Tropical Dry Forest Structure, Distribution and Dynamics - B
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Tropical Deciduous Forests and Savannas
2/1/17 Tropical Coastal Communities Relationships to other tropical forest systems — specialized swamp forests: Tropical Coastal Forests Mangrove and beach forests § confined to tropical and & subtropical zones at the interface Tropical Deciduous Forests of terrestrial and saltwater Mangrove Forests Mangrove Forests § confined to tropical and subtropical § stilt roots - support ocean tidal zones § water temperature must exceed 75° F or 24° C in warmest month § unique adaptations to harsh Queensland, Australia environment - convergent Rhizophora mangle - red mangrove Moluccas Venezuela 1 2/1/17 Mangrove Forests Mangrove Forests § stilt roots - support § stilt roots - support § pneumatophores - erect roots for § pneumatophores - erect roots for O2 exchange O2 exchange § salt glands - excretion § salt glands - excretion § viviparous seedlings Rhizophora mangle - red mangrove Rhizophora mangle - red mangrove Xylocarpus (Meliaceae) & Rhizophora Mangrove Forests Mangrove Forests § 80 species in 30 genera (20 § 80 species in 30 genera (20 families) families) § 60 species OW& 20 NW § 60 species OW& 20 NW (Rhizophoraceae - red mangrove - Avicennia - black mangrove; inner Avicennia nitida (black mangrove, most common in Neotropics) boundary of red mangrove, better Acanthaceae) drained Rhizophora mangle - red mangrove Xylocarpus (Meliaceae) & Rhizophora 2 2/1/17 Mangrove Forests § 80 species in 30 genera (20 families) § 60 species OW& 20 NW Four mangrove families in one Neotropical mangrove community Avicennia - Rhizophora - Acanthanceae Rhizophoraceae -
North America Land Cover Characteristics Data Base Version 2.0
North America Land Cover Characteristics Data Base Version 2.0 PLEASE NOTE: This is the Version 2.0 release of the North America land cover characteristics data base. The land cover information has been updated from Version 1.2. Please read section 5.0 for information about the revision process and what changes have been made to the data. Table of Contents 1.0 Data Description ....................................................................................................................... 1 2.0 Geometric Characteristics ......................................................................................................... 2 2.1 Interrupted Goode Homolosine Projection Parameters .............................................. 2 2.2 Lambert Azimuthal Equal Area Projection Parameters ............................................... 3 3.0 Derived Data Sets ..................................................................................................................... 3 3.1 North America Seasonal Land Cover Regions Legend .............................................. 3 3.2 Global Ecosystems Legend ............................................................................................. 9 3.3 IGBP Land Cover Legend .............................................................................................. 12 3.4 USGS Land Use/Land Cover System Legend (Modified Level 2) ........................... 13 3.5 Simple Biosphere Model Legend .................................................................................. 14 3.6 -
Deciduousness in a Seasonal Tropical Forest in Western Thailand: Interannual and Intraspecific Variation in Timing, Duration and Environmental Cues
Oecologia (2008) 155:571–582 DOI 10.1007/s00442-007-0938-1 ECOSYSTEM ECOLOGY - ORIGINAL PAPER Deciduousness in a seasonal tropical forest in western Thailand: interannual and intraspecific variation in timing, duration and environmental cues Laura J. Williams Æ Sarayudh Bunyavejchewin Æ Patrick J. Baker Received: 20 February 2007 / Accepted: 3 December 2007 / Published online: 10 January 2008 Ó Springer-Verlag 2007 Abstract Seasonal tropical forests exhibit a great diver- the timing of leaf flushing varied among species, most sity of leaf exchange patterns. Within these forests variation (*70%) flushed during the dry season. Leaf flushing was in the timing and intensity of leaf exchange may occur associated with changes in photoperiod in some species and within and among individual trees and species, as well as the timing of rainfall in other species. However, more than a from year to year. Understanding what generates this third of species showed no clear association with either diversity of phenological behaviour requires a mechanistic photoperiod or rainfall, despite the considerable length and model that incorporates rate-limiting physiological condi- depth of the dataset. Further progress in resolving the tions, environmental cues, and their interactions. In this underlying internal and external mechanisms controlling study we examined long-term patterns of leaf flushing for a leaf exchange will require targeting these species for large proportion of the hundreds of tree species that co- detailed physiological and microclimatic studies. occur in a seasonal tropical forest community in western Thailand. We used the data to examine community-wide Keywords Dry season flushing Á Huai Kha Khaeng Á variation in deciduousness and tested competing hypotheses Southeast Asia Á Tropical tree phenology regarding the timing and triggers of leaf flushing in seasonal tropical forests. -
Global Change Effects on Humid Tropical Forests
PUBLICATIONS Reviews of Geophysics REVIEW ARTICLE Global change effects on humid tropical forests: Evidence 10.1002/2015RG000510 for biogeochemical and biodiversity shifts Key Points: at an ecosystem scale • Negative effects of all global change factors were found for humid tropical Daniela F. Cusack1, Jason Karpman2, Daniel Ashdown1, Qian Cao1, Mark Ciochina1, Sarah Halterman1, forest biogeochemical processes 1 1 • All global change factors except Scott Lydon , and Avishesh Neupane carbon dioxide fertilization are likely 1 2 to promote warming and/or Department of Geography, University of California, Los Angeles, California, USA, Department of Urban Planning, greenhouse gas emissions University of California, Los Angeles, California, USA • Effects of drying and deforestation are relatively clear; effects of CO2 fertilization and N deposition are Abstract Government and international agencies have highlighted the need to focus global change less certain research efforts on tropical ecosystems. However, no recent comprehensive review exists synthesizing humid tropical forest responses across global change factors, including warming, decreased precipitation, Supporting Information: carbon dioxide fertilization, nitrogen deposition, and land use/land cover changes. This paper assesses • Supporting Information S1 fi • Table S1 research across spatial and temporal scales for the tropics, including modeling, eld, and controlled laboratory studies. The review aims to (1) provide a broad understanding of how a suite of global change Correspondence to: factors are altering humid tropical forest ecosystem properties and biogeochemical processes; (2) assess D. F. Cusack, spatial variability in responses to global change factors among humid tropical regions; (3) synthesize results [email protected] from across humid tropical regions to identify emergent trends in ecosystem responses; (4) identify research and management priorities for the humid tropics in the context of global change. -
Neotropical Rainforest Restoration: Comparing Passive, Plantation and Nucleation Approaches
UC Riverside UC Riverside Previously Published Works Title Neotropical rainforest restoration: comparing passive, plantation and nucleation approaches Permalink https://escholarship.org/uc/item/4hf3v06s Journal BIODIVERSITY AND CONSERVATION, 25(11) ISSN 0960-3115 Authors Bechara, Fernando C Dickens, Sara Jo Farrer, Emily C et al. Publication Date 2016-10-01 DOI 10.1007/s10531-016-1186-7 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Biodivers Conserv DOI 10.1007/s10531-016-1186-7 REVIEW PAPER Neotropical rainforest restoration: comparing passive, plantation and nucleation approaches 1,2 2 2 Fernando C. Bechara • Sara Jo Dickens • Emily C. Farrer • 2,3 2 2,4 Loralee Larios • Erica N. Spotswood • Pierre Mariotte • Katharine N. Suding2,5 Received: 17 April 2016 / Revised: 5 June 2016 / Accepted: 25 July 2016 Ó Springer Science+Business Media Dordrecht 2016 Abstract Neotropical rainforests are global biodiversity hotspots and are challenging to restore. A core part of this challenge is the very long recovery trajectory of the system: recovery of structure can take 20–190 years, species composition 60–500 years, and reestablishment of rare/endemic species thousands of years. Passive recovery may be fraught with instances of arrested succession, disclimax or emergence of novel ecosystems. In these cases, active restoration methods are essential to speed recovery and set a desired restoration trajectory. Tree plantation is the most common active approach to reestablish a high density of native tree species and facilitate understory regeneration. While this approach may speed the successional trajectory, it may not achieve, and possibly inhibit, a long-term restoration trajectory towards the high species diversity characteristic of these forests. -
Tree Community Phenodynamics and Its Relationship with Climatic Conditions in a Lowland Tropical Rainforest
Article Tree Community Phenodynamics and Its Relationship with Climatic Conditions in a Lowland Tropical Rainforest Jakeline P. A. Pires 1, Nicholas A. C. Marino 2, Ary G. Silva 3, Pablo J. F. P. Rodrigues 4 and Leandro Freitas 4,* 1 Departamento de Biologia, Pontifícia Universidade Católica do Rio de Janeiro, Rua Marquês de São Vicente 225, Rio de Janeiro 22451-900, RJ, Brazil; [email protected] 2 Programa de Pós-Graduação em Ecologia, Universidade Federal do Rio de Janeiro (UFRJ), Rio de Janeiro CP 68020, RJ, Brazil; [email protected] 3 Programa de Pós-Graduação em Ecologia de Ecossistemas, Universidade Vila Velha, Rua Comissário José Dantas de Melo 21, Vila Velha 29102-770, ES, Brazil; [email protected] 4 Jardim Botânico do Rio de Janeiro, Rua Pacheco Leão, 915, Rio de Janeiro 22460-030, RJ, Brazil; [email protected] * Correspondence: [email protected] Received: 18 October 2017; Accepted: 25 February 2018; Published: 2 March 2018 Abstract: The timing, duration, magnitude and synchronicity of plant life cycles are fundamental aspects of community dynamics and ecosystem functioning, and information on phenodynamics is essential for accurate vegetation classification and modeling. Here, we recorded the vegetative and reproductive phenodynamics of 479 individuals belonging to 182 tree species monthly over two years in a lowland Atlantic Forest in southeastern Brazil, and assessed the relationship between local climatic conditions and the occurrence and intensity of phenophases. We found a constant but low intensity of occurrence of both leaf fall and leaf flush with respect to canopy cover, resulting in an evergreen cover throughout the year. -
Forest--Savanna Transition Zones
Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Biogeosciences Discuss., 11, 4591–4636, 2014 Open Access www.biogeosciences-discuss.net/11/4591/2014/ Biogeosciences BGD doi:10.5194/bgd-11-4591-2014 Discussions © Author(s) 2014. CC Attribution 3.0 License. 11, 4591–4636, 2014 This discussion paper is/has been under review for the journal Biogeosciences (BG). Forest–savanna Please refer to the corresponding final paper in BG if available. transition zones Structural, physiognomic and E. M. Veenendaal et al. aboveground biomass variation in Title Page savanna-forest transition zones on three Abstract Introduction continents. How different are Conclusions References co-occurring savanna and forest Tables Figures formations? J I E. M. Veenendaal1, M. Torello-Raventos2, T. R. Feldpausch3, T. F. Domingues4, J I 5 3 2,25 3,6 7 8 F. Gerard , F. Schrodt , G. Saiz , C. A. Quesada , G. Djagbletey , A. Ford , Back Close J. Kemp9, B. S. Marimon10, B. H. Marimon-Junior10, E. Lenza10, J. A. Ratter11, L. Maracahipes10, D. Sasaki12, B. Sonké13, L. Zapfack13, D. Villarroel14, Full Screen / Esc M. Schwarz15, F. Yoko Ishida6,16, M. Gilpin3, G. B. Nardoto17, K. Affum-Baffoe18, L. Arroyo14, K. Bloomfield3, G. Ceca1, H. Compaore19, K. Davies2, A. Diallo20, Printer-friendly Version N. M. Fyllas3, J. Gignoux21, F. Hien20, M. Johnson3, E. Mougin22, P. Hiernaux22, Interactive Discussion T. Killeen14,23, D. Metcalfe8, H. S. Miranda17, M. Steininger24, K. Sykora1, M. I. Bird2, J. Grace4, S. Lewis3,26, O. L. Phillips3, and J. Lloyd16,27 4591 -
Structural Dynamics of a Natural Mixed Deciduous Forest in Western Thailand
Journal of Vegetation Science 10: 777-786, 1999 © IAVS; Opulus Press Uppsala. Printed in Sweden - Structural dynamics of a natural mixed deciduous forest in Thailand - 777 Structural dynamics of a natural mixed deciduous forest in western Thailand Marod, Dokrak1,2*, Kutintara, Utis1, Yarwudhi, Chanchai1, Tanaka, Hiroshi3 & Nakashisuka, Tohru2 1Department of Forest Biology, Faculty of Forestry, Kasetsart University, Bangkok, Thailand; 2Center for Ecological Research, Kyoto University, Otsu, 520-01 Japan; 3Forestry and Forest Products Research Institute, Tsukuba 305 Japan; *Corresponding author; Center for Ecological Research, Kyoto University, Otsu, 520-01 Japan; Fax +8177549 8201; E-mail [email protected] Abstract. Structural dynamics of a natural tropical seasonal – Their ecological characteristics, structure and dynamics mixed deciduous – forest were studied over a 4-yr period at may differ largely from those of tropical rain forests Mae Klong Watershed Research Station, Kanchanaburi Prov- (Murphy & Lugo 1986; Mooney et al. 1995; Gerhardt & ince, western Thailand, with particular reference to the role of Hytteborn 1992). In addition, they have a long history of forest fires and undergrowth bamboos. All trees > 5 cm DBH disturbance from frequent fires and human activities in a permanent plot of 200 m × 200 m were censused every two years from 1992 to 1996. The forest was characterized by a (Mueller-Dombois & Goldammer 1990; Murphy & Lugo low stem density and basal area and relatively high species 1986). Despite the large areas covered and uniqueness diversity. Both the bamboo undergrowth and frequent forest of the forest, little attention has been given to this fires could be dominant factors that prevent continuous regen- diverse ecosystem compared to tropical rain forests and eration. -
Changes in Global Terrestrial Live Biomass Over the 21St Century
advances.sciencemag.org/cgi/content/full/7/27/eabe9829/DC1 Supplementary Materials for Changes in global terrestrial live biomass over the 21st century Liang Xu, Sassan S. Saatchi*, Yan Yang, Yifan Yu, Julia Pongratz, A. Anthony Bloom, Kevin Bowman, John Worden, Junjie Liu, Yi Yin, Grant Domke, Ronald E. McRoberts, Christopher Woodall, Gert-Jan Nabuurs, Sergio de-Miguel, Michael Keller, Nancy Harris, Sean Maxwell, David Schimel *Corresponding author. Email: [email protected] Published 2 July 2021, Sci. Adv. 7, eabe9829 (2021) DOI: 10.1126/sciadv.abe9829 This PDF file includes: Figs. S1 to S10 Tables S1 to S7 Supplementary Materials Supplementary Figures & Tables Fig. S1. Flow chart of procedures estimating global live biomass carbon stocks. It includes the organizations of input data forming training samples for regional and spatio-temporal models, spatially continuous annual remote sensing data sets as predictor layers, the models used, and the final output products at 10km resolution. Fig. S2. Ecoregion maps used in this study. (A) Regional land cover types by separating the biomes based on continents; (B) Combined land cover types aggregated to a total of 5 vegetation classes globally. Maps were derived from the MODIS IGBP (International Geosphere-Biosphere Programme) land cover product. We selected the data in 2001 as the base map for the inclusion of forest clearing and fire events in their original classes. Detailed description of each class can be found in Table S1. Fig. S3. Regional carbon stock series from 2000 to 2019. The land cover classes were derived from MODIS LC product (Fig. S2) and divided continentally to show regional effects. -
The Tropical Rainforest Grades K-2 and 3-5 Through the Activities Provided, Children Are Introduced to the Components of the Rainforest
Activity The Tropical Packet Rainforest Table Introduction to the Teacher Activity Packets 3 of Contents Meeting the Needs of the NYC Teacher 6 Introduction to the Rainforest 8 Concepts, Objectives and Vocabulary for Grades K - 2 10 Concepts, Objectives and Vocabulary for Grades 3 - 5 12 Pre-trip Activities: Grades K - 2 1. What is a Rainforest? 14 2. What Does a Rainforest Look Like? 16 3. What Lives in a Rainforest? 19 4. Endangered Animals of the Rainforests 22 5. Rainforest Products 30 6. Fruit from the Rainforest 33 Grades 3 - 5 7. Where are Rainforests Found? 35 8. Life in the Layers of the Rainforest 39 9. People of the Rainforest 43 10. The Costs of Extinction 47 11. How Fast is Extinction Happening? 49 12. Saving the Rainforest 53 13. Bromeliads are Products of the Rainforest 55 What to do after your trip to the Zoo 57 References for the Rainforest 59 Feedback Questionnaire 60 Funding for Activity Packets provided by: • SI Bank and Trust Community Foundation • In memory of Norbert H. Leeseberg 1 STATEN ISLAND ZOO Acknowledgements Thanks to the following people involved in the two - year development of the Teacher Guides and Student Activity Packets. These packets are a symbol of the Staten Island Zoological Society’s dedication to provide science education to the children of the New York City and surrounding area. Clay Wollney............Curriculum Writer Harry Strano III....... Director of Education, Editor Karin Jakubowski... Former Assistant Director of Education, Editor Lorraine Austin........Former Director of Education, Editor Ellen Palm...............Graphics Coordinator, Designer and Illustrator Wendy Jackelow......Illustrator We are grateful to Vincent N. -
Mesobrowser Abundance and Effects on Woody Plants in Savannas David J
551 16 Mesobrowser Abundance and Effects on Woody Plants in Savannas David J. Augustine1, Peter Frank Scogings2, and Mahesh Sankaran3,4 1 Rangeland Resources Research Unit, US Department of Agriculture – Agricultural Research Service, Fort Collins, CO, USA 2 School of Life Sciences, University of KwaZulu‐Natal, Pietermaritzburg, South Africa 3 National Centre for Biological Sciences, Tata Institute of Fundamental Research, Bangalore, Karnataka, India 4 School of Biology, Faculty of Biological Sciences, University of Leeds, Leeds, UK 16.1 Introduction Savannas, as defined in Chapter 1, are any formation with a C4 grass understory and a woody canopy layer that has not reached a closed canopy state (Ratnam et al. 2011). Climate, soils, fire, and herbivory are widely recognized as four key drivers of the structure, composition, and functioning of savanna ecosystems. The relative role of these factors, and how they interact at varying spatial and temporal scales, has been the subject of an immense body of ecological literature. Continental‐scale syntheses focused on these drivers show that climate and soils are primary determinants of woody vegetation abundance and species composition in savannas (Sankaran et al. 2008; Lehmann et al. 2014). However, at local spatial scales, fire and herbivory can regulate woody plant abundance below climatically determined maxima and alter plant growth rates, size class distributions, and community composition (e.g. Sankaran et al. 2013; Scholtz et al. 2014). Fire is well known to shape woody vegetation structure and composition in savannas worldwide (Lehmann et al. 2014), while less is known about the role of herbi- vores and the complex suite of factors that can regulate herbivore abundance and plant defenses (Chapter 15). -
Model of the Seasonal and Perennial Carbon Dynamics in Deciduous-Type Forests Controlled by Climatic Variables
Ecological Modelling, 49 (1989) 101-124 101 Elsevier Science Publishers B.V., Amsterdam - Printed in The Netherlands MODEL OF THE SEASONAL AND PERENNIAL CARBON DYNAMICS IN DECIDUOUS-TYPE FORESTS CONTROLLED BY CLIMATIC VARIABLES A. JANECEK, G. BENDEROTH, M.K.B. LUDEKE, J. KINDERMANN and G.H. KOHLMAIER lnstitut pftr Physikalische und Theoretische Chemie, Johann Wolfgang Goethe Unioersitiit Frankfurt, Niederurseler Han~ 6000 Frankfurt 50 (Federal Republic of Germany) (Accepted 24 May 1989) ABSTRACT Janacek, A., Benderoth, G., Liideke, M.K.B., Kindermann, J. and Kohlmaier, G.H., 1989. Model of the seasonal and perennial carbon dynamics in deciduous-type forests controlled by climatic variables. Ecol. Modelling, 49: 101-124. A model of the seasonal and long-term carbon dynamics of temperature deciduous forests and tropical broadleaved evergreen forests in response to variations of the climatic parame- ters light intensity and air temperature, is proposed in order to be able to assess the influence of (future) climatic change on vegetation. The driving variables operate upon carbon assimilation and respiration of a two-compartment model of living biomass. The model allocation of assimilates depends on the developmental stage of the living biomass and on the climatic variables, without prescribing the time course of the phenophases explicitly. Almost all model parameters can be interpreted in terms of measurable physiological/ecological quantities, restricting the parameter values to a limited range. Measured growth dynamics and annual CO 2 fluxes for a non-seasonal tropical forest and two different temperate deciduous forest stands are reproduced satisfactorily. 1. INTRODUCTION Global warming as a consequence of anthropogenic emissions of CO 2 and other trace gases seems almost inevitable.