Impact of Population Growth on Environmental Degradation: Case of India
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Asia's Wicked Environmental Problems
ADBI Working Paper Series Asia’s Wicked Environmental Problems Stephen Howes and Paul Wyrwoll No. 348 February 2012 Asian Development Bank Institute Stephen Howes and Paul Wyrwoll are director and researcher, respectively, at the Development Policy Centre, Crawford School, Australian National University. This paper was prepared as a background paper for the Asian Development Bank (ADB)/Asian Development Bank Institute (ADBI) study Role of Key Emerging Economies—ASEAN, the People Republic of China, and India—for a Balanced, Resilient and Sustainable Asia. The views expressed in this paper are the views of the authors and do not necessarily reflect the views or policies of ADBI, the ADB, its Board of Directors, or the governments they represent. ADBI does not guarantee the accuracy of the data included in this paper and accepts no responsibility for any consequences of their use. Terminology used may not necessarily be consistent with ADB official terms. The Working Paper series is a continuation of the formerly named Discussion Paper series; the numbering of the papers continued without interruption or change. ADBI’s working papers reflect initial ideas on a topic and are posted online for discussion. ADBI encourages readers to post their comments on the main page for each working paper (given in the citation below). Some working papers may develop into other forms of publication. Suggested citation: Howes, S. and P. Wyrwoll. 2012. Asia’s Wicked Environmental Problems. ADBI Working Paper 348. Tokyo: Asian Development Bank Institute. Available: http://www.adbi.org/working- paper/2012/02/28/5009.asia.wicked.environmental.problems/ Please contact the author(s) for information about this paper. -
New Perspectives for Mapping Global Population Distribution Using World Settlement Footprint Products
sustainability Article New Perspectives for Mapping Global Population Distribution Using World Settlement Footprint Products Daniela Palacios-Lopez 1,* , Felix Bachofer 1 , Thomas Esch 1, Wieke Heldens 1 , Andreas Hirner 1, Mattia Marconcini 1 , Alessandro Sorichetta 2, Julian Zeidler 1 , Claudia Kuenzer 1, Stefan Dech 1, Andrew J. Tatem 2 and Peter Reinartz 1 1 German Aerospace Center (DLR), German Remote Sensing Data Center (DFD), Oberpfaffenhofen, D-82234 Wessling, Germany; [email protected] (F.B.); [email protected] (T.E.); [email protected] (W.H.); [email protected] (A.H.); [email protected] (M.M.); [email protected] (J.Z.); [email protected] (C.K.); [email protected] (S.D.); [email protected] (P.R.) 2 WorldPop, Department Geography and Environment, University of Southampton, Southampton SO17 1B, UK; [email protected] (A.S.); [email protected] (A.J.T.) * Correspondence: [email protected]; Tel.: +49-81-5328-2169 Received: 3 September 2019; Accepted: 28 October 2019; Published: 31 October 2019 Abstract: In the production of gridded population maps, remotely sensed, human settlement datasets rank among the most important geographical factors to estimate population densities and distributions at regional and global scales. Within this context, the German Aerospace Centre (DLR) has developed a new suite of global layers, which accurately describe the built-up environment and its characteristics at high spatial resolution: (i) the World Settlement Footprint 2015 layer (WSF-2015), a binary settlement mask; and (ii) the experimental World Settlement Footprint Density 2015 layer (WSF-2015-Density), representing the percentage of impervious surface. -
Land-Use, Land-Cover Changes and Biodiversity Loss - Helena Freitas
LAND USE, LAND COVER AND SOIL SCIENCES – Vol. I - Land-Use, Land-Cover Changes and Biodiversity Loss - Helena Freitas LAND-USE, LAND-COVER CHANGES AND BIODIVERSITY LOSS Helena Freitas University of Coimbra, Portugal Keywords: land use; habitat fragmentation; biodiversity loss Contents 1. Introduction 2. Primary Causes of Biodiversity Loss 2.1. Habitat Degradation and Destruction 2.2. Habitat Fragmentation 2.3. Global Climate Change 3. Strategies for Biodiversity Conservation 3.1. General 3.2. The European Biodiversity Conservation Strategy 4. Conclusions Glossary Bibliography Biographical Sketch Summary During Earth's history, species extinction has probably been caused by modifications of the physical environment after impacts such as meteorites or volcanic activity. On the contrary, the actual extinction of species is mainly a result of human activities, namely any form of land use that causes the conversion of vast areas to settlement, agriculture, and forestry, resulting in habitat destruction, degradation, and fragmentation, which are among the most important causes of species decline and extinction. The loss of biodiversity is unique among the major anthropogenic changes because it is irreversible. The importance of preserving biodiversity has increased in recent times. The global recognition of the alarming loss of biodiversity and the acceptance of its value resultedUNESCO in the Convention on Biologi – calEOLSS Diversity. In addition, in Europe, the challenge is also the implementation of the European strategy for biodiversity conservation and agricultural policies, though it is increasingly recognized that the strategy is limitedSAMPLE by a lack of basic ecological CHAPTERS information and indicators available to decision makers and end users. We have reached a point where we can save biodiversity only by saving the biosphere. -
Effective Population Size and Genetic Conservation Criteria for Bull Trout
North American Journal of Fisheries Management 21:756±764, 2001 q Copyright by the American Fisheries Society 2001 Effective Population Size and Genetic Conservation Criteria for Bull Trout B. E. RIEMAN* U.S. Department of Agriculture Forest Service, Rocky Mountain Research Station, 316 East Myrtle, Boise, Idaho 83702, USA F. W. A LLENDORF Division of Biological Sciences, University of Montana, Missoula, Montana 59812, USA Abstract.ÐEffective population size (Ne) is an important concept in the management of threatened species like bull trout Salvelinus con¯uentus. General guidelines suggest that effective population sizes of 50 or 500 are essential to minimize inbreeding effects or maintain adaptive genetic variation, respectively. Although Ne strongly depends on census population size, it also depends on demographic and life history characteristics that complicate any estimates. This is an especially dif®cult problem for species like bull trout, which have overlapping generations; biologists may monitor annual population number but lack more detailed information on demographic population structure or life history. We used a generalized, age-structured simulation model to relate Ne to adult numbers under a range of life histories and other conditions characteristic of bull trout populations. Effective population size varied strongly with the effects of the demographic and environmental variation included in our simulations. Our most realistic estimates of Ne were between about 0.5 and 1.0 times the mean number of adults spawning annually. We conclude that cautious long-term management goals for bull trout populations should include an average of at least 1,000 adults spawning each year. Where local populations are too small, managers should seek to conserve a collection of interconnected populations that is at least large enough in total to meet this minimum. -
Energy Development's Impacts on the Wildlife, Landscapes, And
Losing Ground: Energy Development’s Impacts on the Wildlife, Landscapes, and Hunting Traditions of the American West A Report by the National Wildlife Federation and the Natural Resources Defense Council Barbara Wheeler he iconic game species of the American wildlife are an ecological marker for the health of non- West are in perilous decline, as migratory game species, which are also becoming increasingly T animals lose ground to energy development vulnerable to the effects of energy development. and habitat destruction in southeast Montana and northeast Wyoming. Sage-grouse, mule deer, and Bountiful wildlife populations are a major part of the pronghorn are facing decreasing herd sizes and cultures and economies of Montana and Wyoming. downward long-term population trends, which Deteriorations in habitat quality associated with threaten the continued viability of these species in energy development can negatively affect wildlife the coming decades. Of the species considered, only populations and, in turn, impact hunters, wildlife- elk populations are forecast to rebound and stabilize watchers, and the tourism industry as a whole, which brings millions of people and billions of dollars to that additional habitat loss or degradation from the region every year. These impacts justify the need from historic lows, though there is significant concern energy development could stall population growth and for land management reforms and for wide-scale further displace the species. Simultaneously, big game investments in game and non-game wildlife protection Losing Ground Jack Dempsey at state and federal levels to offset the increasing impact on wildlife from energy development. Oregon Department of Fish and Wildlife A study commissioned by the National Wildlife Federation and the Natural Resources Defense A study commissioned by the Council analyzes trends in population and hunting National Wildlife Federation and opportunities for mule deer, pronghorn, elk, and the Natural Resources Defense greater sage-grouse. -
Globalization and Infectious Diseases: a Review of the Linkages
TDR/STR/SEB/ST/04.2 SPECIAL TOPICS NO.3 Globalization and infectious diseases: A review of the linkages Social, Economic and Behavioural (SEB) Research UNICEF/UNDP/World Bank/WHO Special Programme for Research & Training in Tropical Diseases (TDR) The "Special Topics in Social, Economic and Behavioural (SEB) Research" series are peer-reviewed publications commissioned by the TDR Steering Committee for Social, Economic and Behavioural Research. For further information please contact: Dr Johannes Sommerfeld Manager Steering Committee for Social, Economic and Behavioural Research (SEB) UNDP/World Bank/WHO Special Programme for Research and Training in Tropical Diseases (TDR) World Health Organization 20, Avenue Appia CH-1211 Geneva 27 Switzerland E-mail: [email protected] TDR/STR/SEB/ST/04.2 Globalization and infectious diseases: A review of the linkages Lance Saker,1 MSc MRCP Kelley Lee,1 MPA, MA, D.Phil. Barbara Cannito,1 MSc Anna Gilmore,2 MBBS, DTM&H, MSc, MFPHM Diarmid Campbell-Lendrum,1 D.Phil. 1 Centre on Global Change and Health London School of Hygiene & Tropical Medicine Keppel Street, London WC1E 7HT, UK 2 European Centre on Health of Societies in Transition (ECOHOST) London School of Hygiene & Tropical Medicine Keppel Street, London WC1E 7HT, UK TDR/STR/SEB/ST/04.2 Copyright © World Health Organization on behalf of the Special Programme for Research and Training in Tropical Diseases 2004 All rights reserved. The use of content from this health information product for all non-commercial education, training and information purposes is encouraged, including translation, quotation and reproduction, in any medium, but the content must not be changed and full acknowledgement of the source must be clearly stated. -
Land Degradation Neutrality
Land Degradation Neutrality: implications and opportunities for conservation Nature Based Solutions to Desertification, Land Degradation and Drought 2nd Edition, November 2015 IUCN Global Drylands Initiative Land Degradation Neutrality: implications and opportunities for conservation Nature Based Solutions to Desertification, Land Degradation and Drought 2nd Edition, November 2015 With contributions from Global Drylands Initiative, CEM, WCEL, WCPA, CEC1 1 Contributors: Jonathan Davies, Masumi Gudka, Peter Laban, Graciela Metternicht, Sasha Alexander, Ian Hannam, Leigh Welling, Liette Vasseur, Jackie Siles, Lorena Aguilar, Lene Poulsen, Mike Jones, Louisa Nakanuku-Diggs, Julianne Zeidler, Frits Hesselink Copyright: ©2015 IUCN, International Union for Conservation of Nature and Natural Resources, Global Drylands Initiative, CEM, WCEL, WCPA and CEC. The designation of geographical entities in this book, and the presentation of the material, do not imply the expression of any opinion whatsoever on the part of IUCN and CEM concerning the legal status of any country, territory, or area, or of its authorities, or concerning the delimitation of its frontiers or boundaries. The views expressed in this publication do not necessarily reflect those of IUCN,Global Drylands Initiative, CEM, WCEL, WCPA and CEC. All rights reserved. No part of this book may be reprinted or reproduced or utilised in any form or by any electronic, mechanical, or other means, now known or hereafter invented, including photocopying and recording, or in any information storage -
Population Growth & Resource Capacity
Population Growth & Resource Capacity Part 1 Population Projections Between 1950 and 2005, population growth in the U.S. has been nearly linear, as shown in figure 1. Figure 1 U.S. Population in Billions 0.4 0.3 0.2 Actual Growth 0.1 Linear Approximation - - - H L Year 1950 1960 1970 1980 1990 2000 2010 Source: Population Division of the Department of Economic and Social Affairs of the United Nations Secretariat. World Population Prospects: The 2010 Revision. If you looked at population growth over a longer period of time, you would see that it is not actually linear. However, over the relatively short period of time above, the growth looks nearly linear. A statistical technique called linear regression can create a linear function that approximates the actual population growth over this period very well. It turns out that this function is P = 0.0024444t + 0.15914 where t represents the time variable measured in years since 1950 and P represents the (approximate) population of the U.S. measured in billions of people. (If you take statistics, you’ll probably learn how to obtain this function.) The graph of this linear function is shown in the figure above. (1) Just to make sure that you understand how to work with this function, use it to complete the following table. The actual population values are given. If you are working with the function correctly, the values you obtain should be close to the actual population values! Actual Population t P Year (billions of people) (years) (billions of people) 1960 .186158 1990 .256098 2005 .299846 (2) Use the linear function to determine the approximate year when the population of the U.S. -
Diffuse Agricultural Water Pollution in India
r 244 99DI Pergamon Wat. Sci. Tech. Vol 39, No. 3, pp. 33-47, 1999. ©1999 IAWQ r quality. In: Published by Elsevier Science Ltd IRC ai^Vater Printed in Great Britain. All rights reserved ana Sanitation Centre 0273-1223/99 $1900+ 0 00 >n in Beijing. Tel.:+31 70 30 609 80 PII: SO273-1223(99)0OO3O-X Fax: +31 ?0 38 390 64 «. Water and hinese), 6(4), DIFFUSE AGRICULTURAL WATER ol (Chinese), POLLUTION IN INDIA nvironmental G. D. Agrawal Enviroteck inst.(P) Ltd, New Delhi, India nvironmental >urces and its ABSTRACT nvironmental Concern over agricultural diffuse pollution sources in integrated water quality management has been growing recently. Such sources are likely to be even more critical in developing countries, including India, where agriculture and rural habitats are still dominant, unlike the G7 or other affluent industrialised nations. A 88. number of special features of the Indian scene need to be considered. These include: (i) extremely varying pesticides in rainfall and stream-flow patterns; (ii) still largely traditional agricultural practices with average application of ce, J4(l), 72- fertilizers and pesticides and significant areas under dry farming or only marginal irrigation; (iii) a very large cattle population, with agriculture almost always linked with animal husbandry; (iv) a culture of living close ter irrigation. to the river (if not in the river) with dominating instream uses of bathing, washing, cattle wading, waste disposal, etc. and large-scale floodplain farming; and (v) scant respect for rules, regulations and laws . PhD thesis, alongside an extremely weak law-enforcement machinery. The paper shows that in the non-monsoon (non-flood) periods, which may account for all but 2 months of a trs (Chinese), year, agricultural diffuse pollution sources seem to have no impact on stream water quality. -
The North American Mosaic: an Overview of Key Environmental Issues 3
The North American Mosaic An Overview of Key Environmental Issues June 2008 Commission for Environmental Cooperation section title A This report addresses the state of the environment in the territories of the Parties to the North American Agreement on Environmental Cooperation by providing an overview of key environmental issues. It provides an objective appraisal of environmental trends and conditions to inform the Council’s deliberations on strategic planning and future cooperative activities. This publication was prepared by the Secretariat of the Commission for Environmental Cooperation. The design and implementation of this report benefited from the participation of the State of the Environment Advisory Group, which is composed of environmental reporting experts from the Parties. The views contained herein do not necessarily reflect the views of the governments of Canada, Mexico or the United States of America. In general, this report does not address the wide variety of responses to the environmental issues described herein. Likewise, an evaluation of the efficacy of these responses is beyond its scope. More information, including detailed references for the findings in this report, is available on the CEC website: <http://www.cec.org/soe>. Publication details Type: Project report Date: June 2008 Original language: English Review and Quality Assurance Procedures • Review by the Parties: February – April 2008; April – May 2008 • For more information please consult the Acknowledgements. Published by the Communications Department -
Assessing Resource Depletion in LCA: a Review of Methods and Methodological Issues
Assessing resource depletion in LCA: a review of methods and methodological issues Serenella Sala www.jrc.ec.europa.eu Serving society Stimulating innovation Supporting legislation Outline Sustainability and resources Key concepts and perspectives Review on current impact assessment methodologies for Resources 27 November 2012 2 Resources and sustainability -1 One of the father of the definition of “sustainability” was Hans Carl von Carlowitz. The concept was founded in forestry and was strictly resource-based and stayed so for centuries (Carlowitz 1713, Cotta 1828). The concept was developed by foresters because timber had been excessively overused and become a very scarce resource in the process of the industrial revolution and urbanisation. Carlowitz HC (1713)Sylvicultura oeconomica, oder haußwirthliche Nachricht und Naturmäßige Anweisung zur wilden Baum-Zucht 27 November 2012 3 Resources and sustainability _2 Around 1700, the mining industry and livelihood of thousands was threatened in Saxony. It was not that the mines had been exhausted of their ores, the problem was an acute scarcity of timber. The mining industry and smelting of ores had consumed whole forests. In the vicinity of places of mining activity the old growth forests had disappeared completely. Trees had been cut at unsustainable rates for decades without efforts to restore the forests. First, the river systems in the Erzgebirge was engineered, so logs could be transported from ever more distant forest areas, but these measures only postponed the crisis. The prices for timber rose ever more, which led to bankruptcy and closure of parts of the mining industry. 27 November 2012 4 Resources and sustainability _3 • Environmental as well as economic and social dimension • Interplay between socio-economic drivers, environmental and socio economic impacts Should resources be included in LCIA? Scientific debate For sure they should be part of the impact assessment in LCSA…. -
Utah's Long-Term Demographic and Economic Projections Summary Principal Researchers: Pamela S
Research Brief July 2017 Utah's Long-Term Demographic and Economic Projections Summary Principal Researchers: Pamela S. Perlich, Mike Hollingshaus, Emily R. Harris, Juliette Tennert & Michael T. Hogue continue the existing trend of a slow decline. From Background 2015-2065, rates are projected to decline from 2.32 to 2.29. These rates are projected to remain higher The Kem C. Gardner Policy Institute prepares long-term than national rates that move from 1.87 to 1.86 over demographic and economic projections to support in- a similar period. formed decision making in the state. The Utah Legislature funds this research, which is done in collaboration with • In 2065, life expectancy in Utah is projected to be the Governor’s Office of Management and Budget, the -Of 86.3 for women and 85.2 for men. This is an increase fice of the Legislative Fiscal Analyst, the Utah Association of approximately 4 years for women and 6 years for of Governments, and other research entities. These 50- men. The sharper increase for men narrows the life year projections indicate continued population growth expectancy gap traditionally seen between the and illuminate a range of future dynamics and structural sexes. shifts for Utah. An initial set of products is available online • Natural increase (births minus deaths) is projected to at gardner.utah.edu. Additional research briefs, fact remain positive and account for two-thirds of the cu- sheets, web-enabled visualizations, and other products mulative population increase to 2065. However, giv- will be produced in the coming year. en increased life expectancy and declining fertility, the rate and amount of natural increase are project- State-Level Results ed to slowly decline over time.