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Rev. bras. Bot. vol.34 no.3 São Paulo July/Sept. 2011
Características quantitativas do lenho em Cedrela odorata L. (Meliaceae)
Agnes E. Luchi*
Instituto de Botânica, Centro de Pesquisa em Plantas Vasculares, Núcleo de Pesquisa em Anatomia, Caixa Postal 68041, 04045-972 São Paulo, SP, Brasil
Cedrela odorata L. (Meliaceae) occurs in the Atlantic forest, Amazon rain forest, riparian forest of the country, and wetlands, which demand species adapted to their water conditions. Studies in ecological wood anatomy demonstrated that weather factors' variations have direct influence on the wood anatomical structure and that the fragmentation of the natural habitats is a direct cause of the edge effect which alters the abiotic aspects of the location, interfering consequently in its vegetation. A comparative analysis of 20 anatomical quantitative features of the wood structure was performed in populations of Cedrela odorata growing inside and on the edge of the swamp forest and granulometric analysis was made on the soil. The quantitative data were submitted to the Mann-Whitney's nonparametric test, presenting a statistically significant value decrease in the eleven wood features mean for the specimens growing in the edge of swamp forest.
Key words: edge effect, swamp forest, wood anatomy
Cedrela odorata L. (Meliaceae) ocorre na Mata Atlântica, floresta pluvial amazônica e nas matas ciliares do interior do país, em ambientes brejosos que demandam espécies adaptadas às suas condições hídricas. Estudos em anatomia ecológica do lenho têm demonstrado que a variação dos fatores climáticos atua diretamente na estrutura anatômica do lenho e que o efeito de borda causado pela fragmentação dos habitats naturais altera os aspectos abióticos e bióticos do local, interferindo na vegetação. Efetuou-se análise comparativa quantitativa de 20 características anatômicas do lenho de espécimes de Cedrela odorata do interior e da borda da mata de brejo e análise granulométrica do solo. Os dados quantitativos foram submetidos à prova não paramétrica de Mann-Whitney e demonstraram uma diminuição estatisticamente significativa nas médias dos valores de onze características dos espécimes da borda da mata de brejo.
Palavras-chave: anatomia de madeira, efeito de borda, mata de brejo
Cedrela is a neotropical genus of Meliaceae with by several species, whose principal are Cedrela odorata L., C. angustifolia Sessé & Moc. and C. fissilis Vell. (Manieri & Chimelo 1989).
In Brazil, Cedrela odorata receives many popular denominations under cedro (cedar, white cedar, odorous cedar, swamp cedar, pink cedar and red cedar) (Lorenzi 1998); outside Brazil it is known as cedar, ceder, colorado cedar, castillas cedar, dulce cedar, bitter cedar, and "redceder" (Loureiro & Silva 1968, Manieri & Chimelo 1989).
According to Richter & Dallwitz (2000) its wood presents density between 0.43-0.51/ g/cm3, classified as light and soft, being also easy to work with (Lorenzi 1992). Due the high economical value and low linear and volumetric retractability (Manieri & Chimelo 1989), its wood is widely used in civil and naval construction as well as in the manufacture of fine furniture and musical instruments. The yearly growth of highly visible layers (Dünisch et al. 2003) makes easy the age determination, rendering the species a great potential for dendrochronological studies.
Cedrela odorata is common in the Atlantic forest, the Amazonic rain forest and inside riparian forests allover tropical Brazil, not occurring in the Brazilian cerrado (savanna) (Lorenzi 1992). Outside Brazil it grows in the Mexican Pacific coast, Central America, in great part of South America, and in the Occidental India from the Greater and Lesser Antilles to Trinidad and Tobago. It was also introduced in southeastern Florida and Europe (Loureiro & Silva 1968). This wide geographic range is another attribute for its importance in dendrochronology.
In the beginning of the 20th century it was believed that C. odorata could grow in any dry land (Pereira 1914); however, the species is characteristic of wetlands (Torres et al. 1994).
The swamp forests (named 'hygrophilic forests' by Leitão Filho, 1982) have typically a smaller variety of wood species, since the constant presence of water in the soil demands specific survival adaptations, interfering in their natural selection (Leitão Filho 1982, Joly 1991, Ivanauskas et al. 1997, Toniato et al. 1998).
With the natural habitats fragmentation due to the great expansion of the agriculture and cattle-raising (Williams-Linera et al. 1998), the contact regions of the natural vegetation fragment with the anthropic area undergoes physical alterations called edge effect (Murcia 1995), that acquire greater importance with the decrease in the size of the fragments (Metzger 1999).
The edge effects can be both physical and biological (Murcia 1995). The first comprehend changes in weather factors such as solar radiation, temperature, and wind, that lead to environmental changes (Matlack 1993); the biological are related to abundance, distribution and structural alterations of the species (Fox et al. 1997). However, these effects never were analyzed through anatomical wood structure of swamp forests species, although classic studies of the ecological wood anatomy have demonstrated that the weather factors alterations be directly linked to the anatomical structure of the wood by influencing the xylogenesis (Carlquist 1975, 1980, Baas 1982), which may also be susceptible to changes in soil moisture (Luchi 2004a, 2004b, 2005).
This main goal of this study was to verify the edge effect in the quantitative anatomical characteristics of the Cedrela odorata wood by a comparative structural analysis of specimens that are growing inside the swamp forest, the typical environment for the species, with those growing on the edge of the swamps, where the environmental conditions might be altered.
Material and methods
The wood and soil samples were collected in an fragment of swamp forest inside the Reserva Biológica e Estação Experimental de Mogi-Guaçu, in Mogi-Guaçu municipality, São Paulo State, Brazil (22°15'02"-22°14'43"/ S, 47°08'50"-47°07'60"/ W). The area of about 12 ha is north-limited by Pinus plantation, in the south and east by orange farm and in the west by a paved road. The climate, is Cwa, hot humid with dry winters, with mean temperatures above 22/ °C in warmer months and above 18/ °C in the coldest ones. The mean rainfall is 250 mm in January, the wettest month, and less than 30 mm in July, the driest month, apparently with two well defined seasons (Setzer 1946, 1966).
Three specimens with similar trunks diameters were chosen from both inside and edge (orange farm) of the swamp forest and sampled by a non-destructive method (Luchi et al. 2005) at the breast height. The samples were registered and stored in the Wood Collection of the Instituto de Botânica (SPw) of Secretaria do Meio Ambiente de São Paulo (table 1).
The samples were fixed in FAA in 50% ethanol and stored in 70% ethanol. Histological sections 15 to 20 µm of thick were obtained with sliding microtome in transversal, tangential and radial longitudinal sections from the last four growth rings. The sections were stained and mounted in histological slides according to usual techniques of wood anatomy (Johansen 1940, Sass 1951). Macerations were made according to Franklin's test modified by Normand (1972), and mounted in glycerin jelly. Counting and measuring were made in Jenamed 2 microscope coupled to Retarmed 2 system in macerated tissue and in histological sections. Twenty anatomical parameters were analysed: vessels per square millimeter, vessel diameter, vessel element length, intervessel pit diameter, vessel-ray pit diameter, ray per millimeter, ray height in micrometer, ray height in number of cells, ray width in fibers in micrometer, ray width in fibers in number of cells, ray width in axial parenchyma in micrometer, ray width in axial parenchyma in number of cells, fibre length, fibre diameter, fibre lumina diameter, fibre wall thickness, axial parenchyma percentage, vessel percentage, fibre percentage and ray percentage, as recommended IAWA Committee (1989), for each characteristic in each sample (n = 30). The data set was submitted to the Mann-Whitney's non-parametric test, equal to the two averages test for independent samples, at a 5% probability level, by using BioEstat v.2.0 (Ayres et al. 2000).
Granulometric analysis were performed for the soil of both areas by the densimeter method (Camargo et al. 1986), in the Soil and Plants Nutrition Department of the Escola Superior de Agricultura Luiz de Queiroz - Universidade de São Paulo.
The border soil was also analyzed concerning the humidity at the weight basis (µ) (Reichardt 1985), collected at the depth of 0-10 cm in three standard points, near the trees from where the wood samples were collected. The collecting of soil samples happened once a month, during 12 months, always in the second fortnight of each month.
Results and discussion
Table 2 shows the areas are quite distinct as for their granulometry, the internal with a very-clay texture while the edge area presented two spots as sandy loam, a texture similar to the one observed in 'cerrado' soils (Luchi et al. 2005), which typically present a relatively low capacity for water retention (Coutinho 2009). The third edge sample stands out for presenting a lesser percentage of total sand and almost twice the percentage of clay, being classified as sandy clay loam and tending to a texture more similar to those inside the swamp, which granted it a higher percentage of soil humidity (figure 1) than spots 1 and 2, indicating that perhaps the edge effect on the soil of this swamp fragment is not so marked yet, though the edge effect be not considered a natural and continuous but a phenomenon rather abrupt and with a very quick dynamic (Bettoni et al. 2007).
The border effect defined as a structural alteration in the composition and/or relative abundance of species in the peripheral part of the fragment may be observed in the lowest heights and smaller diameters (table 1) of the edge specimens, compared to those inside the swamp. Similar data was obtained by Barros (2006) in a mountain forest fragment and by Bettoni et al. (2007) in a riparian forest fragment.
Table 3 shows the results of the Mann-Whitney's test for anatomical features and the figure 2 shows the graphic with the averages of the variables, which are significantly different from each other, for the specimens from inside the swamp and the specimens from the edge.
The vessel per square millimeter is usually lower in species that grow in more humid environments and higher in those of dry environments (Bass 1973, Barajas-Morales 1985, Lindorf 1994). However, Luchi (2004a), analyzing the anatomical characteristics of the Croton urucurana Baill. from soils with different levels of humidity, demonstrated that the higher vessel per square millimeter averages occurred in specimens from more humid and flooded areas.
Although the data relative to the soil texture grants characteristics of a dryer environment to the edge soil, the consequences of this fact were not revealed by five of the observed characteristics in the studied Cedrela odorata specimens, which presented no difference in the vessel per square millimeter averages from both areas, as well by the tissue quantification data of the axial parenchyma, vessels, fibres and rays, which also did not present variations between the inside and the edge specimens, a very important feature to be considered in dendrochronological studies.
Nevertheless, eleven characteristics showed values significantly lower for the specimens on the edge of the swamp forest: diameter and length of vessel elements, ray per millimeter, ray height in micrometer and in number of cells, ray width in fibres in micrometer and in number of cells, ray width in axial parenchyma in micrometer and in number of cells, fibres length and fibre wall thickness; some of these characteristics may be confronted figures 3-6 and 11-12.
The decrease of vessel diameter for the edge specimens coincides with the already reported for species of dryer environments (Baas et al. 1983, Baas & Carlquist 1985), where this feature represents an adaptation to hydraulic safety, since elements of lower caliber diminish the possibility of embolism in the case of a hydric stress endanger the hydric flow of the vessel. Data similar to these were obtained for Croton urucurana (Luchi 2004a).
The length of vessels element and fibres is usually bigger in specimens where the hydric availability is higher because the fusiform initials that originates these cells will present a bigger cell turgor, resulting in bigger axial elements (Levitt 1980). The Cedrela edge specimens shows statistically lower values than those from inside the swamp, reflecting therefore the lower degree of humidity in the edge soil, as verified by the granulometric analysis.
Data concerning the rays are rarely mentioned, though existing papers show the highest ray per millimeter values, both in the height and width of the rays, for specimens of more xeric ecosystems such as savannas, cerrado, caatinga (Outer & Veennendaal 1976, Chimelo & Mattos Filho 1988, Pereira 1990) or even in gallery forest (Luchi 1998) characterized for a lower hydric availability, the opposite of the found here for the edge specimens for Cedrela odorata.
Fibres with thicker walls appear frequently in dryer environments, as observed by Fahn et al. (1986) in Mediterranean and desertic species, by Alves & Angyalossy-Alfonso (2002) for Brazilian species of low humidity environments. However, although it has been statistically confirmed a thickening in the fibres walls of Croton urucurana in dryer areas (Luchi 2004a) and in Xylopia aromatica (Lam.) Mart. in cerrado (Luchi et al. 2005), opposite results had been obtained in Guarea macrophylla Vahl, Casearia sylvestris Sw. and Nectandra megapotamica (Spreng.) Mez from hydrically more favorable gallery forest (Luchi 1998), just like it was verified here for the Cedrela odorata specimens from inside the swamp.
By the other side, four characteristics are proved statistically higher for specimens from the swamp edge: the diameter of intervessel pits (figures 7-8) and vessel-ray pits (figures 9-10), the fibres diameter and the fibres lumina diameter (figures 11-12).
The intervessel pits and vessel-ray pits diameter are characteristics that are still hardly used in any approach relating the wood anatomy to the environmental variations, in spite of the important role performed by them plant transportation system (Holbrook & Zwieniecki 2005).
Luchi (1998), working in two distinct forested areas verified the highest statistically significant values for the intervessel pits diameter and the vessel-ray pits diameter in gallery forest specimens of Guarea macrophylla, characterized by a lesser hydric availability similar to that obtained here in Cedrela odorata specimens from the edge of the swamp.
Antagonistic results were already reported for environments considered mesic or with a greater availability of water, viz., bigger intervessel pit diameters in Casearia sylvestris and vessel-ray pit diameter in Psychotria carthaginensis Jacq. in specimens of one of the gallery forests (Luchi 1998), bigger intervessel pit diameters in specimens of Copaifera langsdorffii Desf. from semideciduous mesophytic forest (Marcati et al. 2001) and for intervessel pit diameter in specimens of Croton urucurana from a flooded area (Luchi 2004a) and for both kinds of pit in the wood stem of Xylopia aromatica specimens from a cerrado with a greater availability of water in the soil (Luchi et al. 2005).
The fibre diameter is another characteristic without bibliographical reference that may be related to environment just like the fibre lumina diameter.
For the fibre diameter only one result, contradictory, was obtained from literature, with the highest fibre diameter values obtained for the wood stem of Croton urucurana specimens from moist and flooded areas (Luchi 2004a). On the other hand, corroborating the data obtained for Cedrela odorata, Luchi (1989) has also verified the highest fibre lumina diameters for Guarea macrophylla and Eugenia repanda O. Berg in specimens of gallery forest statistically characterized by a lesser hydric availability.
The structural differences observed in individuals of Cedrela odorata in the edge of swamp forest were clearly related to decreased water availability, which is reflected in the xilogenesis. The lower water availability is related to structural differences found in the soil of forest edge. This, in turn, may indicate an aspect of the edge effect, where the exposed open areas lead to a change microclimatic condition (Kapos 1989). The greater penetration of sunlight, higher temperatures and evapotranspiration imply in reduction of both air and soil humidity, favoring thus the occurrence of water stress.
ALVES, E.S. & ANGYALOSSY-ALFONSO, V. 2002. Ecological trends in the wood anatomy of some Brazilian species. 2. Axial parenchyma, rays and fibres. IAWA Journal 23:391-418. [ Links ]
AYRES, M., AYRES JR. M., AYRES, D.L. & SANTOS, A.S. 2000. BioEstat 2.0: Aplicações estatísticas nas áreas das ciências biológicas e médicas. Sociedade Civil Mamirauá, Belém. [ Links ]
BAAS, P. 1973. The wood anatomical range in Ilex (Aquifoliaceae) and its ecological and phylogenetic significance. Blumea 21:193- 258. [ Links ]
BAAS, P. 1982. Systematic, phylogenetic and ecological wood anatomy - History and perspectives. In New perspectives in wood anatomy (P. Baas, ed.). Martinus Nyhoff Publishers, The Hague, p.23-58. [ Links ]
BAAS, P. & CARLQUIST, S. 1985. A comparison of the ecological wood anatomy of the floras of Southern California and Israel. IAWA Bulletin new series 6:349-353. [ Links ]
BAAS, P., WERKER, E.E. & FAHN, A. 1983. Some ecological trends in vessel characters. IAWA Bulletin new series 4:141-159. [ Links ]
BARAJA-MORALES, J. 1985. Wood structural differences between trees of two tropical forests in Mexico. IAWA Bulletin new series 6:355-364. [ Links ]
BARROS, F.A. 2006. Efeito de borda em fragmentos de floresta Montana, Nova Friburgo - RJ. Dissertação de mestrado, em Ciências Ambientais da Universidade Fluninense, Niteroi. [ Links ]
BETTONI, S.G., NAGY, M.B, BERTOLDI, E.R.M. & FLYNN, M.N. 2007. Efeito de borda em fragmento de mata ciliar, microbacia do Rio do Peixe, Socorro, SP. In Anais do VIII Congresso de Ecologia do Brasil, Caxambu, p.1-2. [ Links ]
CAMARGO, O.A., MONIZ, O.A.A.C., JORGE, J.A. & VALADARES, J.M.A.S. 1986. Métodos de análise química e física de solos do Instituto Agronômico de Campinas. Instituto Agronômico de Campinas,Campinas. [ Links ]
CARLQUIST, S. 1975. Ecological strategies in xylem evolution. University of California Press, Berkeley. [ Links ]
CARLQUIST, S. 1980. Further concepts in ecological wood anatomy, with comments on recent work in wood anatomy and evolution. Aliso 9:499-553. [ Links ]
CHIMELO, J.P. & MATTOS FILHO, A. 1988. Preliminary wood structure observations of five hardwood species from different sites in Brazil. In Anais of 5th Conference of International Union of Forestry Research Organization - IUFRO, São Paulo, v.II, p.100. [ Links ]
DÜNISCH, O., MONTÓIA, R.V. & BAUCH, J. 2003. Dendroecological investigations on Switenia macrophylla King and Cedrela odorata L. (Meliaceae) in the central Amazon. Trees 17:244-250. [ Links ]
FAHN, A., WERKER, E. & BAAS, P. 1986.Wood anatomy and identification of trees and shrubs from Israel and adjacent regions. The Israel Academy of Sciences and Humanities, Jerusalem. [ Links ]
FOX, B.J., TAYLOR, J.E., FOX, M.D. & WILLIAMS, C. 1997. Vegetation changes across edges of rainforest remnants. Biological Conservation 82:1-13. [ Links ]
HOLBROOK, N.M. & ZWIENIECKI, M.A. 2005. Vascular transport in plants, 1st ed. Elsevier, Academic Press, Amsterdam. [ Links ]
IVANAUSKAS, N.M., RODRIGUES, R.R. & NAVE, A.G. 1997. Aspectos ecológicos de um trecho de brejo em Itatinga, SP: florística, fitossociologia e seletividade de espécies. Revista Brasileira de Botânica 20:139-153. [ Links ]
JOHANSEN, D.A. 1940. Plant microtechnique. McGraw-Hill Book Company, Inc., New York. [ Links ]
JOLY, C.A. 1991. Flooding tolerance in tropical trees. In Plant life under oxigen deprivation (M.B. Jackson, D.D. Davies & H. Lambers, eds.). Academic Publishing, The Hague, p.23-34. [ Links ]
KAPOS, V. 1989. Effects of isolation on the water status of forest patches in the Brazilian Amazon. Journal of Tropical Ecology 5:173-185. [ Links ]
LEITÃO FILHO, H.F. 1982. Aspectos taxonômicos das florestas do estado de São Paulo. In: Congresso Nacional sobre essências nativas, Campos de Jordão, 1982. Anais... Silvicultura em São Paulo 16A:197-206. [ Links ]
LEVITT, J. 1980. Responses of plants to environmental stress. V. I - Chilling, freezing and high temperature stresses. Physiological Ecology. Academic Press, New York. [ Links ]
LINDORF, H. 1994. Eco-anatomical wood features of species from a very tropical Forest. IAWA Journal 15:361-376. [ Links ]
LORENZI, H. 1998. Árvores Brasileiras. Manual de identificação e cultivo de plantas arbóreas nativas do Brasil. Editora Plantarum Ltda., Nova Odessa, v.2. [ Links ]
LOUREIRO, A.A. & SILVA, M.F. 1968. Catálogo das madeiras da Amazônia. Ministério do Interior Superintendência do desenvolvimento da Amazônia, Belém. [ Links ]
LUCHI, A.E. 1998. Periodicidade de crescimento em Hymenaea courbaril L. e anatomia ecológica do lenho de espécies de mata ciliar. Tese de doutorado, Universidade de São Paulo, São Paulo. [ Links ]
LUCHI, A.E. 2004a. Anatomia do lenho de Croton urucurana Baill. (Euphorbiaceae) de solos com diferentes níveis de umidade. Revista Brasileira de Botânica 27:271-280. [ Links ]
LUCHI, A.E. 2004b. Anatomia do lenho de raiz de Croton urucurana Baill. (Euphorbiaceae) de solos com diferentes níveis de umidade. Hoehnea 31:243-250. [ Links ]
Luchi, A.E., PEREIRA SILVA, l.c. & mORAES, m.a. 2005. Anatomia comparada do lenho de Xylopia aromatica (Lam.) Mart. em áreas de cerrado e de plantação de Pinus elliottii Engelm. Revista Brasileira de Botânica 28:809-820. [ Links ]
MAINIERI, C. & CHIMELO, J.P. 1989. Fichas de características das madeiras brasileiras. Instituto de Pesquisas Tecnológicas, São Paulo. [ Links ]
MARCATI, C.R., ANGYALOSSY-ALFONSO, V. & BENETATI, L. 2001. Anatomia comparada do lenho de Copaifera langsdorffii Desf. (Leguminosae-Caesalpinoideae) de floresta e cerradão. Revista Brasileira de Botânica 24:311-320. [ Links ]
MATLACK, G.R. 1993. Microenvironment variation within and among forest edge sites in te eastern United States. Biological Conservation 66:185-194. [ Links ]
METZGER, J.P. 1999. Estrutura da paisagem e fragmentação: análise bibliográfica. Anais da Academia Brasileira de Ciências 71:445-463. [ Links ]
MURCIA, C. 1995. Edge effects in fragmented forest: implications for conservation. Trends in Ecology and Evolution 10:58-62. [ Links ]
NORNAND, D. 1972. Manuel d'identification dês bois comerciaux. Centre Technique Forestier Tropical, Nogent-sur-Marne. [ Links ]
OUTER, R.W. & VEENENDAAL, W.L.H.1976. Variation in wood anatomy of species with a distribution covering both rain forest and savanna areas of the Ivory Coast, West-Africa. In: Wood structure in biological and technological research (P. Baas, A.J. Bolton & D.M. Catling, eds.). Leiden Botanical Series n.3. Leiden University Press, Leiden, p.182-195. [ Links ]
PEREIRA, B.A.S. 1990. Estudo morfo-anatômico da madeira, casca e folhas de duas variedades vicariantes de Sclerolobium paniculatum Vogel (Leguminosae, Caesalpinioideae) de mata e cerrado. Dissertação de mestrado, Escola Superior de Agricultura Luiz de Queiroz, Piracicaba. [ Links ]
PEREIRA, H. 1914. Apontamentos sobre as madeiras do estado de São Paulo. Casa Espindola, São Paulo. [ Links ]
REICHARDT, K. 1985. Processos de transferência no Sistema-Solo-Planta-Atmosfera. 4ª ed., Fundação Cargill, Campinas. [ Links ]
RICHTER, H.G. & DALLWITZ, M.J. (2000 onwards). Commercial timbers: descriptions, illustrations, identification and information retrieval. In English, French, German and Spanish. Version: 4thMay 2000. http://biodiversity.uno.edu/delta/ (acesso em 16/10/2009). [ Links ]
SASS, J.E. 1951. Botanical microtechnique. The Iowa State College Press, Ames. [ Links ]
SETZER, J. 1949. Os solos do Estado de São Paulo. Biblioteca Geográfica Brasileira, série A, publicação n.6, Instituto Brasileiro de Geografia e Estatística - IBGE, Rio de Janeiro. [ Links ]
SETZER, J. 1966. Atlas climático e ecológico do Estado de São Paulo. Comissão Interestadual da Bacia Paraná-Uruguai e Centrais Elétricas de São Paulo, São Paulo. [ Links ]
TONIATO, M.T.Z., Leitão FILHO, H.F. & RODRIGUES, R.R. 1998. Fitossociologia de uma remanescente de floresta higrófila (mata de brejo) em Campinas, SP. Revista Brasileira de Botânica 21:197-210. [ Links ]
TORRES, R.B., MATTHES, L.A.F. & RODRIGUES, R.R. 1994. Florística e estrutura do componente arbóreo de mata de brejo em Campinas, SP. Revista Brasileira de Botânica 17:189-194. [ Links ]
WILLIAMS-LINERE, G., DOMÍNGUEZ-GASTELÚ, V. & GARCÍA-ZURITA, M.E. 1998. Microenvironment and floristic of different edges in a fragmented tropical rainforest. Conservation Biology 12:1091-1102 [ Links ]
(received: July 22, 2010; accepted: August 9, 2011)