataí, Rod. BR 364, km 192 - 75801-615 - Jataí, GO - Brasil
IIIUFC - Depto. de Ciências do Solo, Av. Mister Hull, 2977 - 60021-970 - Fortaleza, CE - Brasil
IVUSP/ESALQ - Depto. de Ciência do Solo, C.P. 09 - 13418-900 - Piracicaba, SP - Brasil
VUNESP - Instituto de Biociências, Depto. de Botânica, Laboratório de Fenologia, Av. 24A, 1515 - 13506-900 - Rio Claro, SP - Brasil

 

 


ABSTRACT

In tropical forests, the environmental heterogeneity can provide niche partitioning at local scales and determine the diversity and plant species distribution. Thus, this study aimed to investigate the variations of tree species structure and distribution in response to relief and soil profile features in a portion of the largest remnant of Brazilian Atlantic rain forest. All trees ³ 5 cm diameter at breast height were recorded in two 0.99 ha plots. Topographic survey and a soil characterization were accomplished in both plots. Topsoil samples (0-20 cm) were taken from 88 quadrats and analyzed for chemical and particle size properties. Differences for both diversity and tree density were identified among three kinds of soils. A canonical correspondence analysis (CCA) indicated that the specific abundance varied among the three kinds of soils mapped: a shallow Udept - Orthent / Aquent gradient, probably due to differences in soil drainage. Nutrient content was less likely to affect tree species composition and distribution than relief, pH, Al3+, and soil texture. Some species were randomly distributed and did not show restriction to relief and soil properties. However, preferences in niche occupation detected in this study, derived from the catenary environments found, rise up as an important explanation for the high tree species diversity in tropical forests.

Keywords: tropical rain forest, catena, tree diversity, niche partitioning, tropical soils


 

 

Introduction

Plant species diversity is greatest in tropical forests (Wright, 2002) and increases when environmental conditions vary spatially. Therefore, a higher plant species diversity found on local scales may be a consequence of a remarkable local environmental-temporal heterogeneity. Environmental heterogeneity may be the result of climate variations, moisture gradient, relief and soil profile properties (Svenning, 2001). The distribution of tree species frequently correlates with these environmental variables, and ecological niche differentiation might be important to maintain the diversity of tree species throughout the tropics (Valencia et al., 2004; Russo et al., 2005).

Oscillations on landform and slope may modify soil drainage and nutrient availability on local scales (Wright, 2002). This may interfere in the distribution and abundance of tree species in tropical forests (Clark et al., 1999; Russo et al., 2005). At short distances, the heterogeneity along an ecotone of a gallery-slope forest (also called catena) has been reported for other forests in Southeastern of Brazil (Oliveira Filho et al., 1994a; Sanchez et al., 1999; Botrel et al., 2002; Carvalho et al., 2005). Oliveira Filho and Fontes (2000), Scudeller et al. (2001) and Ferraz et al. (2004) have shown that rainfall, temperature and altitude play an important role on both distribution and abundance of the tree species from the Atlantic rain forest. However, studies of the plant species distribution and relief and edaphic properties throughout the Atlantic rain forest are scarce.

The Atlantic forest is a global biodiversity hotspot (Myers et al., 2000), highly endemic and one of the largest biodiversity centers. Only 11 to 16 % of their original area is preserved (Ribeiro et al., 2009). Its remnants are vulnerable to several kinds of human intervention and constantly threatened. This study aimed to investigate tree species distribution and abundance based in environmental heterogeneity along patches of one of the largest remnants of Atlantic rain forest, the Intervales State Park, a highly important conservation unit located on Southeastern Brazil. The Park comprises part of a steep mountainous landscape of the "Serra do Mar and "Serra de Paranapiacaba" mountain chains. We aimed to answer the following questions: (i) how does the tree community composition and structure vary in relation to landscape features and soil physical and chemical properties? and (ii) is there a niche partitioning related to a soil catena at the Atlantic rain forest?

 

Materials and Methods

The study was carried out at Intervales State Park, Saibadela Base, a 49,000-ha reserve located in São Paulo State, SE Brazil (24º14' S; 48º04' W). The local climate is humid tropical with frequent rainfall evenly distributed throughout the year with a minimum of 100 mm per month. The average annual rainfall is 4,200 mm (Morellato et al., 2000). However, between April and August there is a period of less intense and fewer frequent rains. During this period, low temperatures may occur but rarely dropping below 10°C, which contrasts with the wetter period when maximum temperatures may reach 42°C. The Park is located ca. 60 km away from the Atlantic Ocean, on the east side of the Atlantic mountain chain, in which there are various mountainous, erosive features with steep slopes and deep valleys that make up the edge of the Atlantic Crystalline Plateau. The Intervales State Park is located in the Atlantic Domain stricto sensu (Ab' Saber, 1977) with altitudes ranging from 60 to 1,100 m, including the Lowland Atlantic rain forest (< 300 m), with a 30 m-high canopy, up to the Upper Montane Atlantic rain forest (> 1,100 m), with a 15 m-high canopy.

The Saibadela Base is located between 70-250 m altitude, mostly spread over the Lowland Atlantic rain forest. The most important anthropic interference is the illegal extraction of heart of palms from Euterpe edulis palm trees. A total of 436 Angiosperm species was reported in a floristic survey at Saibadela (Zipparro et al., 2005). Considering only tree species, Guilherme et al. (2004a) surveyed 172 species among 3,078 individuals inside the same area sampled in the present study. Myrtaceae showed the greatest number of species (38) and individuals (745).

Two 0.99 ha (60 × 165 m) sampling plots of 44 contiguous quadrats (15 × 15 m) (Figure 1) were marked in the Lowland Atlantic rain forest (sensu Oliveira Filho and Fontes, 2000) and were kept at an approximate distance of 1,500 m one from the other (Guilherme et al., 2004a). The average altitude of Plot 1 was 120 m (range of 110-130 m), which was located perpendicularly and at a distance of 25 m away from the Saibadela riverbed. The Saibadela river is a ca. 15 m wide river with fast, shallow rocky water flow. Farther from the riverbed, the terrain becomes slightly steep and there is an increase on the soil drainage, except for a specific spot where there is a permanent groundwater spring at the central area of the plot. Plot 2 was located at a flatter area (86-97 m) with a bumper surface, away from watercourses and on well-drained soils. The plot configuration was adopted to evaluate the occurrence of environmental heterogeneity at short distance along an ecotone of the type gallery-slope forest (Plot 1), and to verify whether such heterogeneity exists far from watercourses (Plot 2). This heterogeneity has been reported for riparian forests within the Brazilian Central Plateau (Oliveira Filho et al., 1994a) and for the Atlantic forest along the riverbanks (Sanchez et al., 1999). All trees with a diameter at breast height > 5 cm were sampled, identified and marked with numbered aluminum tags, and had their estimated total height registered. Vouchers of botanical materials were incorporated to the HRCB Herbarium. The complete list of the 172 species reported within the sample units was reported by Guilherme et al. (2004a).

 

 

Relief variations within both sampled plots were analyzed during topographic surveys by using a measure tape and a clinometer. These data were used to generate a tridimensional representation with 1-m level curves for each plot (Figure 1). The slope variable was estimated for each of the 88 quadrats from the difference between the maximum and minimum values that had been reported at the vertices of each quadrat.

Samples for description of the soil morphology were collected at four different depths (0-20, 20-40 cm and 40-60 or 60-80 cm when possible) along those paths, inside plots, where soil color, soil texture and relief were markedly variant. Soil chemical and physical analyses (only for the 0-20 cm samples) were carried out using standard methods (EMBRAPA, 1997). Soil samples were analyzed for pH in water; extractable P, exchangeable bases [K+, Ca2+, Mg2+ and Na+] and sum of bases [SB = K+ + Na+ + Ca2+ + Mg2+]; base saturation (V%); cation exchangeable capacity (CEC); organic matter (MO), and content of sand, silt and clay. Soils were tentatively classified according to Soil Taxonomy (Soil Survey Staff, 1999, 2010) as Aquent (poorly drained soil), Orthent (shallow soil) and Udept (moderately developed soil) (Figure 1).

Topsoil variables and their slope, as well as tree density and basal area, were compared among the three kinds of soil taken in each of the 88 quadrats by using ANOVA followed by Tukey-Kramer tests for significant differences (Zar, 1996). Shannon's diversity index was calculated for each kind of soil and values were compared in pairs with Hutcheson's t test (Zar, 1996). To avoid the problem of different sampling intensities among indexes comparisons, five quadrats for the shallow and moderately developed soils (Orthent and Udept, respectively) were randomly chosen. This number corresponded to the total amount of quadrats found for the poorly drained soil (Aquent). We used χ2 tests to evaluate the distribution of the species abundance in each kind of soil. By considering that survey in contiguous quadrats do not make up independent samples, the statistical tests applied in the present study were used as a mean of highlighting differences and evidencing patterns.

The canonical correspondence analysis (CCA) was performed to determine correlations between the abundance of species and the environmental variables using PC-ORD package (McCune and Mefford, 1999). The species abundance matrix made up the number of individuals by quadrat of the species that had more than 13 individuals, and generated a matrix with 48 species (28 % of the total) and 88 quadrats. The less abundant species were eliminated when they offered little contribution to the ordination and increased the amount of calculation to be done. In a preliminary CCA, the environment matrix included all of the topsoil variables and slope (14 variables cited above). In the analysis, we eliminated self-redundant variables or those that had little correlation with the first two ordination axes (< 0.4). After that only six variables (clay, pH, V, sand, Al3+ and slope) remained. A Monte Carlo permutation test was performed to assess the significance of the correlations between the overall species abundance distributions and environmental variables. The three kinds of soil were discriminated on quadrat ordination diagrams to facilitate interpretation of emergent patterns. Pearson's correlation coefficients were calculated (Zar, 1996) in order to confirm the consistency of the distribution patterns of the species evidenced with the CCA. To normalize the frequencies distribution, environmental variables were modified by arcsin (x½), and the others were log-transformed before analyses.

 

Results

Soil atributes and slope

Three soils were identified in the studied site (Figure 1). The first was tentatively classified as an Orthent, a shallow, moderately-well drained soil with a clay-loam texture, a low base saturation (dystrophic) and a lithic contact within 50 cm depth. Six quadrats under this soil were sampled in Plot 1. This soil had a relatively high content of rock fragments and a low vulnerability to flooding, except when occasional overflow occurs, especially at lower areas near the Saibadela river. The second is a poorly drained, clay-loamy, dystrophic, and tentatively classified as an Aquent. These are very poorly drained soils that have dominantly gleyed colors close to the surface and that occur in depressions along five quadrats in Plot 1. The third and predominant soil is a clay loam to clay soil, moderately developed, moderately-well drained, shallow, low activity clay, tentatively classified as an Udept. This soil was sampled in 33 quadrats in Plot 1 and throughout Plot 2.

In general, the three soils are very acid (pH ~ 4.0), had a high value of exchangeable Al (aluminum saturation > 50 %), and low base saturation (V < 14 %) due to the low content of exchangeable K+, Ca2+ and Mg2+ evidencing a dominance of nutrient-poor soils. However, soils differed for 11 out of the 14 compared attributes (Table 1). Differences were observed mainly between the shallow and moderately developed soils, and less noticeable between the shallow and poorly drained soils. The latter had higher pH values, higher Ca2+ contents, sum of bases and sand content, as well as lower values of Al3+ and clay content when compared to moderately developed soil. Contents of exchangeable K+ and Mg2+ were higher in the shallow soil and lower in the moderately developed soil, whereas base saturation was different among the three soils, decreasing in the following order shallow - poorly drained- moderately developed. CEC was higher in the moderately developed soil and lower in the shallow one.

Tree community diversity and structure

The diversity index was higher in the moderately developed soil than in the shallow one (Table 2). These results may be related to a great species number and a higher tree density in the first than in latter kind of soil (Table 3). The shallow soil had a low value of equability and concentrated many individuals into few species, mainly Euterpe edulis, Alsophila sternbergii and Eugenia cambucarana with 68 % of the grand total of individuals (Table 4). The tree's basal area was not different for the tree kind of soils (Table 3).

 

 

 

 

CCA eigenvalues for the first two ordination axes remained below 0.5 (0.23: axis 1; 0.06: axis 2), and pointed out the existence of short gradients, i.e. most species spread over throughout the gradient. Specific accumulated variance values were low, both for axis 1 (10.7 %) and axis 2 (2.8 %), and those determined an accumulated total of 13.5 %. Although results suggests either 'noise' or non-explained remaining variance in ordination, the significance of the correlations between species and environmental variables was not affected, once CCA generated high species-environment correlation in the first two axes (0.76: axis 1; 0.73: axis 2). Moreover, the Monte Carlo permutation test suggested a significant correlation between species abundance and environmental variables with p < 0.05 for both axes. The first axis was positively correlated with pH, base saturation and sand content, and negatively correlated to clay content and Al3+ saturation (Table 5). The second CCA axis was negatively correlated to landscape slope. Variables had strong pondered correlations, and it must be highlighted the positive correlations between base saturation and pH, and between sand and pH, and negative correlations between Al3+ and pH, and between Al3+ and base saturation.

The quadrats ordination in the first axis clearly differentiated two groups (Figure 2a), and revealed a gradient between the moderately developed soil on the left and the shallow and the poorly drained soils on the right of the diagram. Correlations between variables were well defined and the gradient from left to right, showed increasing pH, base saturation and sand contents, and a decreasing Al3+ and clay contents. The soil slope was correlated with the second axis and did not show apparent connections with the kinds of soil.

The ordination suggests that most species are more abundant in the moderately developed soil (Figure 2b), whereas few species, such as Alsophila sternbergii and Eugenia cambucarana, are strictly related to the adjacent areas of the river and local depressions, as it happens at the shallow and poorly drained soil sites. Aparisthmium cordatum seemed to be associate with the soil slope in the ordination, and it was more abundant along steeper patches (r = 0.24, p < 0.05).

Some species spread under intermediate or indifferent conditions along the gradient (Figure 2b), and did not correlate with the environmental variables. From a total of 48 analyzed species, 22 (46 %) have presented significant correlations with at least one of the six variables. Clay was the variable that most strongly correlated with the first CCA, generating 12 significant correlations followed by sand and slope within each quadrat (10 each). Four out of the eight species that had an increase on the abundance with higher clay proportions had a decrease in abundance as sand contents increased. On the other hand, four out of the five species that had an increase on the number of individuals with increasing sand contents showed a decrease in abundance with higher clay contents. Five species reduced and other five increased their abundance with high declivities.

Marlierea obscura and Garcinia gardneriana (both with r = - 0.22, p < 0.05) were associated with the increase of soil acidity, whereas Eugenia bocainensis had an inverse association (r = 0.23, p < 0.05). Eugenia mosenii (r = 0.27, p < 0.05) was significantly associated with higher Al3+ concentrations. Euterpe edulis and Ixora burchelliana increased their abundance with an increase in soil acidity (r = -0.27, p < 0.05; r = -0.26, p < 0.05, respectively) and Al3+ (r = 0.29, p < 0.01; r = 0.24, p < 0.05, respectively). E. edulis was significantly less abundant at the site of the poorly drained soil (Table 4). Alsophila sternbergii, Eugenia cambucarana and Marlierea tomentosa showed a reverse association and occurred mostly at shallow and poorly drained soils. A. sternbergii (r = 0.57, p < 0.001) and E. cambucarana (r = 0.24, p < 0.05) were also more abundant at higher base saturation (shallow soil; Tables 1 and 3). Finally, Guapira opposita and G. gardneriana were less abundant at the shallow soil sites, whereas Bathysa australis and Endlicheria paniculata had a higher number of individuals at poorly drained soil sites (Table 4).

 

Discussion

The irregular relief, with steep edges at Saibadela Base, favors the occurrence of shallow soils, mainly represented by the tentatively classified Orthent and Udept. The high local rainfall (~ 4,000 mm per year) associated with such landscape conditions increase soil erosion vulnerability and also the nutrients loss by both leaching and water erosion. The water availability throughout the whole year, however, supports the existence of such exuberant vegetation on poor soils, once most of its nutrients are made available through mineralization of organic matter (Kitayama and Aiba, 2002). The occurrence of acid and nutrient-poor soils has been systematically described along the Atlantic rain forest (Leitão Filho, 1993). Well drained soils, such as the moderately developed one, are usually more strongly leached and acid than those less drained, such as the poorly drained soil and the shallow soil under study. However, the high soil acidity and Al3+ saturation were not limiting to the structural development of vegetation at well drained and moderately developed soil, as previously reported by Leitão Filho (1993).

Close to the margin of Saibadela River, the shallow soils have a coarser texture and are highly vulnerable to flooding. These soils may have been originated during the periodical deposition of sediments by the river which might also explain the differential distribution of the two species in the present study: Alsophila sternbergii, an arborescent fern which is frequently found along gallery forests at the Brazilian Central Plateau (Oliveira Filho et al., 1994b) and Eugenia cambucarana. Eugenia genus is widely spread throughout neotropical forests, but its species are frequently found in wetlands and depressions close to water courses, such as E. inundata (Ferreira and Stohlgren, 1999) and E. neomyrtifolia (Guilherme et al., 2004b). This characteristic highlights the high functional groups of plant species richness in terms of specific niche differentiation.

Other species were clearly associated with the poorly drained soil, and may have adaptative features to tolerate flooding conditions. Although reported with only one individual in the phytosociological survey due to its small size (Guilherme et al., 2004a), the shrub species Piper aduncum is very abundant on the poorly drained soil, with extensive entangled nets along such soil patches, suggesting vegetative reproduction (F.A.G. Guilherme, pers. obs.). The two arborescent ferns Cyathea phalerata and Alsophila sternbergii were also abundant on these hydromorphic soils. According to Brade (1971), A. sternbergii has stolon roots, which favor its vegetative propagation and explain its significantly clustered spatial distribution. Thus, soil drainage conditions observed in this study would favor the establishment of species with this reproductive feature. The occurrence of sprouting has been detected as an important characteristic of canopy Atlantic rain forest trees on periodic flooded soils (Negrelle, 1995) and also on other tropical forests (Paciorek et al., 2000).

Lower species richness, diversity and tree number were also found at the shallow and poorly drained soil sites. During periodical flooding, individuals should probably be adapted to the higher environmental instability caused by hypoxia (Duivenvoorden, 1996) and sediment deposition. The complex fluvial processes favor disturbances and change the tree community structure along forest patches close to water courses (Junk, 1990). Although conditions found in wetlands environments favor a lower diversity, the present study registered some exclusive species in those areas, such as Eugenia cambucarana, Cyathea phalerata and Alsophila sternbergii. This highlights a selection pressure on the niche occupation and reinforces the importance of preserving such patches to maintain the species diversity.

Plot 1 was characterized by its proximity to the Saibadela riverbed towards the well drained forest patches associated with both soil profile and relief gradients. This suggests a catenary situation with the presence of an ecotone of the type gallery-slope forest, as already detected on other tropical semi deciduous forests in Brazil (Botrel et al., 2002; Carvalho et al., 2005). Thus, landscape features are certainly associated with the three kinds of soils which are conditioning changes on physical and chemical soil properties. This also suggests a higher environmental heterogeneity when compared to Plot 2, which was exclusively dominated by the moderately developed soil. Relief variation has been considered the most important abiotic factor responsible for environmental changes and, consequently, on tree community structure of tropical forests within the Atlantic Domain at local scales (Berg and Oliveira Filho, 1999). The slightly higher number of species in Plot 1 (140) when compared to Plot 2 (134), also reported by Guilherme et al. (2004a), probably reflects an ecotonal feature between valley-back patches and well drained slopes, and suggests that more heterogeneous environments generate an increase on diversity. Previous studies in tropical forests have correlated between plant species and edaphic parameters (Clark et al., 1999; Valencia et al., 2004), emphasizing the relation of non-randomly specific distribution with environmental conditions.

The CCA ordination diagram separated the specific abundance distribution on the shallow and poorly drained soils from the moderately developed soil. The similar pattern was evidenced in an detrended correspondence analysis (DCA) performed in the same sample units, where some quadrats on the poorly drained soil and mainly on the shallow one were well delimited in relation to the quadrats on the moderately developed soil (Guilherme et al., 2004a). This reinforces the occurrence of environmental heterogeneity in Plot 1, even in contiguous survey, where chances to detect ecotones are lower.

Strong correlations with texture, soil acidity and Al3+ saturation were also found in the CCA ordination. Once soils within the Saibadela Base are nutrient poor, we suggest that the non-randomly distribution of some species occurs predominantly in terms of texture classes, pH and Al3+, possibly associated with soil drainage, whereas nutrient requisites would be a less preponderant factor over species distribution. Physical properties of soils, especially those related to soil drainage, which is affected by relief, seem to play a more important role in plant species composition than chemical properties (Sollins, 1998). Conversely, many important species in this survey showed no relation with relief and soil properties, such Euterpe edulis, Guapira opposita, Garcinia gardneriana, Psychotria suterella, Marlierea obscura, Eugenia cuprea, E. neoglomerata, E. oblongata, Calycorectes autralis and Alchornea triplinervea, which encompassed 40 % of tree density found in the survey (Guilherme et al., 2004a). Hereafter, there was a restriction by the high acidity and Al3+ saturation, which are common characteristics of tropical Lowland Forest soils. The above cited species and other 13 abundant ones are reported in a checklist of the 60 tree species more abundant and widespread along the Lowland Atlantic rain forest in Southeastern Brazil (Scudeller et al., 2001). Probably, such species have wide tolerance to various environmental conditions, which was evidenced in our study by the lack of correlation with the analyzed variables. We suggest that other non-evaluated environmental factors, such as soil micronutrients, stochastic events and possibly biological features, such as pathogen, herbivore attacks and seed dispersal ecology, are also important to explain the patterns of tree species distribution and abundance. A nonrandom spatial distribution is described for many tropical forest tree species related to edaphic features when analyzed at the landscape scale (Clark et al., 1999).

Some soil properties are related the tree species composition and structure of patches in Atlantic rain forest. Moreover, soil profile and relief features can determine preferences for niche occupation and can also rule the spatial distribution of tree species. In fact, the differential demographic distribution of tree species toward differences on soil profile and relief features has been reported in studies carried out on tropical forests (e.g. Valencia et al., 2004; Russo et al., 2005). Such environmental variations suggest that niche differentiations that emerge from catenary environments may explain the high tree species diversity throughout the old-growth tropical forests landscapes.

 

Acknowledgements

To the Instituto Florestal and Fundação Florestal for the permission to work in the Park and logistic support; to Levi Carina Terribile for help with illustrations; to FAPESP (proc. # 95/9626-0) for the financial support; to UNESP Prope funds for supporting the English version; to CNPq for the Research Productivity fellowship to F.A.G.G. and L.P.C.M.; Capes for the doctor's degree scholarship to F.A.G.G - Programa de Pós-graduação em Biologia Vegetal - UNESP Rio Claro.

 

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* Corresponding author
pmorella@rc.unesp.br

Edited by: Luís Reynaldo Ferracciú Alleoni

Received March 19, 2010 Accepted January 20, 2011