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Dendrochronology and dendroclimatology of Ceiba speciosa (A. St.-Hil.) Ravenna (Malvaceae) exposed to urban pollution in Rio de Janeiro city,Brazil
Affiliation:1. Programa de Pós-graduação em Biologia Vegetal, Universidade do Estado do Rio de Janeiro, Instituto de Biologia Roberto Alcantara Gomes, Laboratório de Anatomia Vegetal, Rua São Francisco Xavier, 524 - PHLC, sala 224, 20550-013. Rio de Janeiro, RJ, Brazil;2. Universidade de São Paulo, Escola Superior de Agricultura “Luiz de Queiroz”, Departamento de Ciências Florestais, Avenida Pádua Dias, 11 - Agronomia, 13418-900, Piracicaba, SP, Brazil;3. Universidade do Estado do Rio de Janeiro, Instituto de Biologia Roberto Alcantara Gomes, Laboratório de Anatomia Vegetal, Rua São Francisco Xavier, 524 - PHLC, sala 224, 20550-013, Rio de Janeiro, RJ, Brazil;1. Khakass Technical Institute, Siberian Federal University, 27 Shchetinkina, 655017, Abakan, Russia;2. Siberian Federal University, 79 Svobodny, 660041, Krasnoyarsk, Russia;3. Sukachev Institute of Forest, Siberian Branch of the Russian Academy of Sciences, 50/28 Akademgorodok, 660036, Krasnoyarsk, Russia;1. Department of Geography and Anthropology, Louisiana State University, Baton Rouge, LA, United States;2. Department of Geography, University of Idaho, Moscow, ID, United States;3. Ecosystems Research Group, School of Biological Sciences, The University of Western Australia, Crawley, Western Australia, Australia;4. 1539 Religious Street, New Orleans, LA, United States;1. Dra Desenvolvimento e Meio Ambiente (PRODEMA/UFS), Universidade Federal de Sergipe, Av. Marechal Rondon s/n, Rosa Elze, São Cristóvão, Sergipe 49100-000, Brazil;2. Laboratorio de Dendrocronología e Historia Ambiental, IANIGLA, CCT-CONICET-Mendoza, Avda. Ruiz Leal s/n, CC 330, PO Box 5500, Mendoza, Argentina;3. Departamento de Ecologia, CCBS, Universidade Federal de Sergipe, Av. Marechal Rondon s/n, Rosa Elze, São Cristovão, Sergipe 49100-000, Brazil;4. Departamento de Biologia, CCBS, Universidade Federal de Sergipe, Av. Marechal Rondon s/n, Rosa Elze, São Cristovão, Sergipe 49100-000, Brazil;1. University of Vale do Rio dos Sinos (UNISINOS), Av. Unisinos, 950, Cristo Rei, 93022-750, São Leopoldo, RS, Brazil;2. Université de Lorraine, AgroParisTech, INRA, UMR Silva, 54000 Nancy, France;3. Coimbra University, Department of Life Sciences, Functional Ecology Center, Calçada Martim de Freitas, 3000, no 456, Coimbra, Portugal;4. University Trás-os-Montes e Alto Douro/CITAB, Forestry Department, Quinta de Prados, 5001-801, Vila Real, Portugal;5. Brazilian Agricultural Research Corporation (Embrapa), Embrapa Forestry, Estrada da Ribeira - Km 111, 83411-000, Colombo, PR, Brazil;1. Laboratório de Anatomia Vegetal, Departamento de Biologia Vegetal, Instituto de Biologia Roberto Alcantara Gomes, Universidade do Estado do Rio de Janeiro, Rua São Francisco Xavier, 524, Maracanã, 20550-900 Rio de Janeiro, RJ, Brazil;2. Empresa Brasileira de Pesquisa Agropecuária, Embrapa Florestas, Estrada da Ribeira, km 111—P.O. Box 319, 83411-000 Colombo, PR, Brazil;3. Programa de Pós-Graduação em Biologia Vegetal—UERJ, Brazil
Abstract:Nowadays, the biological monitoring through the growth rings has received increasing attention from ecologists and toxicologists. Structural analysis of these rings allows the incorporation of a time component in the study of plant responses to environmental variation. This allows also to evaluate long time series from the woody plants. In this paper, we assessed the dendrochronological characteristics of Ceiba speciosa growing in forest environment and under urbanization impact. Stem samples were obtained with Pressler probe into trees growing the campus of the Oswaldo Cruz Foundation, adjacent to one of the main urban thoroughfares of the city of Rio de Janeiro (Avenida Brasil), and at Tinguá Biological Reserve, an important remnant of Atlantic Forest. The samples were processed and analyzed following usual dendrochronological methods, with COFECHA and ARSTAN softwares. A negative exponential curve was used for standardization of the series. The residual chronologies were correlated with precipitation and temperature indexes obtained from NOAA weather database. Growth rings are distinct and annual, marked by bands of marginal parenchyma, thick-walled and radially flattened fibres in latewood and distended rays in earlywood. In both sites, the intercorrelation between the trees was above 0.40. Ages ranged from 11 to 41 years in the urban site and from 27 to 64 years in the forest site. In urban area, mean annual increment and cumulative average growth rates were 6 mm/year and 142.62 mm, respectively. At the forest site, these rates were 4 mm/year and 173.07 mm, respectively. The comparison between cumulative radial increment of the two sites revealed that trees of the urban site had higher increment rates beginning at the start of their development and consequently, they showed similar diameters despite lower ages. Correlation analysis between the chronologies and climatic factors revealed a positive association between growth and hot and rainy periods for both study sites. However, there is an immediate response of urban trees in relation to the rains and, a late response of forest trees to the same factor. The dry and hot climate, typical of urban environments, and the absence of natural water reserves in urban soil, may explain this more immediate response of urban tree growth to rainfall and temperature indexes. Our results revealed that Ceiba speciosa is a plastic and stress-tolerant species that is able to survive and adapt to polluted urban conditions. These features, along with its wide natural distribution and frequent planting for city landscaping, make this species an important biomarker for environmental monitoring studies.
Keywords:Tree rings  Wood production  Urban pollution  Environmental biomonitoring  Biomarkers  Tropical rainforest
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