CHAPTER 1 Urbanization and Growth: Setting the Context Patricia Clarke Annez and Robert M
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Effects of Eutrophication on Stream Ecosystems
EFFECTS OF EUTROPHICATION ON STREAM ECOSYSTEMS Lei Zheng, PhD and Michael J. Paul, PhD Tetra Tech, Inc. Abstract This paper describes the effects of nutrient enrichment on the structure and function of stream ecosystems. It starts with the currently well documented direct effects of nutrient enrichment on algal biomass and the resulting impacts on stream chemistry. The paper continues with an explanation of the less well documented indirect ecological effects of nutrient enrichment on stream structure and function, including effects of excess growth on physical habitat, and alterations to aquatic life community structure from the microbial assemblage to fish and mammals. The paper also dicusses effects on the ecosystem level including changes to productivity, respiration, decomposition, carbon and other geochemical cycles. The paper ends by discussing the significance of these direct and indirect effects of nutrient enrichment on designated uses - especially recreational, aquatic life, and drinking water. 2 1. Introduction 1.1 Stream processes Streams are all flowing natural waters, regardless of size. To understand the processes that influence the pattern and character of streams and reduce natural variation of different streams, several stream classification systems (including ecoregional, fluvial geomorphological, and stream order classification) have been adopted by state and national programs. Ecoregional classification is based on geology, soils, geomorphology, dominant land uses, and natural vegetation (Omernik 1987). Fluvial geomorphological classification explains stream and slope processes through the application of physical principles. Rosgen (1994) classified stream channels in the United States into seven major stream types based on morphological characteristics, including entrenchment, gradient, width/depth ratio, and sinuosity in various land forms. -
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. -
Urban Planning and Urban Design
5 Urban Planning and Urban Design Coordinating Lead Author Jeffrey Raven (New York) Lead Authors Brian Stone (Atlanta), Gerald Mills (Dublin), Joel Towers (New York), Lutz Katzschner (Kassel), Mattia Federico Leone (Naples), Pascaline Gaborit (Brussels), Matei Georgescu (Tempe), Maryam Hariri (New York) Contributing Authors James Lee (Shanghai/Boston), Jeffrey LeJava (White Plains), Ayyoob Sharifi (Tsukuba/Paveh), Cristina Visconti (Naples), Andrew Rudd (Nairobi/New York) This chapter should be cited as Raven, J., Stone, B., Mills, G., Towers, J., Katzschner, L., Leone, M., Gaborit, P., Georgescu, M., and Hariri, M. (2018). Urban planning and design. In Rosenzweig, C., W. Solecki, P. Romero-Lankao, S. Mehrotra, S. Dhakal, and S. Ali Ibrahim (eds.), Climate Change and Cities: Second Assessment Report of the Urban Climate Change Research Network. Cambridge University Press. New York. 139–172 139 ARC3.2 Climate Change and Cities Embedding Climate Change in Urban Key Messages Planning and Urban Design Urban planning and urban design have a critical role to play Integrated climate change mitigation and adaptation strategies in the global response to climate change. Actions that simul- should form a core element in urban planning and urban design, taneously reduce greenhouse gas (GHG) emissions and build taking into account local conditions. This is because decisions resilience to climate risks should be prioritized at all urban on urban form have long-term (>50 years) consequences and scales – metropolitan region, city, district/neighborhood, block, thus strongly affect a city’s capacity to reduce GHG emissions and building. This needs to be done in ways that are responsive and to respond to climate hazards over time. -
The Effects of Urbanization on Natural Resources in Jamaica
Doneika Simms. The Effects of Urbanization on Natural Resources in Jamaica . 44th ISOCARP Congress 2008 THE EFFECTS OF URBANIZATION ON NATURAL RESOURCES IN JAMAICA BACKGROUND OF STUDY AREA Jamaica is the third largest island in the Caribbean, comprising of approximately 4,400 sq. miles or 10,991 square kilometers in area. Over two-thirds of the country’s land resources consist of a central range of hills and mountains, with the Blue Mountain Range being the most significant, ranging over 6000 ft. in height (GOJ, 1994; Clarke, 2006). This means that urban development in areas such as the capital city of Kingston and other principal towns such as Montego Bay and Ocho Rios is limited to the relatively small amount of flat lands most of which has a coastal location (see figure 1). Figure 1 Showing a Map of Jamaica and the Various Cities along the Coast Source: http://www.sangstersrealty.com/jamaica_map.htm Although a significant portion of the terrain is mountainous, in several places the coastal plain extends to form broad embayments. Among these, a dry embankment on the south side of the island known as the Liguanea Plain has been occupied by the city of Kingston. The built-up area of the city spreads over 50 sq. miles and comprises the parish of Kingston and the suburban section of St. Andrew. The city is located on the eastern side of the island which is sheltered from the north-east trade winds by the Blue Mountains, hence being ideal for the major seaport of the country- the Kingston Harbour (Clarke, 2006). -
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. -
Urbanization As a Threat to Biodiversity: Trophic Theory, Economic Geography, and Implications for Conservation Land Acquisition
Proceedings of a Symposium at the Society for Conservation Biology 2004 Annual Meeting URBANIZATION AS A THREAT TO BIODIVERSITY: TROPHIC THEORY, ECONOMIC GEOGRAPHY, AND IMPLICATIONS FOR CONSERVATION LAND ACQUISITION Brian Czech1 ABSTRACT—Habitat loss is often cited as the primary cause of species endangerment in the United States, followed by invasive species, pollution, and direct take. Urbanization, one type of habitat loss, is the leading cause of species endangerment in the contiguous United States and entails a relatively thorough transformation from the “economy of nature” to the human economy. Principles of economic geography indicate that urbanization will continue as a function of economic growth, while principles of conservation biology indicate that the most thorough competitive exclusion occurs in urban areas. These findings suggest the need for an ecologically macroeconomic approach to conservation land acquisition strategies. “Habitat loss” is often cited as the primary cause of species these types of habitat loss are considered separate causes of endangerment in the United States, followed by invasive species endangerment, invasive species are identified as the species, pollution, disease, and direct take. However, vari- leading cause of species endangerment in the United States, ous types of habitat loss are readily identified, such as log- including Hawaii and Puerto Rico (Czech et al. 2000). On ging, mining, agriculture, and urbanization (table 1). When the mainland United States, however, urbanization is the Table 1.— Causes of endangerment for the first 877 (of the current 1,262) species in the United States and Puerto Rico classified as threatened or endangered by the United States Fish and Wildlife Service (from Czech et al. -
The Transition to a Predominantly Urban World and Its Underpinnings
Human Settlements Discussion Paper Series Theme: Urban Change –4 The transition to a predominantly urban world and its underpinnings David Satterthwaite This is the 2007 version of an overview of urban change and a discussion of its main causes that IIED’s Human Settlements Group has been publishing since 1986. The first was Hardoy, Jorge E and David Satterthwaite (1986), “Urban change in the Third World; are recent trends a useful pointer to the urban future?”, Habitat International, Vol. 10, No. 3, pages 33–52. An updated version of this was published in chapter 8 of these authors’ 1989 book, Squatter Citizen (Earthscan, London). Further updates were published in 1996, 2003 and 2005 – and this paper replaces the working paper entitled The Scale of Urban Change Worldwide 1950–2000 and its Underpinnings, published in 2005. Part of the reason for this updated version is the new global dataset produced by the United Nations Population Division on urban populations and on the populations of the largest cities. Unless otherwise stated, the statistics for global, regional, national and city populations in this paper are drawn from United Nations (2006), World Urbanization Prospects: the 2005 Revision, United Nations Population Division, Department of Economic and Social Affairs, CD-ROM Edition – Data in digital form (POP/DB/WUP/Rev.2005), United Nations, New York. The financial support that IIED’s Human Settlements Group receives from the Swedish International Development Cooperation Agency (Sida) and the Royal Danish Ministry of Foreign Affairs (DANIDA) supported the writing and publication of this working paper. Additional support was received from the World Institute for Development Economics Research. -
Human Population 2018 Lecture 8 Ecological Footprint
Human Population 2018 Lecture 8 Ecological footprint. The Daly criterea. Questions from the reading. pp. 87-107 Herman Daly “All my economists say, ‘on the one hand...on the other'. Give me a one- handed economist,” demanded a frustrated Harry S Truman. BOOKS Daly, Herman E. (1991) [1977]. Steady-State Economics (2nd. ed.). Washington, DC: Island Press. Daly, Herman E.; Cobb, John B., Jr (1994) [1989]. For the Common Good: Redirecting the Economy toward Community, the Environment, and a Sustainable Future (2nd. updated and expanded ed.). Boston: Beacon Press.. Received the Grawemeyer Award for ideas for improving World Order. Daly, Herman E. (1996). Beyond Growth: The Economics of Sustainable Development. Boston: Beacon Press. ISBN 9780807047095. Prugh, Thomas; Costanza, Robert; Daly, Herman E. (2000). The Local Politics of Global Sustainability. Washington, DC: Island Press. IS The Daly Criterea for sustainability • For a renewable resource, the sustainable rate to use can be no more than the rate of regeneration of its source. • For a non-renewable resource, the sustainable rate of use can be no greater than the rate at which a renewable resource, used sustainably, can be substituted for it. • For a pollutant, the sustainable rate of emmission can be no greater that the rate it can be recycled, absorbed or rendered harmless in its sink. http://www.footprintnetwork.org/ Ecosystem services Herbivore numbers control Carbon capture and Plant oxygen recycling and production soil replenishment Soil maintenance and processing Carbon and water storage system Do we need wild species? (negative) • We depend mostly on domesticated species for food (chickens...). • Food for domesticated species is itself from domesticated species (grains..) • Domesticated plants only need water, nutrients and light. -
The Role of Industrial and Post-Industrial Cities in Economic Development
Joint Center for Housing Studies Harvard University The Role of Industrial and Post-Industrial Cities in Economic Development John R. Meyer W00-1 April 2000 John R. Meyer is James W. Harpel Professor of Capital Formation and Economic Growth, Emeritus and chairman of the faculty committee of the Joint Center for Housing Studies. by John R. Meyer. All rights reserved. Short sections of text, not to exceed two paragraphs, may be quoted without explicit permission provided that full credit, including notice, is given to the source. Draft paper prepared for the World Bank Urban Development Division's research project entitled "Revisiting Development - Urban Perspectives." Any opinions expressed are those of the author and not those of the Joint Center for Housing Studies of Harvard University or of any of the persons or organizations providing support to the Joint Center for Housing Studies, nor of the World Bank Urban Development Division. The Role of Industrial and Post-Industrial Cities in Economic Development by John R. Meyer Once upon a time the location of towns and cities, at least superficially, seemed to be largely determined by the preferences of kings, princes, bishops, generals and other political and military leaders of society. A site’s defensibility or its capabilities for imposing military or administrative control over surrounding countryside were often of paramount importance. As one historian summed up the conventional wisdom: “Cities...were to be found...wherever agriculture produced sufficient surplus to sustain a population of rulers, soldiers, craftsmen and other nonfood producers.”1 The key to successful urbanization, in short, wasn’t so much what the city could do for the countryside as what the countryside could do for the city.2 This traditional view of early cities, while perhaps correct in its essentials, is also almost surely too limited.3 Cities were never just parasitic; most have always added at least some economic value. -
Safe Use of Wastewater in Agriculture Safe Use of Safe Wastewater in Agriculture Proceedings No
A UN-Water project with the following members and partners: UNU-INWEH Proceedings of the UN-Water project on the Safe Use of Wastewater in Agriculture Safe Use of Wastewater in Agriculture Wastewater Safe of Use Proceedings No. 11 No. Proceedings | UNW-DPC Publication SeriesUNW-DPC Coordinated by the UN-Water Decade Programme on Capacity Development (UNW-DPC) Editors: Jens Liebe, Reza Ardakanian Editors: Jens Liebe, Reza Ardakanian (UNW-DPC) Compiling Assistant: Henrik Bours (UNW-DPC) Graphic Design: Katja Cloud (UNW-DPC) Copy Editor: Lis Mullin Bernhardt (UNW-DPC) Cover Photo: Untited Nations University/UNW-DPC UN-Water Decade Programme on Capacity Development (UNW-DPC) United Nations University UN Campus Platz der Vereinten Nationen 1 53113 Bonn Germany Tel +49-228-815-0652 Fax +49-228-815-0655 www.unwater.unu.edu [email protected] All rights reserved. Publication does not imply endorsement. This publication was printed and bound in Germany on FSC certified paper. Proceedings Series No. 11 Published by UNW-DPC, Bonn, Germany August 2013 © UNW-DPC, 2013 Disclaimer The views expressed in this publication are not necessarily those of the agencies cooperating in this project. The designations employed and the presentation of material throughout this publication do not imply the expression of any opinion whatsoever on the part of the UN, UNW-DPC or UNU concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. Unless otherwise indicated, the ideas and opinions expressed by the authors do not necessarily represent the views of their employers. -
Spatiotemporal Variability of Urban Heat Island: Influence of Urbanization on Seasonal Pattern of Land Surface Temperature in the Metropolitan Region of Belém, Brazil
Scientific Article doi: 10.1590/2175-3369.013.e20200260 Spatiotemporal variability of urban heat 3369 island: Influence of urbanization on - seasonal pattern of land surface temperature in the Metropolitan Region ISSN 2175 of Belém, Brazil Variabilidade espaço-temporal das ilhas de calor urbano: Influência da urbanização no padrão sazonal da temperatura da superfície terrestre na Região Metropolitana de Belém, Brasil Licenciadosob uma Licença Creative Commons Jefferson Inayan de Oliveira Souto [a] , Julia Clarinda Paiva Cohen [a] [a] Universidade Federal do Pará, Instituto de Geociências, Belém, PA, Brasil How to cite: Souto, J. I. O., & Cohen, J. C. P. (2021). Spatiotemporal variability of urban heat island: Influence of urbanization on seasonal pattern of land surface temperature in the Metropolitan Region of Belém, Brazil. urbe. Revista Brasileira de Gestão Urbana, v. 13, e20200260. https://doi.org/10.1590/2175-3369.013.e20200260 Abstract Cities experience the extensive urban heat island effect (UHI), which continue to pose challenges for humanity's increasingly urban population, where tropical cities have experienced a continued and rapid urbanization process in the past few decades. We present the evolution of surface UHI and its controlling factors in the Metropolitan Region of Belém, over the last 16 years (2003–2018), which has experienced unique consolidated economic growth and urban transformation under wet equatorial climate. We incorporate MODIS and Landsat satellite data and evaluate statistical techniques for estimates the variation in the land surface temperature (LST) during two seasons: wet season and dry season. Our result revealed that the regions of fast urbanization resulted in a decrease of normalized difference vegetation index and increase of LST. -
Land Degradation
SPM4 Land degradation Coordinating Lead Authors: Lennart Olsson (Sweden), Humberto Barbosa (Brazil) Lead Authors: Suruchi Bhadwal (India), Annette Cowie (Australia), Kenel Delusca (Haiti), Dulce Flores-Renteria (Mexico), Kathleen Hermans (Germany), Esteban Jobbagy (Argentina), Werner Kurz (Canada), Diqiang Li (China), Denis Jean Sonwa (Cameroon), Lindsay Stringer (United Kingdom) Contributing Authors: Timothy Crews (The United States of America), Martin Dallimer (United Kingdom), Joris Eekhout (The Netherlands), Karlheinz Erb (Italy), Eamon Haughey (Ireland), Richard Houghton (The United States of America), Muhammad Mohsin Iqbal (Pakistan), Francis X. Johnson (The United States of America), Woo-Kyun Lee (The Republic of Korea), John Morton (United Kingdom), Felipe Garcia Oliva (Mexico), Jan Petzold (Germany), Mohammad Rahimi (Iran), Florence Renou-Wilson (Ireland), Anna Tengberg (Sweden), Louis Verchot (Colombia/ The United States of America), Katharine Vincent (South Africa) Review Editors: José Manuel Moreno (Spain), Carolina Vera (Argentina) Chapter Scientist: Aliyu Salisu Barau (Nigeria) This chapter should be cited as: Olsson, L., H. Barbosa, S. Bhadwal, A. Cowie, K. Delusca, D. Flores-Renteria, K. Hermans, E. Jobbagy, W. Kurz, D. Li, D.J. Sonwa, L. Stringer, 2019: Land Degradation. In: Climate Change and Land: an IPCC special report on climate change, desertification, land degradation, sustainable land management, food security, and greenhouse gas fluxes in terrestrial ecosystems [P.R. Shukla, J. Skea, E. Calvo Buendia, V. Masson-Delmotte, H.-O. Pörtner, D. C. Roberts, P. Zhai, R. Slade, S. Connors, R. van Diemen, M. Ferrat, E. Haughey, S. Luz, S. Neogi, M. Pathak, J. Petzold, J. Portugal Pereira, P. Vyas, E. Huntley, K. Kissick, M. Belkacemi, J. Malley, (eds.)]. In press.