Growth modeling of Carapa guianensis and Tetragastris altissima for improved management in native forests in the Amazon

Abstract In forests of the Amazon biome, Sustainable Forest Management Plans are based on technical guidelines. Such legislation provides for a cutting cycle that can vary from 25 to 35 years and a minimum cutting diameter of 50 cm. In view of the above, the present research aimed to evaluate the accuracy of regression models for the projection of growth in diameter and to calculate the t by diametric class for trees of the species C. guianensis and T. altissima. Four models with fixed effects were tested and best model was selected as the base model for the incorporation of random effects. The best fixed-effect model was Pienaar and Schiver. Thus, structures of variance and autocorrelation were added to this model to correct heteroscedasticity and autocorrelation. Finally, the time of passage for each species studied was calculated. The average annual increment in diameter estimated with the Pienaar and Schiver model with fixed effect was 0.38 cm.year−1 for C. guianensis and 0.46 cm.year−1 for T. altissima. Using the Pienaar and Schiver model with a random effect, the average annual diameter increase varied from 0.31 to 0.58 cm.year−1 for C. guianensis and from 0.37 to 0.65 mm.year−1 for T. altissima. Results showed that the estimated cutting cycle varied from 24 to 45 years for the species C. guianensis and from 21 to 38 years for the species T. altissima. Thus, using the cutting time of 25 to 35 years and a minimum cutting diameter of 50 cm for these species, can lead to incorrect decisions about the intensity of logging or the appropriate length of the cutting cycle. The growth and production models depict a synthesis of the growth dynamics of the forest, allowing to providing fundamental information for the definition of planning strategies, such as the establishment of a cutting cycle and an exploration intensity more compatible with the growth rate of the forest and for each species.

[1]  F. Bongers,et al.  Using tree-ring data to improve timber-yield projections for African wet tropical forest tree species , 2017 .

[2]  N. Subedi,et al.  Individual-tree diameter growth models for black spruce and jack pine plantations in northern Ontario , 2011 .

[3]  P. Sist,et al.  Sustainability of reduced-impact logging in the Eastern Amazon , 2007 .

[4]  P. Zuidema,et al.  Long-term growth patterns of juvenile trees from a Bolivian tropical moist forest: shifting investments in diameter growth and height growth , 2015, Journal of Tropical Ecology.

[5]  K. Paredes-Villanueva,et al.  Regional chronologies of Cedrelafissilis and Cedrela angustifolia in three forest types and their relation to climate , 2016, Trees.

[6]  David A. Ratkowsky,et al.  Problems of hypothesis testing of regressions with multiple measurements from individual sampling units , 1984 .

[7]  B. Griscom,et al.  Sustaining conservation values in selectively logged tropical forests: the attained and the attainable , 2012 .

[8]  Timothy G. Gregoire,et al.  A conspectus on Estimating Function theory and its applicability to recurrent modeling issues in forest biometry. , 1995 .

[9]  J. Carvalho,et al.  A 20-year tree liberation experiment in the Amazon: Highlights for diameter growth rates and species-specific management , 2019 .

[10]  F. Jardim,et al.  Efeito de diferentes tamanhos de clareiras, sobre o crescimento e a mortalidade de espécies arbóreas, em Moju-PA , 2007 .

[11]  P. R. Schneider,et al.  Taxa de corte sustentável para manejo das florestas tropicais , 2012 .

[12]  Incremento, ingresso e mortalidade em uma floresta de contato ombrófila aberta/estacional em Marcelândia, Estado do Mato Grosso , 2010 .

[13]  A. Ruschel,et al.  The continuous timber production over cutting cycles in the Brazilian Amazon depends on volumes of species not harvested in previous cuts , 2021 .

[14]  S. Martins,et al.  Estrutura florestal em projeto de assentamento, comunidade São Mateus, município de Placas, Pará, Brasil , 2013 .

[15]  N. Brown,et al.  Silvicultural intensification for tropical forest conservation: a response to Fredericksen and Putz , 2004, Biodiversity & Conservation.

[16]  L. Rodriguez,et al.  Non linear mixed modeling to describe the taper of clonal Eucalyptus sp. , 2014 .

[17]  C. Dormann,et al.  Recruitment, growth and recovery of commercial tree species over 30 years following logging and thinning in a tropical rain forest , 2017 .

[18]  Andrea Nogueira Dias,et al.  MODELAGEM DO INCREMENTO EM DIÂMETRO DA Araucaria angustifolia EM UMA FLORESTA OMBRÓFILA MISTA NO CENTRO-SUL DO PARANÁ , 2012 .

[19]  J. Terborgh,et al.  Hyperdominance in the Amazonian Tree Flora , 2013, Science.

[20]  José Antônio Aleixo da Silva,et al.  MODELOS VOLUMÉTRICOS MISTOS EM CLONES DE EUCALYPTUS NO POLO GESSEIRO DO ARARIPE, PERNAMBUCO , 2015 .

[21]  J. Schöngart Growth-Oriented Logging (GOL): A new concept towards sustainable forest management in Central Amazonian várzea floodplains , 2008 .

[22]  Carlos Pedro Boechat Soares,et al.  Estimation of mortality and survival of individual trees after harvesting wood using artificial neural networks in the amazon rain forest , 2018 .

[23]  W. Cropper,et al.  Multi-Model Projections for Evaluating Sustainable Timber and Seed Harvest of Carapa guianensis , 2017 .

[24]  N. Higuchi,et al.  Análise estrutural da floresta tropical úmida do município de Alta Floresta, Mato Grosso, Brasil , 2009 .

[25]  Denis Alder,et al.  An empirical cohort model for management of Terra Firme forests in the Brazilian Amazon , 2000 .

[26]  G. Mohren,et al.  Post-harvesting silvicultural treatments in logging gaps: A comparison between enrichment planting and tending of natural regeneration , 2013 .

[27]  A. Ruschel,et al.  How long does the Amazon rainforest take to grow commercially sized trees? An estimation methodology for Manilkara elata (Allemão ex Miq.) Monach , 2020 .

[28]  I. D. K. Ferraz,et al.  Sementes e plântulas de andiroba (Carapa guianensis Aubl. e Carapa procera D. C.): aspectos botânicos, ecológicos e tecnológicos , 2002 .

[29]  Carlos Pedro Boechat Soares,et al.  Individual tree growth models for eucalyptus in northern Brazil , 2014 .

[30]  César Augusto Guimarães Finger,et al.  Tree basal area increment models for Cedrela, Amburana, Copaifera and Swietenia growing in the Amazon rain forests , 2016 .

[31]  Mahadev Sharma,et al.  Height–diameter equations for boreal tree species in Ontario using a mixed-effects modeling approach , 2007 .

[32]  Karen A. Kainer,et al.  Viability of combined timber and non-timber harvests for one species: A Carapa guianensis case study , 2012 .

[33]  F. Putz,et al.  Beyond reduced-impact logging: silvicultural treatments to increase growth rates of tropical trees , 2008 .

[34]  C. P. B. Soares,et al.  Prognosis on the diameter of individual trees on the eastern region of the amazon using artificial neural networks , 2016 .

[35]  G. Schwartz,et al.  Natural regeneration of tree species in the Eastern Amazon : Short-term responses after reduced-impact logging , 2017 .

[36]  Rafael Calama,et al.  Multilevel linear mixed model for tree diameter increment in stone pine (Pinus pinea): a calibrating approach , 2005 .

[37]  R Core Team,et al.  R: A language and environment for statistical computing. , 2014 .

[38]  Julian C. Fox,et al.  Stochastic structure and individual-tree growth models , 2001 .

[39]  P. Adame,et al.  Individual-tree diameter growth model for rebollo oak (Quercus pyrenaica Willd.) coppices , 2008 .

[40]  J. D. Carvalho,et al.  Fitossociologia e uso múltiplo de espécies arbóreas em floresta manejada, comunidade Santo Antônio, município de Santarém, estado do Pará , 2012 .

[41]  I. Brown,et al.  Burning in southwestern Brazilian Amazonia, 2016-2019. , 2021, Journal of environmental management.

[42]  H. Priyadi,et al.  Reduced-impact logging in Indonesian Borneo: some results confirming the need for new silvicultural prescriptions , 2003 .