Modeling the Urban Ecosystem: a Conceptual Framework

Total Page:16

File Type:pdf, Size:1020Kb

Modeling the Urban Ecosystem: a Conceptual Framework Environment and Planning II Planning and Design IW), volume 26, pages 603 630 Modeling the urban ecosystem: a conceptual framework M Aibcrtt Department of Urban Design and Planning, University of Washington, Box 355740, Seattle, WA 98195, USA; e-mail: maibcrttou.wasliington.edu Received 14 October 1998; in revised form 22 March 1999 Abstract. In this paper I build on current research in urban and ecological simulation modeling to develop n conceptual framework for modeling the urban ecosystem. Although important progress has been made in various areas of urban modeling, operational urban models are still primitive in terms of their ability to represent ecological processes. On the other hand, environmental models designed to assess the ecological impact of an urban region are limited in their ability to represent human systems, I present here a strategy to integrate these two lines of research into an urban ecological model (UEM). This model addresses the human dimension of the Pugct Sound regional integrated simulation model (PRISM)—a multidisciplinary initiative at the University of Washington aimed at developing a dynamic and integrated understanding of the environmental and human systems in the Pugct Sound. UEM simulates the environmental pressures associated with human activities under alternative demographic, economic, policy, and environmental scenarios. The specific objectives of UEM are to: quantify the major sources of human-induced environmental stresses (such as land-cover changes and nutrient discharges); determine the spatial and temporal variability of human stressors in relation to changes in the biophysical structure; relate the biophysical impacts of these stressors to the variability and spatial heterogeneity in land uses, human activities, and management practices; and predict the changes in stressors in relation to changes in human factors. 1 Introduction Planning agencies worldwide are increasingly challenged by the need to assess the environmental implications of alternative urban growth patterns—and policies to control them—in a comprehensive manner. Urban growth leads to rapid conversion of land and puts increasing pressure on local and global ecosystems. It causes changes in water and energy fluxes. Natural habitats are reduced and fragmented, exotic organisms arc introduced, and nutrient cycles are severely modified. Although impacts of urban development often seem local, they cause environmental changes at larger scales. Assessments of urban growth that are timely and accurate, and developed in a transparent manner, are crucial to achieve sound decisions. However, operational urban models designed to analyze or predict the development of urban areas are still primitive in their ability to represent ecological processes and urban ecosystem dynamics. Though important progress has been made in various areas of urban modeling (Wegener, 1994; 1995), only a few scholars have attempted to integrate the environmental dimension. The majority of these models are designed to answer a set of fundamental but limited planning questions relevant to housing (Anas, 1995; Anas and Arnott, 1991; Kain and Apgar, 1985), land use (Landis, 1992; 1995; Prastacos, 1986; Waddell, 1998), transportation (Boyce, 1986; Kim, 1989) and in some cases the inter­ actions among them (de la Barra, 1989; Echenique et al, 1990; Mackett, 1990; Putman, 1983; 1991; Wegener, 1983). On the other hand, the environmental models designed to assess the ecological impact of an urban region are limited in their ability to represent human systems. These models represent people as static scenarios of land uses and economic activities and predict human-induced disturbances from aggregated measures of economic develop­ ment and urban growth. Only with the increasing attention paid to the role of human 606 M Alberti activities in global environmental change has the need emerged to represent more explicitly human systems in environmental models. Whereas integrated assessment modeling can be traced back to the late 1960s (Forrester, 1969; Meadows et al, 1972), the first generation of operational integrated models has emerged only in the mid-1980s. During the last decade, integrated assessment modeling has been proposed as a new approach to link biophysical and socioeconomic systems in assessing climate change (Dowlatabadi, 1995). At present more than thirty integrated assessment models (IAMs) have been developed (Alcamo, 1994; Dowlatabadi, 1995; Rotmans et al, 1995). The focus of current IAMs is global; however, a new generation of spatially explicit regional integrated models is now emerging (Maxwell and Costanza, 1995). These models have started to treat human decisions explicitly but are still too limited in the repre­ sentation of human behavior and the heterogeneity of urban land uses (Alberti, 1998). Recent progress in the study of complex systems (Schneider and Kay, 1994) and the evolution of computer modeling capabilities (Brail, 1990) have made possible a more explicit treatment of the link between human and ecological systems. The development of GIS has provided the capability to integrate spatial processes. However, the greatest challenge for integrating urban and environmental modeling will be in interfacing the various disciplines involved. Urban subsystems have been studied for several decades but progress in urban-ecological modeling has been limited because of the difficulty in integrating the natural and social sciences. A recent National Science Foundation workshop on urban processes pointed out that ecologists, social scientists, and urban planners will need to work together to make their data, models, and findings compatible with one another and to identify systematically where fruitful clusters of multidisci- plinary research problems can be developed (Brown, 1997). Such an approach can offer a new perspective on modeling urban systems. In this paper I build on research in urban and ecological simulation modeling to develop an integrated urban-ecological modeling framework. This framework is part of a current effort to develop an urban-ecological model (UEM) at the University of Washington as part of the Puget Sound regional integrated simulation model (PRISM). UEM simulates the environmental impacts associated with human activities under alter­ native demographic, economic, policy, and environmental scenarios. Its objectives are to: (1) Quantify the major sources of human-induced environmental stresses (such as land- cover changes and nutrient discharges); (2) Determine the spatial and temporal variability of human stressors in relation to changes in the biophysical structure; (3) Relate the biophysical impacts of these stressors to the variability and spatial hetero­ geneity in land uses, human activities, and management practices; and (4) Predict the changes in stressors in relation to changes in human factors. The development of an integrated urban-ecological framework has both scientific and policy relevance. It provides a basis for developing integrated knowledge of the processes and mechanisms that govern urban ecosystem dynamics. It also creates the basis for modeling urban systems and provides planners with a powerful tool to simulate the ecological impacts of urban development patterns. 2 The urban ecosystem Early efforts to understand the interactions between urban development and environ­ mental change led to the conceptual model of cities as urban ecosystems (Boyden et al, 1981; Douglas, 1983; Duvigneaud, 1974; Odum, 1963; 1997; Stearns and Montag, 1974). Ecologists have described the city as a heterotrophic ecosystem highly dependent on large inputs of energy and materials and a vast capacity to absorb emissions and waste (Boyden et al, 1981; Duvigneaud, 1974; Odum, 1963). Wolman (1965) applied an 'urban Modeling the urhan ecosystem 607 metabolism1 approach to quantify the Hows of energy and materials into and out of a hypothetical American city. Systems ccologists provided formal equations to describe the energy balance and the cycling of materials (Douglas, 1983; Oclum, 1983). Although these efforts have never been translated into operational simulation models, they have laid out the basis for urban-ecological research. Urban scholars were rightly skeptical about the attempts to integrate biological and socioeconomic concepts into system dynamics models. None of these models represented explicitly the processes by which humans affect or are affected by the urban environment. At best, human behavior was reduced to a few differential equations. These models simplified the interactions of natural and social systems so much that they could provide little useful insight for planners and decisionmakers. Since then, however, urban and ecological research has made important progress with respect to understanding how urban ecosystems operate and how they differ from natural ecosystems. Urban-ecological interactions are complex. Urban ecosystems consist of several interlinked subsystems -social, economic, institutional, and environmental each representing a complex system of its own and affecting all the others at various structural and functional levels. Urban development is a major determinant of eco­ system structure and influences significantly the functioning of natural ecosystems through (a) the conversion of land and transformation of the landscape; (b) the use of natural resources; and (c) the release of emissions and waste. The earth's ecosystems also provide (d) important services to the human population in urban
Recommended publications
  • An Assessment of Marine Ecosystem Damage from the Penglai 19-3 Oil Spill Accident
    Journal of Marine Science and Engineering Article An Assessment of Marine Ecosystem Damage from the Penglai 19-3 Oil Spill Accident Haiwen Han 1, Shengmao Huang 1, Shuang Liu 2,3,*, Jingjing Sha 2,3 and Xianqing Lv 1,* 1 Key Laboratory of Physical Oceanography, Ministry of Education, Ocean University of China, Qingdao 266100, China; [email protected] (H.H.); [email protected] (S.H.) 2 North China Sea Environment Monitoring Center, State Oceanic Administration (SOA), Qingdao 266033, China; [email protected] 3 Department of Environment and Ecology, Shandong Province Key Laboratory of Marine Ecology and Environment & Disaster Prevention and Mitigation, Qingdao 266100, China * Correspondence: [email protected] (S.L.); [email protected] (X.L.) Abstract: Oil spills have immediate adverse effects on marine ecological functions. Accurate as- sessment of the damage caused by the oil spill is of great significance for the protection of marine ecosystems. In this study the observation data of Chaetoceros and shellfish before and after the Penglai 19-3 oil spill in the Bohai Sea were analyzed by the least-squares fitting method and radial basis function (RBF) interpolation. Besides, an oil transport model is provided which considers both the hydrodynamic mechanism and monitoring data to accurately simulate the spatial and temporal distribution of total petroleum hydrocarbons (TPH) in the Bohai Sea. It was found that the abundance of Chaetoceros and shellfish exposed to the oil spill decreased rapidly. The biomass loss of Chaetoceros and shellfish are 7.25 × 1014 ∼ 7.28 × 1014 ind and 2.30 × 1012 ∼ 2.51 × 1012 ind in the area with TPH over 50 mg/m3 during the observation period, respectively.
    [Show full text]
  • Vegetation Demographics in Earth System Models: a Review of Progress and Priorities
    Lawrence Berkeley National Laboratory Recent Work Title Vegetation demographics in Earth System Models: A review of progress and priorities. Permalink https://escholarship.org/uc/item/3912p4m3 Journal Global change biology, 24(1) ISSN 1354-1013 Authors Fisher, Rosie A Koven, Charles D Anderegg, William RL et al. Publication Date 2018 DOI 10.1111/gcb.13910 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Received: 11 April 2017 | Revised: 12 August 2017 | Accepted: 17 August 2017 DOI: 10.1111/gcb.13910 RESEARCH REVIEW Vegetation demographics in Earth System Models: A review of progress and priorities Rosie A. Fisher1 | Charles D. Koven2 | William R. L. Anderegg3 | Bradley O. Christoffersen4 | Michael C. Dietze5 | Caroline E. Farrior6 | Jennifer A. Holm2 | George C. Hurtt7 | Ryan G. Knox2 | Peter J. Lawrence1 | Jeremy W. Lichstein8 | Marcos Longo9 | Ashley M. Matheny10 | David Medvigy11 | Helene C. Muller-Landau12 | Thomas L. Powell2 | Shawn P. Serbin13 | Hisashi Sato14 | Jacquelyn K. Shuman1 | Benjamin Smith15 | Anna T. Trugman16 | Toni Viskari12 | Hans Verbeeck17 | Ensheng Weng18 | Chonggang Xu4 | Xiangtao Xu19 | Tao Zhang8 | Paul R. Moorcroft20 1National Center for Atmospheric Research, Boulder, CO, USA 2Lawrence Berkeley National Laboratory, Berkeley, CA, USA 3Department of Biology, University of Utah, Salt Lake City, UT, USA 4Los Alamos National Laboratory, Los Alamos, NM, USA 5Department of Earth and Environment, Boston University, Boston, MA, USA 6Department of Integrative Biology,
    [Show full text]
  • Emergent Biogeography of Microbial Communities in a Model Ocean
    REPORTS germ insects not only uncovers those features es- mRNA localization indeed appears to be an sential to this developmental mode but also sheds important component of long-germ embryogene- light on how the bcd-dependent anterior patterning sis, perhaps even playing a role in the transition program might have evolved. Through analysis of from the ancestral short-germ to the derived long- the regulation of the trunk gap gene Kr in Dro- germ fate. sophila and Nasonia,wehavebeenabletodem- onstrate that anterior repression of Kr is essential References and Notes for head and thorax formation and is a common 1. G. K. Davis, N. H. Patel, Annu. Rev. Entomol. 47, 669 (2002). feature of long-germ patterning. Both insects 2. T. Berleth et al., EMBO J. 7, 1749 (1988). accomplish this task through maternal, anteriorly 3. W. Driever, C. Nusslein-Volhard, Cell 54, 83 (1988). localized factors that either indirectly (Drosophila) 4. J. Lynch, C. Desplan, Curr. Biol. 13, R557 (2003). or directly (Nasonia) repress Kr and, hence, trunk 5. J. A. Lynch, A. E. Brent, D. S. Leaf, M. A. Pultz, C. Desplan, Nature 439, 728 (2006). fates. In Drosophila, the terminal system and bcd 6. J. Savard et al., Genome Res. 16, 1334 (2006). regulate expression of gap genes, including Dm-gt, 7. G. Struhl, P. Johnston, P. A. Lawrence, Cell 69, 237 (1992). that repress Dm-Kr. Nasonia’s bcd-independent 8. A. Preiss, U. B. Rosenberg, A. Kienlin, E. Seifert, long-germ embryos must solve the same problem, H. Jackle, Nature 313, 27 (1985). Fig. 4.
    [Show full text]
  • Meta-Ecosystems: a Theoretical Framework for a Spatial Ecosystem Ecology
    Ecology Letters, (2003) 6: 673–679 doi: 10.1046/j.1461-0248.2003.00483.x IDEAS AND PERSPECTIVES Meta-ecosystems: a theoretical framework for a spatial ecosystem ecology Abstract Michel Loreau1*, Nicolas This contribution proposes the meta-ecosystem concept as a natural extension of the Mouquet2,4 and Robert D. Holt3 metapopulation and metacommunity concepts. A meta-ecosystem is defined as a set of 1Laboratoire d’Ecologie, UMR ecosystems connected by spatial flows of energy, materials and organisms across 7625, Ecole Normale Supe´rieure, ecosystem boundaries. This concept provides a powerful theoretical tool to understand 46 rue d’Ulm, F–75230 Paris the emergent properties that arise from spatial coupling of local ecosystems, such as Cedex 05, France global source–sink constraints, diversity–productivity patterns, stabilization of ecosystem 2Department of Biological processes and indirect interactions at landscape or regional scales. The meta-ecosystem Science and School of perspective thereby has the potential to integrate the perspectives of community and Computational Science and Information Technology, Florida landscape ecology, to provide novel fundamental insights into the dynamics and State University, Tallahassee, FL functioning of ecosystems from local to global scales, and to increase our ability to 32306-1100, USA predict the consequences of land-use changes on biodiversity and the provision of 3Department of Zoology, ecosystem services to human societies. University of Florida, 111 Bartram Hall, Gainesville, FL Keywords 32611-8525,
    [Show full text]
  • Chapter 4 – Steady State Models
    CHAPTER 4 Steady State Models X.-Z. Kong, F.-L. Xu1, W. He, W.-X. Liu, B. Yang Peking University, Beijing, China 1Corresponding author: E-mail: xufl@urban.pku.edu.cn OUTLINE 4.1 Steady State Model: Ecopath as an 4.2.4.2 Changes in Ecosystem Example 66 Functioning 79 4.1.1 Steady State Model 66 4.2.4.3 Collapse in the Food 4.1.2 Ecopath Model 66 Web: Differences in 4.1.3 Future Perspectives 68 Structure 81 4.2.4.4 Toward an Immature 4.2 Ecopath Model for a Large Chinese but Stable Ecosystem 83 Lake: A Case Study 68 4.2.4.5 Potential Driving 4.2.1 Introduction 68 Factors and 4.2.2 Study Site 70 Underlying 4.2.3 Model Development 73 Mechanisms 84 4.2.3.1 Model Construction 4.2.4.6 Hints for Future Lake and Parameterization 73 Fishery and 4.2.3.2 Evaluation of Ecosystem Restoration 85 Functioning 74 4.2.3.3 Determination of 4.3 Conclusions 86 Trophic Level 76 References 86 4.2.4 Results and Discussion 76 4.2.4.1 Basic Model Performance 76 Ecological Model Types, Volume 28 Ó 2016 Elsevier B.V. http://dx.doi.org/10.1016/B978-0-444-63623-2.00004-9 65 All rights reserved. 66 4. STEADY STATE MODELS 4.1 STEADY STATE MODEL: ECOPATH AS AN EXAMPLE 4.1.1 Steady State Model Steady state ecological models are established to describe conditions in which the modeled components (mass or energy) are stable, i.e., do not change over time (Jørgensen and Fath, 2011).
    [Show full text]
  • Urex Srn 2020 Annual Report
    UREX SRN 2020 ANNUAL REPORT Award Number 1444755 Project Period July 1, 2015 - June 30, 2020 (No-Cost Extension granted through June 30, 2021) Reporting Period: July 1, 2019 - June 30, 2020 (Year 5) Executive Management Team Charles L. Redman, Arizona State University Nancy B. Grimm, Arizona State University Mikhail V. Chester, Arizona State University Peter Groffman,City University of New York David M. Iwaniec, Georgia State University P. Timon McPhearson, The New School Thaddeus R. Miller, Arizona State University Tischa A. Muñoz-Erickson, USDA Forest Service Urban Resilience to Extremes Sustainability Research Network www.URExSRN.net Table of Contents Overarching UREx SRN Goals 1 Network Partners 2 Common Abbreviations 2 Accomplishments 3 Major Activities Specific Objectives Significant Results Key Outcomes & Other Achievements Opportunities for Training & Professional Development Disseminating Results to Communities of Interest Year 6 Plans Impacts 22 Impact on the Development of the Principal Disciplines of the Project Impact on Other Disciplines Impact on the Development of Human Resources Impact on Physical Resources that Form Infrastructure Impact on Institutional Resources that Form Infrastructure Impact on Information Resources that Form Infrastructure Impact on Technology Transfer Impact on Society Beyond Science & Technology Changes 27 Products 28 Books Book Chapters Journal Articles Conference Presentations Other Publications/Products Thesis/Dissertations Network Researchers 41 External Advisory Members 48 Practitioner Organizations 49 Overarching UREx SRN Goals Climate change is widely considered to be one of the greatest challenges to global sustainability, with extreme events being the most immediate way that people experience this phenomenon. Urban areas are particularly vulnerable to these events given their location, high concentration of people, and increasingly complex and interdependent infrastructure.
    [Show full text]
  • Integrated Approaches to Long-Term Studies of Urban Ecological Systems
    Articles IntegratedIntegrated ApproachesApproaches toto Long-TermLong-Term Studies Studies ofof UrbanUrban EcologicalEcological SystemsSystems NANCY B. GRIMM, J. MORGAN GROVE, STEWARD T. A. PICKETT, AND CHARLES L. REDMAN n 1935, Arthur Tansley wrote: I URBAN ECOLOGICAL SYSTEMS PRESENT We cannot confine ourselves to the so-called “natural” entities and ignore the processes and expressions of vegetation now so MULTIPLE CHALLENGES TO ECOLOGISTS— abundantly provided by man. Such a course is not scientifically PERVASIVE HUMAN IMPACT AND EXTREME sound, because scientific analysis must penetrate beneath the HETEROGENEITY OF CITIES, AND THE forms of the “natural” entities, and it is not practically useful because ecology must be applied to conditions brought about by NEED TO INTEGRATE SOCIAL AND human activity. The “natural” entities and the anthropogenic ECOLOGICAL APPROACHES, CONCEPTS, derivates alike must be analyzed in terms of the most appropriate concepts we can find. (Tansley 1935, p. 304) AND THEORY This quote captures the spirit of the new urban emphasis The conceptual basis for studying urban in the US Long-Term Ecological Research (LTER) net- ecological systems work. We know now that Earth abounds with both subtle and pronounced evidence of the influence of people on Why has the study of urban ecological systems attracted so natural ecosystems (Russell 1993, Turner and Meyer much recent interest? The rationale for the study of 1993). Arguably, cities are the most human dominated of human-dominated systems is three-pronged. First, all ecosystems. Recent calls for studies on “human-domi- humans dominate Earth’s ecosystems (Groffman and nated ecosystems” (Vitousek et al. 1997) finally have been Likens 1994, Botsford et al.
    [Show full text]
  • Models for an Ecosystem Approach to Fisheries
    ISSN 0429-9345 FAO FISHERIES 477 TECHNICAL PAPER 477 Models for an ecosystem approach to fisheries Models for an ecosystem approach to fisheries This report reviews the methods available for assessing the impacts of interactions between species and fisheries and their implications for marine fisheries management. A brief description of the various modelling approaches currently in existence is provided, highlighting in particular features of these models that have general relevance to the field of ecosystem approach to fisheries (EAF). The report concentrates on the currently available models representative of general types such as bionergetic models, predator-prey models and minimally realistic models. Short descriptions are given of model parameters, assumptions and data requirements. Some of the advantages, disadvantages and limitations of each of the approaches in addressing questions pertaining to EAF are discussed. The report concludes with some recommendations for moving forward in the development of multispecies and ecosystem models and for the prudent use of the currently available models as tools for provision of scientific information on fisheries in an ecosystem context. FAO Cover: Illustration by Elda Longo FAO FISHERIES Models for an ecosystem TECHNICAL PAPER approach to fisheries 477 by Éva E. Plagányi University of Cape Town South Africa FOOD AND AGRICULTURE AND ORGANIZATION OF THE UNITED NATIONS Rome, 2007 The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries.
    [Show full text]
  • Can We Detect Ecosystem Critical Transitions and Signals of Changing Resilience from Paleo-Ecological Records? Zofia E
    Can we detect ecosystem critical transitions and signals of changing resilience from paleo-ecological records? Zofia E. Taranu, Stephen R. Carpenter, Victor Frossard, Jean-Philippe Jenny, Zoe Thomas, Jesse C. Vermaire, Marie-Elodie Perga To cite this version: Zofia E. Taranu, Stephen R. Carpenter, Victor Frossard, Jean-Philippe Jenny, Zoe Thomas, etal.. Can we detect ecosystem critical transitions and signals of changing resilience from paleo-ecological records?. Ecosphere, Ecological Society of America, 2018, 9 (10), 10.1002/ecs2.2438. hal-01959637 HAL Id: hal-01959637 https://hal.archives-ouvertes.fr/hal-01959637 Submitted on 18 Dec 2018 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Distributed under a Creative Commons Attribution| 4.0 International License Can we detect ecosystem critical transitions and signals of changing resilience from paleo-ecological records? 1, 2 3 3,4 € 5 ZOFIA E. TARANU, STEPHEN R. CARPENTER, VICTOR FROSSARD, JEAN-PHILIPPE JENNY, ZOE THOMAS, 6 7 JESSE C. VERMAIRE, AND MARIE-ELODIE PERGA 1Department of Biology, University
    [Show full text]
  • Knowing Nature in the City: Comparative Analysis of Knowledge Systems Challenges Along the 'Eco-Techno' Spectrum of Gree
    Portland State University PDXScholar Dissertations and Theses Dissertations and Theses Summer 8-1-2017 Knowing Nature in the City: Comparative Analysis of Knowledge Systems Challenges Along the 'Eco- Techno' Spectrum of Green Infrastructure in Portland & Baltimore Annie Marissa Matsler Portland State University Follow this and additional works at: https://pdxscholar.library.pdx.edu/open_access_etds Part of the Sustainability Commons, and the Urban Studies Commons Let us know how access to this document benefits ou.y Recommended Citation Matsler, Annie Marissa, "Knowing Nature in the City: Comparative Analysis of Knowledge Systems Challenges Along the 'Eco-Techno' Spectrum of Green Infrastructure in Portland & Baltimore" (2017). Dissertations and Theses. Paper 3767. https://doi.org/10.15760/etd.5651 This Dissertation is brought to you for free and open access. It has been accepted for inclusion in Dissertations and Theses by an authorized administrator of PDXScholar. Please contact us if we can make this document more accessible: [email protected]. Knowing Nature in the City: Comparative Analysis of Knowledge Systems Challenges Along the ‘Eco-Techno’ Spectrum of Green Infrastructure in Portland & Baltimore by Annie Marissa Matsler A dissertation submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy in Urban Studies Dissertation Committee: Connie P. Ozawa, Chair Thaddeus R. Miller, Co-Chair Vivek Shandas Jennifer L. Morse Portland State University 2017 © 2017 Annie Marissa Matsler Abstract Green infrastructure development is desired in many municipalities because of its potential to address pressing environmental and social issues. However, despite technical optimism, institutional challenges create significant barriers to effective green infrastructure design, implementation, and maintenance.
    [Show full text]
  • Models of the World's Large Marine Ecosystems: GEF/LME Global
    Intergovernmental Oceanographic Commission technical series 80 Models of the World’s Large Marine Ecosystems UNESCO Intergovernmental Oceanographic Commission technical series 80 Models of the World’s Large Marine Ecosystems* GEF/LME global project Promoting Ecosystem-based Approaches to Fisheries Conservation and Large Marine Ecosystems UNESCO 2008 * As submitted to IOC Technical Series, UNESCO, 22 October 2008 IOC Technical Series No. 80 Paris, 20 October 2008 English only The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the Secretariats of UNESCO and IOC concerning the legal status of any country or territory, or its authorities, or concerning the delimitation of the frontiers of any country or territory. For bibliographic purposes, this document should be cited as follows: Models of the World’s Large Marine Ecosystems GEF/LME global project Promoting Ecosystem-based Approaches to Fisheries Conservation and Large Marine Ecosystems IOC Technical Series No. 80. UNESCO, 2008 (English) Editors: Villy Christensen1, Carl J. Walters1, Robert Ahrens1, Jackie Alder2, Joe Buszowski1, Line Bang Christensen1, William W.L. Cheung1, John Dunne3, Rainer Froese4, Vasiliki Karpouzi1, Kristin Kastner5, Kelly Kearney6, Sherman Lai1, Vicki Lam1, Maria L.D. Palomares1,7, Aja Peters-Mason8, Chiara Piroddi1, Jorge L. Sarmiento6, Jeroen Steenbeek1, Rashid Sumaila1, Reg Watson1, Dirk Zeller1, and Daniel Pauly1. Technical Editor: Jair Torres 1 Fisheries Centre,
    [Show full text]
  • A Theoretical Study of Biological Lotka-Volterra Ecological Model Using Comprehensive Thermodynamic Theory of Stability of Irreversible Processes (Cttsip)
    International Journal of Knowledge Engineering ISSN: 0976-5816 & E-ISSN: 0976-5824, Volume 3, Issue 1, 2012, pp.-91-94. Available online at http://www.bioinfo.in/contents.php?id=40 A THEORETICAL STUDY OF BIOLOGICAL LOTKA-VOLTERRA ECOLOGICAL MODEL USING COMPREHENSIVE THERMODYNAMIC THEORY OF STABILITY OF IRREVERSIBLE PROCESSES (CTTSIP) RAWAT S.G.1, BHALEKAR A.A.2 AND TANGDE V.M.3* 1Department of Applied Chemistry, Priyadarshini College of Engineering, Nagpur, MS, India. 2Department of Chemistry, Rashtrasant Tukadoji Maharaj Nagpur University, Nagpur, MS, India. 3Department of Applied Chemistry, Smt. Bhagwati Chaturvedi College of Engineering, Nagpur, MS, India. *Corresponding Author: Email- [email protected] Received: February 28, 2012; Accepted: March 06, 2012 Abstract- The dynamical relationship between predator and prey (Lotka-Volterra model or host-parasitoid system)[1] is one of the dominant themes in ecology. It was observed from the population data that interaction between a pair of predator-prey influences the population growth of both the species. This paper presents the study of thermodynamic stability of periodic Lotka-Volterra system against Prey popula- tion perturbation. The thermodynamic stability of representative model of Lotka-Volterra ecosystem has been investigated using proposed thermodynamic Lyapunov function in CTTSIP [2, 3, 4, 5] which follows the steps of Lyapunov's second method (also termed as direct meth- od) of stability of motion[6, 7]. The thermodynamic Lyapunov function, used herein is the excess rate of entropy production in thermodynam- ic perturbation space that conforms well with the dictates of second law of thermodynamics[8, 9]. Moreover, present study reveals the re- gions of stability, asymptotic stability and instability.
    [Show full text]