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Population, Consumption & the Environment
12/11/2009 Population, Consumption & the Environment Alex de Sherbinin Center for International Earth Science Information Network (CIESIN), the Earth Institute at Columbia University Population-Environment Research Network 2 1 12/11/2009 Why is this important? • Global GDP is 20 times higher today than it was in 1900, having grown at a rate of 2.7% per annum (population grew at the rate of 13%1.3% p.a.) • CO2 emissions have grown at an annual rate of 3.5% since 1900, reaching 100 million metric tons of carbon in 2001 • The ecological footprint, a composite measure of consumption measured in hectares of biologically productive land, grew from 4.5 to 14.1 billion hectares between 1961 and 2003, and it is now 25% more than Earth’s “biocapacity ” • For CO2 emissions and footprints, the per capita impacts of high‐income countries are currently 6 to 10 times higher than those in low‐income countries 3 Outline 1. What kind of consumption is bad for the environment? 2. How are population dynamics and consumption linked? 3. Who is responsible for environmentally damaging consumption? 4. What contributions can demographers make to the understanding of consumption? 5. Conclusion: The challenge of “sustainable consumption” 4 2 12/11/2009 What kind of consumption is bad for the environment? SECTION 2 5 What kind of consumption is bad? “[Consumption is] human transformations of materials and energy. [It] is environmentally important to the extent that it makes materials or energy less available for future use, and … through its effects on biophysical systems, threatens hhlthlfththill”human health, welfare, or other things people value.” - Stern, 1997 • Early focus on “wasteful consumption”, conspicuous consumption, etc. -
Serengeti National Park
Serengeti • National Park A Guide Published by Tanzania National Parks Illustrated by Eliot Noyes ~~J /?ookH<~t:t;~ 2:J . /1.). lf31 SERENGETI NATIONAL PARK A Guide to your increased enjoyment As the Serengeti National Park is nearly as big as Kuwait or Northern Ireland no-one, in a single visit, can hope to see Introduction more than a small part of it. If time is limited a trip round The Serengeti National Park covers a very large area : the Seronera valley, with opportunities to see lion and leopard, 13,000 square kilometres of country stretching from the edge is probably the most enjoyable. of the Ngorongoro Conservation Unit in the south to the Kenya border in the north, and from the shores of Lake Victoria in the If more time is available journeys can be made farther afield, west to the Loliondo Game Controlled Area in the east. depending upon the season of the year and the whereabouts of The name "Serengeti" is derived from the Maasai language the wildlife. but has undergone various changes. In Maasai the name would be "Siringet" meaning "an extended area" but English has Visitors are welcome to get out of their cars in open areas, but replaced the i's with e's and Swahili has added a final i. should not do so near thick cover, as potentially dangerous For all its size, the Serengeti is not, of itself, a complete animals may be nearby. ecological unit, despite efforts of conservationists to make it so. Much of the wildlife· which inhabits the area moves freely across Please remember that travelling in the Park between the hours the Park boundaries at certain seasons of the year in search of 7 p.m. -
Serengeti: Nature's Living Laboratory Transcript
Serengeti: Nature’s Living Laboratory Transcript Short Film [crickets] [footsteps] [cymbal plays] [chime] [music plays] [TONY SINCLAIR:] I arrived as an undergraduate. This was the beginning of July of 1965. I got a lift down from Nairobi with the chief park warden. Next day, one of the drivers picked me up and took me out on a 3-day trip around the Serengeti to measure the rain gauges. And in that 3 days, I got to see the whole park, and I was blown away. [music plays] I of course grew up in East Africa, so I’d seen various parks, but there was nothing that came anywhere close to this place. Serengeti, I think, epitomizes Africa because it has everything, but grander, but louder, but smellier. [music plays] It’s just more of everything. [music plays] What struck me most was not just the huge numbers of antelopes, and the wildebeest in particular, but the diversity of habitats, from plains to mountains, forests and the hills, the rivers, and all the other species. The booming of the lions in the distance, the moaning of the hyenas. Why was the Serengeti the way it was? I realized I was going to spend the rest of my life looking at that. [NARRATOR:] Little did he know, but Tony had arrived in the Serengeti during a period of dramatic change. The transformation it would soon undergo would make this wilderness a living laboratory for understanding not only the Serengeti, but how ecosystems operate across the planet. This is the story of how the Serengeti showed us how nature works. -
Exotic Hunt in Texas ARTICLE and PHOTOS by CRAIG MOORE
20 lsTMAG .COM Exotic Hunt in Texas ARTICLE AND PHOTOS BY CRAIG MOORE vcr the years Texas has become a I set up a hunting trip to coincide with 0 great counterweight to my life in her business meetin!,rs, We would fly to New England. The hill country San Antonio on Friday and hunt through offers relief from the winter and some of the weekend and then stay with friendsin the best whitetail hunting anywhere. But Houston on Sunday night and b'Ohome on what makes Texas unique arc the people Tuesday afterher meeting. who have taken wildlife conscn·ation to Upon arrh·ing in Devil's River Nature a level not seen or understood in other Arca. we met Hunter Ross of Desert places. Safaris; an affablecharacter of West Texas The herds of exotic animals and the charm. Together, we worked out a plan to thorny scrub of the hill country seem to hunt free range axis on Friday and then transport folksto the plains of Africa-all go to a ranch where I could hunt scimitar while avoiding a 20·hour plane ride. horned oryx. One Thursday morning my wife Samie The majestic curls. coloring and unique called me from her office: MHcy, it looks history of the scimitar oryx enchanted me. like I have a meeting in Houston a couple Texas ranchers saved the scimitar oryx, of weeks fromi\londay ." now almost extinct in its native habitat. JANUARY/FEBRUARY 2017 21 Lone Star hunters and conservationists ensured the species' future through self regulated hunting practices. Recently, a law making it illegal to harvest scimitar horned oryx was presented to Texas Lawmakers. -
Influence of Common Eland (Taurotragus Oryx) Meat Composition on Its Further Technological Processing
CZECH UNIVERSITY OF LIFE SCIENCES PRAGUE Faculty of Tropical AgriSciences Department of Animal Science and Food Processing Influence of Common Eland (Taurotragus oryx) Meat Composition on its further Technological Processing DISSERTATION THESIS Prague 2018 Author: Supervisor: Ing. et Ing. Petr Kolbábek prof. MVDr. Daniela Lukešová, CSc. Co-supervisors: Ing. Radim Kotrba, Ph.D. Ing. Ludmila Prokůpková, Ph.D. Declaration I hereby declare that I have done this thesis entitled “Influence of Common Eland (Taurotragus oryx) Meat Composition on its further Technological Processing” independently, all texts in this thesis are original, and all the sources have been quoted and acknowledged by means of complete references and according to Citation rules of the FTA. In Prague 5th October 2018 ………..………………… Acknowledgements I would like to express my deep gratitude to prof. MVDr. Daniela Lukešová CSc., Ing. Radim Kotrba, Ph.D. and Ing. Ludmila Prokůpková, Ph.D., and doc. Ing. Lenka Kouřimská, Ph.D., my research supervisors, for their patient guidance, enthusiastic encouragement and useful critiques of this research work. I am very gratefull to Ing. Petra Maxová and Ing. Eva Kůtová for their valuable help during the research. I am also gratefull to Mr. Petr Beluš, who works as a keeper of elands in Lány, Mrs. Blanka Dvořáková, technician in the laboratory of meat science. My deep acknowledgement belongs to Ing. Radek Stibor and Mr. Josef Hora, skilled butchers from the slaughterhouse in Prague – Uhříněves and to JUDr. Pavel Jirkovský, expert marksman, who shot the animals. I am very gratefull to the experts from the Natura Food Additives, joint-stock company and from the Alimpex-maso, Inc. -
Sustainable Use of Wildland Resources: Ecological, Economic and Social Interactions
Sustainable Use of Wildland Resources: Ecological, Economic and Social Interactions An Analysis of Illegal Hunting of Wildlife in Serengeti National Park, Tanzania Ken Campbell, Valerie Nelson and Martin Loibooki June 2001 Main Report This report should be cited as: Campbell, K. L. I., Nelson, V. and Loibooki, M. (2001). Sustainable use of wildland resources, ecological, economic and social interactions: An analysis of illegal hunting of wildlife in Serengeti National Park, Tanzania. Department for International Development (DFID) Animal Health Programme and Livestock Production Programmes, Final Technical Report, Project R7050. Natural Resources Institute (NRI), Chatham, Kent, UK. 56 pp. 2 Sustainable Use of Wildland Resources: Ecological, Economic and Social Interactions An Analysis of Illegal Hunting of wildlife in Serengeti National Park, Tanzania FINAL TECHNICAL REPORT, 2001 DFID Animal Health and Livestock Production Programmes, Project R7050 Ken Campbell1, Valerie Nelson2 Natural Resources Institute, University of Greenwich, Chatham, ME4 4TB, UK and Martin Loibooki Tanzania National Parks, P.O. Box 3134, Arusha, Tanzania Executive Summary A common problem for protected area managers is illegal or unsustainable extraction of natural resources. Similarly, lack of access to an often decreasing resource base may also be a problem for rural communities living adjacent to protected areas. In Tanzania, illegal hunting of both resident and migratory wildlife is a significant problem for the management of Serengeti National Park. Poaching has already reduced populations of resident wildlife, whilst over-harvesting of the migratory herbivores may ultimately threaten the integrity of the Serengeti ecosystem. Reduced wildlife populations may in turn undermine local livelihoods that depend partly on this resource. This project examined illegal hunting from the twin perspectives of conservation and the livelihoods of people surrounding the protected area. -
Modeling Population Dynamics
Modeling Population Dynamics Gary C. White INTRODUCTION Population modeling is a tool used by wildlife managers. At its simplest, population modeling is a book keeping system to keep track of the four components of population change: births, deaths, immigration, and emigration. In mathematical symbolism, a population model can be expressed as Nt+1 = Nt + Bt - Dt + It - Et . Population size (N) at time t+1 is equal to the population size at time t plus births (B) minus deaths (D) plus immigrants (I) minus emigrants (E). The simplicity of the relationship belies its usefulness. If you were managing a business, you would be interested in knowing how much money was being paid out of the business, relative to how much money was coming in. The net difference represents your “profit”. The same is true for managing a wildlife population. By knowing the net change in the size of the wildlife population from one year to the next, you as a wildlife manager know whether the population is “profitable” (i.e., gaining in size), or headed towards bankruptcy (i.e., becoming smaller). Two examples will demonstrate typical uses of population models in big game management. In November 1995, voters in Colorado passed an amendment to the state’s constitution that outlawed hunting black bears during spring. Wildlife managers were asked if the bear population would increase because of no spring harvest. A population model can be used to answer this question. The second example of the use of a model is to determine which of two management schemes (e.g., no antlerless harvest versus significant antlerless harvest) will result in Modeling Population Dynamics – Draft May 6, 1998 2 the largest buck harvest in a mule deer population. -
Immigration and the Stable Population Model
IMMIGRATION AND THE STABLE POPULATION MODEL Thomas J. Espenshade The Urban Institute, 2100 M Street, N. W., Washington, D.C. 20037, USA Leon F. Bouvier Population Reference Bureau, 1337 Connecticut Avenue, N. W., Washington, D.C. 20036, USA W. Brian Arthur International Institute for Applied Systems Analysis, A-2361 Laxenburg, Austria RR-82-29 August 1982 Reprinted from Demography, volume 19(1) (1982) INTERNATIONAL INSTITUTE FOR APPLIED SYSTEMS ANALYSIS Laxenburg, Austria Research Reports, which record research conducted at IIASA, are independently reviewed before publication. However, the views and opinions they express are not necessarily those of the Institute or the National Member Organizations that support it. Reprinted with permission from Demography 19(1): 125-133, 1982. Copyright© 1982 Population Association of America. All rights reserved. No part of this publication may be reproduced or transmitted in any form or by any means, electronic or mechanical, including photocopy, recording, or any information storage or retrieval system, without permission in writing from the copyright holder. iii FOREWORD For some years, IIASA has had a keen interest in problems of population dynamics and migration policy. In this paper, reprinted from Demography, Thomas Espenshade, Leon Bouvier, and Brian Arthur extend the traditional methods of stable population theory to populations with below-replacement fertility and a constant annual quota of in-migrants. They show that such a situation results in a stationary population and examine how its size and ethnic structure depend on both the fertility level and the migration quota. DEMOGRAPHY© Volume 19, Number 1 Februory 1982 IMMIGRATION AND THE STABLE POPULATION MODEL Thomos J. -
Chapter 15 Biogeography and Dispersal
Chapter 15 Biogeography and dispersal Rob Hengeveld and Lia Hemerik Introduction This chapter evaluates the role of dispersal in biogeographical processes and their re- sulting patterns. We consider dispersal as a local process, which comprises the com- bined movements of individual organisms, but which can dominate processes even at the scale of continents. If this is correct, it is no longer possible to separate local ecological processes from those at broad, geographical scales. However, biogeo- graphical processes differ from those happening in one or a few localities; at the broader scales,there are additional processes occurring which are only evident when examined from this wider perspective. We integrate biogeography with ecology, explaining broad-scale effects, ranging from processes happening locally as the result of responses of individual organisms to perpetual changes in living conditions in heterogeneous space. The models to be used cannot be those traditional in population dynamics with a dispersal parameter plugged in, but must be spatially explicit. Only a broad-scale perspective of con- tinual redistribution of large groups of individuals or reproductive propagules can give dispersal its biological and biogeographical significance. Our general thesis in this chapter is that adaptation in non-uniform space enables individuals to cope effectively with environmental variation in time. In our analyses of spatially adaptive processes, we concentrate on principles rather than on details of specific phenomena, such as types of distance distribution. We therefore formulate these principles in terms of simple Poisson processes.In spe- cific cases, these distributions can be replaced by more complex ones which may fit better. -
Slides: Exponential Growth and Decay
Exponential Growth Many quantities grow or decay at a rate proportional to their size. I For example a colony of bacteria may double every hour. I If the size of the colony after t hours is given by y(t), then we can express this information in mathematical language in the form of an equation: dy=dt = 2y: A quantity y that grows or decays at a rate proportional to its size fits in an equation of the form dy = ky: dt I This is a special example of a differential equation because it gives a relationship between a function and one or more of its derivatives. I If k < 0, the above equation is called the law of natural decay and if k > 0, the equation is called the law of natural growth. I A solution to a differential equation is a function y which satisfies the equation. Annette Pilkington Exponential Growth dy(t) Solutions to the Differential Equation dt = ky(t) It is not difficult to see that y(t) = ekt is one solution to the differential dy(t) equation dt = ky(t). I as with antiderivatives, the above differential equation has many solutions. I In fact any function of the form y(t) = Cekt is a solution for any constant C. I We will prove later that every solution to the differential equation above has the form y(t) = Cekt . I Setting t = 0, we get The only solutions to the differential equation dy=dt = ky are the exponential functions y(t) = y(0)ekt Annette Pilkington Exponential Growth dy(t) Solutions to the Differential Equation dt = 2y(t) Here is a picture of three solutions to the differential equation dy=dt = 2y, each with a different value y(0). -
The Exponential Constant E
The exponential constant e mc-bus-expconstant-2009-1 Introduction The letter e is used in many mathematical calculations to stand for a particular number known as the exponential constant. This leaflet provides information about this important constant, and the related exponential function. The exponential constant The exponential constant is an important mathematical constant and is given the symbol e. Its value is approximately 2.718. It has been found that this value occurs so frequently when mathematics is used to model physical and economic phenomena that it is convenient to write simply e. It is often necessary to work out powers of this constant, such as e2, e3 and so on. Your scientific calculator will be programmed to do this already. You should check that you can use your calculator to do this. Look for a button marked ex, and check that e2 =7.389, and e3 = 20.086 In both cases we have quoted the answer to three decimal places although your calculator will give a more accurate answer than this. You should also check that you can evaluate negative and fractional powers of e such as e1/2 =1.649 and e−2 =0.135 The exponential function If we write y = ex we can calculate the value of y as we vary x. Values obtained in this way can be placed in a table. For example: x −3 −2 −1 01 2 3 y = ex 0.050 0.135 0.368 1 2.718 7.389 20.086 This is a table of values of the exponential function ex. -
Can More K-Selected Species Be Better Invaders?
Diversity and Distributions, (Diversity Distrib.) (2007) 13, 535–543 Blackwell Publishing Ltd BIODIVERSITY Can more K-selected species be better RESEARCH invaders? A case study of fruit flies in La Réunion Pierre-François Duyck1*, Patrice David2 and Serge Quilici1 1UMR 53 Ӷ Peuplements Végétaux et ABSTRACT Bio-agresseurs en Milieu Tropical ӷ CIRAD Invasive species are often said to be r-selected. However, invaders must sometimes Pôle de Protection des Plantes (3P), 7 chemin de l’IRAT, 97410 St Pierre, La Réunion, France, compete with related resident species. In this case invaders should present combina- 2UMR 5175, CNRS Centre d’Ecologie tions of life-history traits that give them higher competitive ability than residents, Fonctionnelle et Evolutive (CEFE), 1919 route de even at the expense of lower colonization ability. We test this prediction by compar- Mende, 34293 Montpellier Cedex, France ing life-history traits among four fruit fly species, one endemic and three successive invaders, in La Réunion Island. Recent invaders tend to produce fewer, but larger, juveniles, delay the onset but increase the duration of reproduction, survive longer, and senesce more slowly than earlier ones. These traits are associated with higher ranks in a competitive hierarchy established in a previous study. However, the endemic species, now nearly extinct in the island, is inferior to the other three with respect to both competition and colonization traits, violating the trade-off assumption. Our results overall suggest that the key traits for invasion in this system were those that *Correspondence: Pierre-François Duyck, favoured competition rather than colonization. CIRAD 3P, 7, chemin de l’IRAT, 97410, Keywords St Pierre, La Réunion Island, France.