Pioneer Species and Climax Species

Total Page:16

File Type:pdf, Size:1020Kb

Pioneer Species and Climax Species Epilogue Pioneer Species and Climax Species The society tends to define scientific research as individual activities. Credits of theories go to individual authors. Patents are awarded to specific individuals and companies. But most scientific progresses and regresses are determined by the social environment. A look at interactions of different species in nature will help us understand academic and social dynamics. Biologists often classify species into pioneer species and climax species. Pioneer species, like alders and clovers, love the sunshine, and both fix nitrogen, an energy intensive process. As they absorb solar energy to generate nutrients for themselves, they enrich the soil around them. In newly disturbed lands with poor soil content, pioneer species flourish. As pioneer species toil away, the soil they inhabit becomes fertile and rich. Over time, climax species gradually move in. Climax species, like lawn grasses and spruces, require nutritious soil. But they require less solar energy to generate nutrients themselves. So they can tolerate shade. As a forest becomes dense, new plants have to stay in the shade for a long time, waiting for old trees to retire. Pioneer species, which need an abundance of sunshine to generate nutrients, could not wait long. Gradually, climax species take over the landscape. Pioneer species are forced to look for new places to survive. This is why pioneer species are also called refugee species by biologists. On islands in northern region, poplars, a type of pioneer species, grow on the edge. Spruces grow at the core of the islands. The locations of poplars and spruces form a distinct image of periphery and core relation between pioneer and climax species. We love climax species and often detest pioneer species. Fertilizers, which often contain herbicides to kill pioneer species, are applied lavishly on green lawns. Forestry industries encourage the growth of climax species, like spruces, and suppress the growth of pioneer species, like alders. But why? Firstly, an abundance of climax species clearly signals the richness of the land and of the landowner. While pioneer species improve soil quality, they also indicate that the land needs to be improved, which is a sore embarrassment to proud land owners. Secondly, pioneer species do not make high quality products. Because their priority is to generate nutrients, they dedicate less energy to their immune systems. © Springer Science+Business Media New York 2016 125 J. Chen, The Unity of Science and Economics, DOI 10.1007/978-1-4939-3466-9 126 Epilogue: Pioneer Species and Climax Species This vulnerability leads to frequent invasion by other organisms, which lead to unsightly scars on their bodies. Hence, alders are deemed low quality timbers. In their openness and inability to defend themselves, pioneers are more likely to accept different genes and ideas from distant species and camps. This allows pio- neers to adapt, innovate and initiate major changes. In times of poverty and turmoil, pioneers are often enlisted to help. In poor areas, farmers who cannot afford chemical fertilizers rotate the growing season of crops and clover, which is a pioneer species that enrich the soil. During the Second World War, the British government found that Alan Turing, a pioneer in understanding how the mind works, can help decoding enemy messages. But after the war, the British government found Alan Turing himself needed help. Turing rejected gov- ernment’s help and killed himself. As a landscape matures, climax species become dominant and biodiversity declines. The progress of a system is often marked by the dominance of climax species over pioneer species. In modern societies, many medical and public health measures, such as sterilization and antibiotics, aim at eliminating microbes, which are often pioneer species. The short term benefits of these measures are very sig- nificant. But long term harms of many of these measures are gradually being recognized. Nowadays, doctors are less eager to prescribe antibiotics to patients. Over-sterilization deprives us from encountering stimulations that aid us in developing strong immune systems. As the environment becomes sterile, our bodies and minds follow suit. The social groups that demand highly sterile natural and social environments often suffer from below-replacement fertility rates, rendering themselves biologically sterile. If academic and social institutions continue to sterilize the social environment, the aging society will progress into a dying society, a pattern that has occurred consistently in the history of human societies. More than ten years ago, Galbraith (2000) discussed the social environment of the economist profession and the prospect of a theoretical revolution. He wrote: Leading active members of today’s economics profession …… have joined together into a kind of politburo for correct economic thinking. As a general rule–as one might expect from a gentleman’s club–this has placed them on the wrong side of every important policy issue, and not just recently but for decades. …… And when finally they sense that some position cannot be sustained, they do not re-examine their ideas. Instead, they simply change the subject. No one loses face, in this club, for having been wrong. No one is disinvited from presenting papers at later annual meetings. And still less is anyone from the outside invited in. …… The reduction of many of today’s leading economists to footnote status is overdue. But would those economists recognize a theoretical revolution if one were to occur? One is entitled to doubt it. Being right doesn’t count for much in this club. For a theoretical revolution to occur and to flourish, it depends on the efforts of many people. Bibliography Ainslie, G. (1992). Picoeconomics: The interaction of successive motivational states within the person. Cambridge: Cambridge University Press. Ainslie, G., & Herrnstein, R. (1981). Preference reversal and delayed reinforcement. Animal Learning and Behavior, 9, 476–482. Akerlof, G. (1970). The market for ‘Lemons’: Quality uncertainty and the market mechanism. Quarterly Journal of Economics, 84, 488–500. Aleksandrovich, K. V., & Viktorovich, G. A. (2014). Connection of subjective entropy maximum principle to the main laws of psych. Science and Education, 2(3), 59–65. Anderson, P. (2000). Cues of culture: The basis of intercultural differences in nonverbal communication. In Larry Samovar & Richard Porter (Eds.), Intercultural communication; A reader. Belmont, CA: Wadsworth Pub. Co. Annila, A. (2009). Economies evolve by energy dispersal. Entropy, 11, 606–633. Aoki, M., & Yoshikawa, H. (2006). Reconstructing macroeconomics: A perspective from statistical physics and combinatorial stochastic. Cambridge: Cambridge University Press. Applebaum, D. (1996). Probability and information, an integrated approach. Cambridge: Cambridge University Press. Arnott, R., & Casscells, A. (2003). Demographics and capital market returns. Financial Analysts Journal, 59(2), 20–29. Arrow, K. J. (1973). Information and economic behavior (No. TR-14). CAMBRIDGE MASS: HARVARD UNIV. Arrow, K. (1999). Information and the organization of industry. In G. Chichilnisky (Ed.), Markets, information, and uncertainty. Cambridge: Cambridge University Press. Atkins, P. (1991). Atoms, electrons, and Change. New York: Scientific American Library, A division of HPHLP. Atkins, P. (1997). The periodic kingdom: A journey into the land of the chemical elements. New York: Basic Books. Ayres, R., van den Bergh, J., Lindenberger, D., & Warr, B. (2013). The underestimated contribution of energy to economic growth. Structural Change and Economic Dynamics, 27, 79–88. Baierlein, R. (1999). Thermal physics. Cambridge: Cambridge University Press. Baran, P., & Sweezy, P. (1966). Monopoly capital. New York: Monthly Review Press. Barber, B. M., & Odean, T. (2000). Trading is hazardous to your wealth: The common stock investment performance of individual investors. The Journal of Finance, 55(2), 773–806. Barber, B., & Odean, T. (2008). All that glitters: The effect of attention and news on the buying behavior of individual and institutional investors. The Review of Financial Studies, 21(2), 785– 818. Barber, B. M., Odean, T., & Zhu, N. (2009). Do retail trades move markets? Review of Financial Studies, 22(1), 151–186. © Springer Science+Business Media New York 2016 127 J. Chen, The Unity of Science and Economics, DOI 10.1007/978-1-4939-3466-9 128 Bibliography Barber, B. M., Odean, T., & Zhu, N. (2009). Systematic noise. Journal of Financial Markets, 12(4), 547–569. Barkow, J., Cosmides, L., & Tooby, J. (Eds.). (1992). The adapted mind: Evolutionary psychology and the generation of culture. Oxford & New York: Oxford University Press. Banerjee, S., & Kremer, I. (2010). Disagreement and learning: Dynamic patterns of trade. The Journal of Finance, 65(4), 1269–1302. Beck, K., & Andres, C. (2002). Extreme programming explained: Embrace change (2nd ed.). Boston: Addison-Wesley. Beerling, D. (2007). The emerald planet: How plants changed Earth’s history. Oxford: Oxford University Press. Bennett, C. (1988). Notes on the history of reversible computation. IBM Journal of Research and Development, 32,16–23. Bernoulli, D. (1738(1954)). Exposition of a new theory on the measurement of risk. Econometrica, 22(1), 23–36. Berns, G., Laibson, D., & Loewenstein, G. (2007). Intertemporal choice—toward an integrative framework. Trends in Cognitive Science, 11, 482–488. Beutelspacher, A. (1994). Cryptology: An introduction to the art
Recommended publications
  • Fire and Nonnative Invasive Plants September 2008 Zouhar, Kristin; Smith, Jane Kapler; Sutherland, Steve; Brooks, Matthew L
    United States Department of Agriculture Wildland Fire in Forest Service Rocky Mountain Research Station Ecosystems General Technical Report RMRS-GTR-42- volume 6 Fire and Nonnative Invasive Plants September 2008 Zouhar, Kristin; Smith, Jane Kapler; Sutherland, Steve; Brooks, Matthew L. 2008. Wildland fire in ecosystems: fire and nonnative invasive plants. Gen. Tech. Rep. RMRS-GTR-42-vol. 6. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 355 p. Abstract—This state-of-knowledge review of information on relationships between wildland fire and nonnative invasive plants can assist fire managers and other land managers concerned with prevention, detection, and eradi- cation or control of nonnative invasive plants. The 16 chapters in this volume synthesize ecological and botanical principles regarding relationships between wildland fire and nonnative invasive plants, identify the nonnative invasive species currently of greatest concern in major bioregions of the United States, and describe emerging fire-invasive issues in each bioregion and throughout the nation. This volume can help increase understanding of plant invasions and fire and can be used in fire management and ecosystem-based management planning. The volume’s first part summarizes fundamental concepts regarding fire effects on invasions by nonnative plants, effects of plant invasions on fuels and fire regimes, and use of fire to control plant invasions. The second part identifies the nonnative invasive species of greatest concern and synthesizes information on the three topics covered in part one for nonnative inva- sives in seven major bioregions of the United States: Northeast, Southeast, Central, Interior West, Southwest Coastal, Northwest Coastal (including Alaska), and Hawaiian Islands.
    [Show full text]
  • Potential Vegetation, Disturbance, Plant Succession, and Other Aspects of Forest Ecology
    United States Department of Agriculture Forest Service Potential Vegetation, Disturbance, Pacific Northwest Plant Succession, and Other Aspects of Region Umatilla National Forest Ecology Forest F14-SO-TP-09-00 May 2000 David C. Powell The Forest Service of the U.S. Department of Agriculture is dedicated to the principle of multiple use management of the Nation’s forest resources for sustained yields of wood, water, forage, wildlife, and recreation. Through forestry research, cooperation with the States and private forest owners, and man- agement of the national forests and national grasslands, it strives – as directed by Congress – to provide increasingly greater service to a growing nation. The U.S. Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, gender, religion, age, disability, political beliefs, sexual orienta- tion, and marital or family status. (Not all prohibited bases apply to all programs.) Persons with disabili- ties who require alternative means for communication of program information (Braille, large print, audio- tape, etc.) should contact USDA’s TARGET Center at 202-720-2600 (voice and TDD). To file a complaint of discrimination, write USDA, Director, Office of Civil Rights, Room 326-W, Whitten Building, 14th and Independence Avenue, SW, Washington, DC 20250-9410 or call (202) 720- 5964 (voice or TDD). USDA is an equal opportunity provider and employer. ii Potential Vegetation, Disturbance, Plant Succession, and Other Aspects of Forest Ecology David C. Powell U.S. Department of Agriculture, Forest Service Pacific Northwest Region Umatilla National Forest 2517 SW Hailey Avenue Pendleton, OR 97801 Technical Publication F14-SO-TP-09-00 May 2000 iii AUTHOR DAVID C.
    [Show full text]
  • Stand Structure and Species Diversity Regulate Biomass Carbon Stock Under Major Central Himalayan Forest Types of India Siddhartha Kaushal and Ratul Baishya*
    Kaushal and Baishya Ecological Processes (2021) 10:14 https://doi.org/10.1186/s13717-021-00283-8 RESEARCH Open Access Stand structure and species diversity regulate biomass carbon stock under major Central Himalayan forest types of India Siddhartha Kaushal and Ratul Baishya* Abstract Background: Data on the impact of species diversity on biomass in the Central Himalayas, along with stand structural attributes is sparse and inconsistent. Moreover, few studies in the region have related population structure and the influence of large trees on biomass. Such data is crucial for maintaining Himalayan biodiversity and carbon stock. Therefore, we investigated these relationships in major Central Himalayan forest types using non- destructive methodologies to determine key factors and underlying mechanisms. Results: Tropical Shorea robusta dominant forest has the highest total biomass density (1280.79 Mg ha−1) and total carbon density (577.77 Mg C ha−1) along with the highest total species richness (21 species). The stem density ranged between 153 and 457 trees ha−1 with large trees (> 70 cm diameter) contributing 0–22%. Conifer dominant forest types had higher median diameter and Cedrus deodara forest had the highest growing stock (718.87 m3 ha−1); furthermore, C. deodara contributed maximally toward total carbon density (14.6%) among all the 53 species combined. Quercus semecarpifolia–Rhododendron arboreum association forest had the highest total basal area (94.75 m2 ha−1). We found large trees to contribute up to 65% of the growing stock. Nine percent of the species contributed more than 50% of the carbon stock. Species dominance regulated the growing stock significantly (R2 = 0.707, p < 0.001).
    [Show full text]
  • Is Ecological Succession Predictable?
    Is ecological succession predictable? Commissioned by Prof. dr. P. Opdam; Kennisbasis Thema 1. Project Ecosystem Predictability, Projectnr. 232317. 2 Alterra-Report 1277 Is ecological succession predictable? Theory and applications Koen Kramer Bert Brinkman Loek Kuiters Piet Verdonschot Alterra-Report 1277 Alterra, Wageningen, 2005 ABSTRACT Koen Kramer, Bert Brinkman, Loek Kuiters, Piet Verdonschot, 2005. Is ecological succession predictable? Theory and applications. Wageningen, Alterra, Alterra-Report 1277. 80 blz.; 6 figs.; 0 tables.; 197 refs. A literature study is presented on the predictability of ecological succession. Both equilibrium and nonequilibrium theories are discussed in relation to competition between, and co-existence of species. The consequences for conservation management are outlined and a research agenda is proposed focusing on a nonequilibrium view of ecosystem functioning. Applications are presented for freshwater-; marine-; dune- and forest ecosystems. Keywords: conservation management; competition; species co-existence; disturbance; ecological succession; equilibrium; nonequilibrium ISSN 1566-7197 This report can be ordered by paying € 15,- to bank account number 36 70 54 612 by name of Alterra Wageningen, IBAN number NL 83 RABO 036 70 54 612, Swift number RABO2u nl. Please refer to Alterra-Report 1277. This amount is including tax (where applicable) and handling costs. © 2005 Alterra P.O. Box 47; 6700 AA Wageningen; The Netherlands Phone: + 31 317 474700; fax: +31 317 419000; e-mail: [email protected] No part of this publication may be reproduced or published in any form or by any means, or stored in a database or retrieval system without the written permission of Alterra. Alterra assumes no liability for any losses resulting from the use of the research results or recommendations in this report.
    [Show full text]
  • 2005 Forest Ecosystem Study Unit
    TABLE OF CONTENTS Forest Ecosystems............................................................................................................... 1 What is an ecosystem?.................................................................................................... 2 Ecosystem Classification ................................................................................................ 2 What is a forest?.............................................................................................................. 5 What are the different kinds of forests?.......................................................................... 5 Why do we need forests? ................................................................................................ 6 What are the layers of a forest?....................................................................................... 8 Ecological Succession......................................................................................................... 9 How Forest Ecosystems Change..................................................................................... 9 Stages of Succession..................................................................................................... 10 How Succession Affects Energy Flow ......................................................................... 12 Species Characteristic of Georgia’s Ecosystems .......................................................... 13 Tree Identification........................................................................................................
    [Show full text]
  • Disturbance and Mosquito Diversity in the Lowland Tropical Rainforest of Central Panama Received: 28 October 2016 Jose R
    www.nature.com/scientificreports OPEN Disturbance and mosquito diversity in the lowland tropical rainforest of central Panama Received: 28 October 2016 Jose R. Loaiza1,2,3, Larissa C. Dutari1, Jose R. Rovira1,2, Oris I. Sanjur2, Gabriel Z. Laporta 4,5, Accepted: 28 June 2017 James Pecor6, Desmond H. Foley6, Gillian Eastwood7, Laura D. Kramer7, Meghan Radtke8 & Published: xx xx xxxx Montira Pongsiri8 The Intermediate Disturbance Hypothesis (IDH) is well-known in ecology providing an explanation for the role of disturbance in the coexistence of climax and colonist species. Here, we used the IDH as a framework to describe the role of forest disturbance in shaping the mosquito community structure, and to identify the ecological processes that increase the emergence of vector-borne disease. Mosquitoes were collected in central Panama at immature stages along linear transects in colonising, mixed and climax forest habitats, representing diferent levels of disturbance. Species were identifed taxonomically and classifed into functional categories (i.e., colonist, climax, disturbance-generalist, and rare). Using the Huisman-Olf-Fresco multi-model selection approach, IDH testing was done. We did not detect a unimodal relationship between species diversity and forest disturbance expected under the IDH; instead diversity peaked in old-growth forests. Habitat complexity and constraints are two mechanisms proposed to explain this alternative postulate. Moreover, colonist mosquito species were more likely to be involved in or capable of pathogen transmission than climax species. Vector species occurrence decreased notably in undisturbed forest settings. Old-growth forest conservation in tropical rainforests is therefore a highly-recommended solution for preventing new outbreaks of arboviral and parasitic diseases in anthropic environments.
    [Show full text]
  • Old Growth Forest & Hetzel Nature Trail Guide
    Old Growth Forest & Hetzel Nature Trail Rare. Distinctive. Diverse. 25 Acres of forest evolved over 10,000 years 59 63 47 51 56 34 46 26 1 2 17 Scenic. Historic. Dynamic. North Trail (1.4 miles) South Trail (.9 mile) Centerville Creek Trail Entrances Please respect LTC’s Old Growth Forest • Stay on the hiking trail. • No pets or bikes. • Clean the soles of your shoes to avoid introducing seeds of exotic (non-native) species. • Collecting is not allowed. • Leave no trace. Lakeshore Technical College has a unique ecological asset in its 25-acre forest – a wooded area containing old-growth trees. This is a unique biological feature that has evolved for more than 10,000 years without any recent significant intervention. This rare and distinctive treasure located on LTC’s campus will serve as the base for an educational trail. The preservation of the forest, construction of the trail, and this trail guide are the result of a volunteer partnership of concerned community members, with officials from Woodland Dunes Nature Center, UW-Manitowoc, UW-Sheboygan and LTC. LTC lies just northeast of the “Tension Zone” that separated Wisconsin’s two distinct floristic provinces at the time of European exploration: the southern hardwood forest, oak savanna, and prairie province to the south, and the conifer and northern hardwood forest to the north. The tension zone boasts an intermingling of species from both provinces. This forest is close enough to the tension zone to be considered a part of it since it has both the northern and southern components. See page 11.
    [Show full text]
  • A Holistic Assessment Pertains to Bio-Physical Indicators and Ecosystem Values Manish Mathur1,2* and S
    Mathur and Sundaramoorthy Ecological Processes (2018) 7:41 https://doi.org/10.1186/s13717-018-0148-2 RESEARCH Open Access Appraisal of arid land status: a holistic assessment pertains to bio-physical indicators and ecosystem values Manish Mathur1,2* and S. Sundaramoorthy1 Abstract Background: Appraisal of arid land status is very crucial one to know the extent and factors associated with their degradation. Previous studies from arid regions are mostly qualitative in nature (indicator assessment like good, moderate, severe, and very severe) and generally overlooked the significance of temporal fluctuation. Methods: In this study, the temporal status of 12 Indian arid lands was accessed by using a new integrated approach that includes attributes like relative converge score (RCS), herbaceous component score (HCS), soil quality indexModified (SQI), ecosystem monitoring value (EMV), and a modified bare patch index. From each land, data were collected during three seasonal events (pulse, inter-pulse, and non-pulse), and thus, status was evaluated with 36 observations. Data were analyzed by using frequency distribution, principal component analysis (PCA), student t test, and regression technique. Results: RCS and HCS were recorded minimum (0.005, 0.65) during non-pulse event and maximum (0.36, 1.79) during pulse event respectively. With this approach, multi-directional temporal status of lands identified that were grouped into lower (7), moderate (14), high (12), and very high (3) quality lands. Conclusion: This integrated study suggested that in arid regions, although rainfall triggers plant community composition, however, sole utilization of this parameter is unable to portray the true status of lands, and other physical (soil) and biotic (livestock and other anthropogenic) parameters are equally important and influential during other events.
    [Show full text]
  • Forest Succession Jeff Martin and Tom Gower
    No. 78 November, 1996 Forest Succession Jeff Martin and Tom Gower Succession is the natural replacement of plant or Sapling-pole: Trees eventually overtop and animal species, or species associations, in an area out-compete the forbs and over time. When we discuss forest succession, we shrubs. The intolerant trees are usually talking about replacement of tree continue rapid height growth species or tree associations. while the tolerant trees occupy their respective niche. Each stage of succession creates the conditions for the next stage. Temporary plant communities are Young: Growth is still rapid. Tree-to-tree replaced by more stable communities until a sort of competition may be severe equilibrium is reached between the plants and the resulting in competition caused environment. The following sequence is usually mortality. Any intolerant observed if sufficient time passes and no individuals that drop behind may disturbance occurs: die and their growing space may be occupied by tolerant trees. Plant Description Mature: Competition caused mortality Community continues. Both intolerant and tolerant trees may share the main Grass-forb: Forbs, grasses and shrubs canopy. In mixed conifer stands dominate the site. Seedlings there may be a distinct layering of may be present. intolerants and tolerants. Shrub-seedling: Trees tend to share and Climax: A relatively stable plant then begin to dominate the community which has a dominant site. The intolerant species plant population suited to the (see Forestry Fact No. 79, environment. Tolerant species Tolerance of Tree Species) dominate the site and the climax grow rapidly and dominate species will reproduce over tolerant species. successfully under their own shade.
    [Show full text]
  • Ecological Succession Refers to the Series of Ecological Changes That Every Community Undergoes Over Long Periods of Time
    Ecological succession refers to the series of ecological changes that every community undergoes over long periods of time. The process of succession begins with relatively few pioneering plants and the animals that are associated with these plants. The plant life serves as food, and often shelter for the animal life that can survive in that environment. The succession in the plant life is therefore paralleled by a succession in animal life. As a result of the process of succession, a primitive community develops. The organisms that make up the primitive community gradually change the environmental conditions so each successive community paves the way for the next. Each successive community develops through increasing complexity until it becomes a final, sustainable, stable, or self-perpetuating community, of dominant organisms, known as a climax community. In an ecosystem with a climax community, the conditions continue to be suitable for all the members of the community. The climax community is the final stage of ecological succession. In Newfoundland and Labrador there are examples of succession at various stages all around us. A muddy hole that seems to have dried up and new vegetation is growing around and even in it. A large open area that may have pockets of water but when you step back you can visualize a pond covering the whole area. Now let's have a look at the stages of succession and explain the factors that cause it to occur. Primary Succession Secondary Succession Contributing Factors Primary succession: There are two types of succession, the first type of succession is called primary succession which refers to a sequence beginning in an area where there is no soil or previous forms of life.
    [Show full text]
  • Forests, Competition and Succession'
    Forests, Competition and Succession David A. Perry Oregon State University Competition Succession Competition, the struggle for limited resources, than would be possible if all were competing for and succession, the sequence of change in dominant the same set of resources. organisms following colonization, have long been This article first discusses competition: why it key concepts employed by ecologists to understand occurs, why it does not occur, and how it shapes and organize the patterns of nature. Although com- the structure of communities. It then turns to the petition and succession are distinct processes, they patterns and mechanisms of succession, many of are closely related for at least two reasons. First, which turn on the nature of both competitive and successional trajectories are largely driven by inter- cooperative interactions among species. actions among organisms, including (but not re- stricted to) competition. Second, both are inti- mately related to the degree of equilibrium or I. COMPETITION disequilibrium in ecosystems and landscapes. Ecol- ogists once believed that succession led inexorably "The inhabitants of the world at each suc- to a stable equilibrium within a given community cessive period in its history have beaten their of organisms, the composition of which was deter- predecessors in the race for life." (Charles mined in large part by who won the struggle for Darwin, "The Origin of Species," 1859) limited resources. Although that view has not been totally discarded, most ecologists now recognize One of the oldest ideas in ecology is that individ- that change is the rule rather than the exception in uals utilizing the same resource will compete if nature, with few if any ecological communities that resource is in short supply.
    [Show full text]
  • Resprouting of Pioneer and Climax Species in the Pachakumachi Hills, Cumbum Valley, Western Ghats, India
    Ethnobotanical Leaflets 12: 343-347. 2008. Resprouting of Pioneer and Climax Species in the Pachakumachi Hills, Cumbum Valley, Western Ghats, India Jegan, G., Ramesh, G. and Muthuchelian, K. Centre for Biodiversity and Forest studies, Department of Bioenergy, School of Energy, Environmental and Natural Resources, Madurai Kamaraj University, Madurai – 625 021, Tamil Nadu, India. Corresponding Author: [email protected] Issued 30 May 2008 Abstract The resprouting ability of plant species allows them to remain in the ecosystem. Resprouting of pioneer and climax species are dependent upon the light regime. Pioneer species need light for regeneration as well as for resprouting. But in the case of climax species it is reverse. Keywords: Mallotus tetracoccus, Diospyros ovalifolia and forest gap. Introduction Woody plants are subjected to various types of physical disturbances that lead to the loss of foliage or stems. Whether a species is able to resprout is in many cases a direct function of the frequency and intensity of the disturbance. Disturbance and the possibility of damage are ubiquitous aspects of the life of plants. The formation of open gaps in the forest leads to a rapid recruitment and development of the canopy. Such forest gaps maintain high pioneer tree density and diversity. However, forest openings do not appear to maintain species diversity of non-pioneer, shade- tolerant trees. Patterns of plant growth and other ecological processes are thought to vary as a function of gap size, since gap size directly affects light levels and microclimates, and also affect nutrient availability. Forest openings create significant changes in the microclimate of the area as compared to the original forest understorey.
    [Show full text]