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Education in Ecological Engineering—Aneedwhose Time Has Come
Circular Economy and Sustainability https://doi.org/10.1007/s43615-021-00067-4 ORIGINAL PAPER Education in Ecological Engineering—aNeedWhose Time Has Come Glenn Dale1,2 & Gabriela Dotro3 & Puneet Srivastava 4 & David Austin5 & Stacy Hutchinson6 & Peter Head7 & Ashantha Goonetilleke8 & Alexandros Stefanakis9 & Ranka Junge10 & José A. Fernández L. 11 & Vanessa Weyer12 & Wayne Truter 12 & Devi Bühler10 & John Bennett 2 & Hongbo Liu13 & Zifu Li14 & Jianqiang Du 15,16 & Petra Schneider17 & Jochen Hack18 & Andreas Schönborn 10 Received: 4 March 2021 /Accepted: 8 March 2021/ # The Author(s) 2021 Abstract Overcoming Limitations of Ecology and Engineering in Addressing Society’sChallengesBy providing an integrated, systems-approach to problem-solving that incorporates ecolog- ical principles in engineering design, ecological engineering addresses, many of the limitations of Ecology and Engineering needed to work out how people and nature can beneficially coexist on planet Earth. Despite its origins in the 1950s, ecological engineer- ing remains a niche discipline, while at the same time, there has never been a greater need to combine the rigour of engineering and science with the systems-approach of ecology for pro-active management of Earth’s biodiversity and environmental life-support sys- tems. Broad consensus on the scope and defining elements of ecological engineering and development of a globally consistent ecological engineering curriculum are key pillars to mainstream recognition of the discipline and practice of ecological engineering. The Importance of Ecological Engineering in Society In this paper, the importance of ecological engineering education is discussed in relation to the perceived need of our society to address global challenges of sustainable development. The perceived needs of industry, practitioners, educators and students for skills in ecological engineering are also discussed. -
Hawaiian High Islands Ecoregion Pmtecting Nature
5127/2015 Ecoregion Description The Nature Conservancy Hawaiian High Islands Ecoregion Pmtecting nature. Preserving life ~ This page last revised 21 July 2007 Home Introduction Ecoregion Description Ecoregion Conservation Targets Location and context Viability Goals The Hawaiian High Islands Ecoregion lies in the north Portfolio central Pacific Ocean. It is comprised of the ecological TNC Action Sites systems, natural communities, and s~ecies ~ssociated Threats with the terrestrial portion of the mam archipelago of Strategies the Hawaiian Islands (eight major islands and Acknowledgements immediately surrounding islets). These islands have a <I total land area of 1,664,100 hectares (4,062,660 acres). Tables This terrestrial ecoregion excludes the Northwestern Maps &Figures Hawaiian Islands (belonging to Hawai'i coastal/marine The Hawaiian ecoregion contains highly diverse physiography. CPT Database ecoregion) and the surrounding marine environment. Appendices The Hawaiian High Islands Ecoregion lies within the Glossary Hawaiian Biogeographic Province, which encompasses Physiography Sources all of the above ecoregions and occupies the northern portion of the Oceanian Realm. The Hawaiian High Islands Ecoregion is marked by a very wide range of local physiographic settings. These Boundary include fresh massive volcanic shields and cinderlands reaching over 4000 m (13,000 ft) elevation; eroded, faceted topo- graphies on older The Hawaiian High Islands Ecoregion Boundary islands; high sea cliffs (ca 900 m [3,000 ft] in height); is defined by the TNC/NatureServe National raised coral plains ~ and amphitheater-headed Ecoregional Map. It is a modification ofBaile~'s . valley/ridge systems with alluvial/colluvial bottoms. Ecoregions of the United States. The World W1ldhfe Numerous freshwater stream systems are found The Hawaiian High Islands Ecore;Pon lies in Federation (WWF) recognizes four ecoregions for the the central north Pacific Ocean. -
Environmental Awareness and Conceptual Understanding Through a Pilot Sustainable Development Module
AC 2011-1917: FIRST-YEAR ENGINEERING STUDENTS’ ENVIRONMEN- TAL AWARENESS AND CONCEPTUAL UNDERSTANDING THROUGH A PILOT SUSTAINABLE DEVELOPMENT MODULE Nicole R. Weber, Purdue University She is a Postdoctoral Researcher in the School of Engineering Education at Purdue University. She received her B.S. degree in Ecology, Evolution and Behavior from the University of Minnesota, St. Paul. At the University of Massachusetts Boston, she received her Ph.D. in Environmental Biology with an emphasis in Science Education. Her current research is working in ”sustainable engineering” education, creating awareness of engineering as a ”caring” discipline. A discipline where engineers incorporate the ecological footprint into their design, keeping in mind related social and ecological impacts. Melissa Dyehouse, Purdue University Melissa Dyehouse is a Postdoctoral Research Associate at the Institute for P-12 Engineering Research and Learning (INSPIRE). She received her M.S.Ed. and Ph.D. in Educational Psychology from Purdue University with a focus on educational research methodology and assessment. Her research at INSPIRE focuses on the learning and teaching of engineering as a ”caring” discipline in the context of environmen- tal and ecological concerns. Constance A Harris, Purdue University She is a doctoral candidate in the College of Education at Purdue University. She received her B.S. degree in Political Science from the University of Illinois at Urbana-Champaign. In addition, she earned M.S. in Interdisciplinary Studies from DePaul University located in Chicago, Illinois, and a M.A. in Communication Studies from Purdue University Calumet located in Hammond, Indiana. Currently, she works as a research assistant in the School of Engineering Education at Purdue University. -
Long Term Deforestation Assessment in Jharkhand State, India: a Grid Based Geospatial Approach
Biological Forum – An International Journal 9(1): 183-188(2017) ISSN No. (Print): 0975-1130 ISSN No. (Online): 2249-3239 Long Term Deforestation Assessment in Jharkhand state, India: A grid based Geospatial Approach Firoz Ahmad* and Laxmi Goparaju* *Vindhyan Ecology and Natural History Foundation, Mirzapur, Uttar Pradesh, India. (Corresponding author: Laxmi Goparaju) (Received 15 March 2017, Accepted 18 June, 2017) (Published by Research Trend, Website: www.researchtrend.net) ABSTRACT: Forest is a fundamental component of the environment. Deforestation is caused by various anthropogenic factors, forest fire and fragmentation of large contiguous forests. Deforestation represents a global issue mostly caused by human influence and the forest of Jharkhand, India is not an exception as they have also been witnessing large scale deforestation. The aim of the present study is to identify deforestation using historical data for the year 1935 (Survey of India topographical maps of 1924–1935) and for the year of 2015 with Landsat -8 datasets in Jharkhand, India. To achieve this objective, the analysis focuses on grid (5 km*5 km) based assessment to detect long term change. The grid based analysis reveals forest percent in Jharkhand for the year 1935 and 2015 were roughly 49% and 23% respectively. The result shows 2596 forest grid for the year 1935 out of which 1372 forest grids were found present in the year 2015. 1224 forest grid (equivalent to 26% forest area) was lost during the span of 80 years. The analysis of remote sensing data in GIS domain and its derived product must be incorporated in forest conservation; management and planning which will certainly fetch better result in decision making support system. -
Ecosystem Services Generated by Fish Populations
AR-211 Ecological Economics 29 (1999) 253 –268 ANALYSIS Ecosystem services generated by fish populations Cecilia M. Holmlund *, Monica Hammer Natural Resources Management, Department of Systems Ecology, Stockholm University, S-106 91, Stockholm, Sweden Abstract In this paper, we review the role of fish populations in generating ecosystem services based on documented ecological functions and human demands of fish. The ongoing overexploitation of global fish resources concerns our societies, not only in terms of decreasing fish populations important for consumption and recreational activities. Rather, a number of ecosystem services generated by fish populations are also at risk, with consequences for biodiversity, ecosystem functioning, and ultimately human welfare. Examples are provided from marine and freshwater ecosystems, in various parts of the world, and include all life-stages of fish. Ecosystem services are here defined as fundamental services for maintaining ecosystem functioning and resilience, or demand-derived services based on human values. To secure the generation of ecosystem services from fish populations, management approaches need to address the fact that fish are embedded in ecosystems and that substitutions for declining populations and habitat losses, such as fish stocking and nature reserves, rarely replace losses of all services. © 1999 Elsevier Science B.V. All rights reserved. Keywords: Ecosystem services; Fish populations; Fisheries management; Biodiversity 1. Introduction 15 000 are marine and nearly 10 000 are freshwa ter (Nelson, 1994). Global capture fisheries har Fish constitute one of the major protein sources vested 101 million tonnes of fish including 27 for humans around the world. There are to date million tonnes of bycatch in 1995, and 11 million some 25 000 different known fish species of which tonnes were produced in aquaculture the same year (FAO, 1997). -
Ecological Engineering for Biodiversity Adaptation to Climate Change
LAND AND WATER Ecological engineering for biodiversity adaptation to climate change Background Managing contemporary environmental needs whilst ensuring Natural Resource Management (NRM) investment is future‐proofed to withstand climate change is a key challenge for environmental managers in the 21st century. To address this challenge, the Department of the Environment and the CSIRO are collaborating to identify and develop a new generation of climate‐ready ‘ecological engineering’ approaches. What is ecological engineering? The project defines ecological engineering as ‘the design, manipulation or construction of self‐sustaining ecosystems for the mutual benefit of humans and nature’. We use this term in place of ‘ecological restoration’, because restoring characteristics from pre‐existing communities may not be viable in a changing climate. Rather, we may need modified designs and approaches, informed by forecasting tools, to maximise future climate‐ resilience. Why would we need to engineer Australian ecosystems? Governments across Australia have invested billions of dollars in ecosystem restoration through national and state and territory Natural Resource Management (NRM) programs. These investments are occurring in an environment of accelerated climatic change. For example, significant ecological restoration is being undertaken in Australia’s southern agricultural zones to sequester carbon, restore landscape connectivity and habitat for native biodiversity, ameliorate salinisation and provide other ecosystem services. Climate projections -
Restoring Tropical Forests on Lands Mined for Bauxite: Examples from the Brazilian Amazon
Ecological Engineering 17 (2001) 219–239 www.elsevier.com/locate/ecoleng Restoring tropical forests on lands mined for bauxite: Examples from the Brazilian Amazon John A. Parrotta a,*, Oliver H. Knowles b a International Institute of Tropical Forestry, USDA Forest Ser6ice, P.O. Box 25000, Rı´o Piedras, PR 00928-5000, USA b C.P. 15, Santare´m, 68005.970 Para´, Brazil Accepted 19 August 2000 Abstract Restoring self-sustaining tropical forest ecosystems on surface mined sites is a formidable challenge that requires the integration of proven reclamation techniques and reforestation strategies appropriate to specific site conditions, including landscape biodiversity patterns. Restorationists working in most tropical settings are usually hampered by lack of basic information on the wide variety of native tree species that characterize the pre-disturbance forests, as well as insufficient understanding of the ecology of disturbance and natural recovery to design effective restoration programs. A notable exception to this is the forest restoration program developed since the early 1980s by a Brazilian bauxite mining company operating at Trombetas in Para´ State in central Amazonia. A systematic nursery and field research strategy was used to develop a reforestation program based on mixed plantings of more than 70 native old-growth forest tree species. This technique has been used to replant about 100 ha of deforested minelands each year over the past 15 years. Research in recent years has evaluated this approach and other, generally simpler, reforestation methods used at a smaller scale at this site. Post-plantation biodiversity development and other indicators of restoration success or sustainability were recorded. -
Ecological Engineering and Restoration of Eroded Muddy Coasts in South East Asia: Knowledge Gaps and Recommendations
sustainability Review Ecological Engineering and Restoration of Eroded Muddy Coasts in South East Asia: Knowledge Gaps and Recommendations Huynh Van Tien, Nguyen Tuan Anh , Nguyen Tan Phong * and Mai Le Minh Nhut Faculty of Environment and Labour Safety, Ton Duc Thang University, Ho Chi Minh City 700000, Vietnam; [email protected] (H.V.T.); [email protected] (N.T.A.); [email protected] (M.L.M.N.) * Correspondence: [email protected] Abstract: Ecological engineering (EE) was employed for developing strategies for stabilizing eroded muddy coasts (EMCs). However, there was a limited analysis of these EE strategies with respect to design, performance, and lessons learned. This study employed a critical review for addressing the limitations. There were four EE models designed with different restoration interventions for stabilizing EMCs. The models using active interventions have not been cost-effective in controlling erosion because the interventions failed to achieve their goals or were costly and unnecessary. Of the two passive intervention models, the one with structures constructed from onshore proved to be more cost-effective in terms of construction costs, the survival rate of transplanted seedlings, and levels of sea mud accumulation. Interventions with adequate consideration of the muddy coastal ecological processes and the ecological reasoning for the positioning of these interventions play a crucial role in stabilizing EMCs. A passive restoration model using gradually expanded interventions should be promoted in order to ensure sustainable management of EMCs in the future. Citation: Tien, H.V.; Tuan Anh, N.; Keywords: active restoration; muddy coasts; passive restoration; sea mud accumulation; transplantation Tan Phong, N.; Minh Nhut, M.L. -
A Study in Ecological Economics
The Process of Forest Conservation in Vanuatu: A Study in Ecological Economics Luca Tacconi December 1995 A Thesis Submitted for the Degree of Doctor of Philosophy at The University of New South Wales I hereby declare that this submission is my own work and that, to the best of my . knowledge and belief, it contains no material previously published or written by another person nor material which to a substantial extent has been accepted for the award of any other degree or diploma of a university or other institute of higher ·learning, except where due acknowledgment is made in the text of the thesis. Luca Tacconi School of Economics and Management University College The University of New South Wales 22 December 1995 With love to my parents Alfi.o and Leda (Con affetto dedico questa tesi ai miei genitori Alfio e Leda) IV Abstract The objective of this thesis is to develop an ecological economic framework for the assessment and establishment of protected areas (PAs) that are aimed at conserving forests and biodiversity. The framework is intended to be both rigorous and relevant to the decision-making process. Constructivism is adopted as the paradigm guiding the research process of the thesis, after firstly examining also positivist philosophy and 'post-normal' scientific methodology. The tenets of both ecological and environmental economics are then discussed. An expanded model of human behaviour, which includes facets derived from institutional economics and socioeconomics as well as aspects of neoclassical economics, is outlined. The framework is further developed by considering, from a contractarian view point, the implications of intergenerational equity for biodiversity conservation policies. -
IUCN ~ """~0 the World Conse!'Lation Union MC/) USP Library Catalopine-In-Publication Data
South Pacific Regional Environment Programme Proceedings of the Fourth South Pacific Conference on Nature Conservation and Protected Areas Volume II: Papers - Keynotes, Themes and Case Studies Held at Le Lagon Resort, Port Vila, Vanuatu 4- 12 September 1989 L/')C\1m . m e >o .,..__..,._ C\1 '::J IUCN _ _ ~_ """~0 The World Conse!'lation Union MC/) USP Library Catalopine-in-Publication Data South Pacific Conference on Nature Conservation and ProtectedAreas (4th : 1989 : Port Vila, Vanuatu) Proceedings of the Fourth South Pacific Conference on Nature Conser vation and Protected Areas, held at the Le Lagon Resort, Port Vila, Re puhlicofVanuatu, 14-16Septemher 1989. Volume II. • [Apia, Western Samoa] : SPREP, 1989. 155 p. : em. 1. Nature Conservation· Oceania· Congresses 2. Environmental prtection ·Oceania· Congresses I.South Pacific Regional Environment Programme II. Title QH77.03S6 333. 7' 16'0995 ISBN: 982-04-0026-0 Prepared for publication at: South Pacific Regional Environment Programme PO Box 240, Apia, Western Samoa. Printed by Commercial Print, Apia, Western Samoa. p 30 I 2.5C South Pacific Regional Environment Programme Proceedings of the Fourth South Pacific Conference on Nature Conservation and Protected Areas Volume II: Papers - Themes, Keynotes and Case Studies Held at the Le Lagon Resort Port Vila, Republic of Vanuatu 4- 12 September 1989 Foreword The Fourth South Pacific Conference on Nature Conservation and Protected Areas held in Port Vila, in 1989, continues the series of "National Parks and Reserves" conferences held in New Zealand (1975), Sydney, Australia (1979), and Apia, Western Samoa (1985). The decision was made at the Apia conference to change the name to its current title, to better reflect the importance of the wider issues of biological diversity conservation to the region. -
A Global Overview of Wetland and Marine Protected Areas on the World Heritage List
A GLOBAL OVERVIEW OF WETLAND AND MARINE PROTECTED AREAS ON THE WORLD HERITAGE LIST A Contribution to the Global Theme Study of World Heritage Natural Sites Prepared by Jim Thorsell, Renee Ferster Levy and Todd Sigaty Natural Heritage Programme lUCN Gland, Switzerland September 1997 WORLD CONSERVATION MONITORING CENTRE lUCN The World Conservation Union 530S2__ A GLOBAL OVERVIEW OF WETLAND AND MARINE PROTECTED AREAS ON THE WORLD HERITAGE LIST A Contribution to the Global Theme Study of Wodd Heritage Natural Sites Prepared by Jim Thorsell. Renee Ferster Levy and Todd Sigaty Natural Heritage Program lUCN Gland. Switzerland September 1997 Working Paper 1: Earth's Geological History - A Contextual Framework Assessment of World Heritage Fossil Site Nominations Working Paper 2: A Global Overview of Wetland and Marine Protected Areas on the World Heritage List Working Paper 3; A Global Overview of Forest Protected Areas on the World Heritage List Further volumes (in preparation) on biodiversity, mountains, deserts and grasslands, and geological features. Digitized by tine Internet Arciiive in 2010 witii funding from UNEP-WCIVIC, Cambridge littp://www.arcliive.org/details/globaloverviewof97glob . 31 TABLE OF CONTE>rrS PAGE I. Executive Summary (e/f) II. Introduction 1 III. Tables & Figures Table 1 . Natural World Heritage sites with primary wetland and marine values 1 Table 2. Natural World Heritage sites with secondary wetland and marine values 12 Table 3. Natural World Heritage sites inscribed primarily for their freshwater wetland values 1 Table 4. Additional natural World Heritage sites with significant freshwater wetland values 14 Tables. Natural World Heritage sites with a coastal/marine component 15 Table 6. -
A Global Overview of Tropical Marine, Coastal and Small Island Ecosystems and the World Heritage List
coev ^Ht^e- kiCMC ^^JCs Q( Discussion Paper A Global Overview of Tropical Marine, Coastal and Small Island Ecosystems and the World Heritage List Prepared by Edmund Green, UNEP-WCMC June 2001 with assistance from Jerry Harrison, Javier Baltran, Lucy Conway, Sergio Martins and Mark Spalding UNEP WCMC Discussion paper: A Global Oven'iew of Tropical Marine, Coastal and Small Island Ecosystems and the World Heritage List Table of Contents List Of Tables, Figures And Maps 3 Introduction 4 An Overview of the World Heritage Convention 4 What the Convention contains 4 How the Convention works 4 The criteria for selection 4 Protecting endangered sites 5 Background to this report 5 Tropical Marine, Coastal And Small Island Ecosystems In World Heritage Sites 7 Working definition of tropical, coastal and small island ecosystems 7 Present coverage under the convention 7 Future coverage under the Convention 8 Sites in danger 8 Present coverage of tropical marine, coastal and small island ecosystems under other international conventions and programmes 8 The relative distribution and size of tropical marine, coastal and small island World Heritage Sites ... 10 The Distribution of existing World Heritage Sites in Relation to Important Tropical Marine Ecosystems and Species 13 Coral Reefs 13 Mangroves 13 Marine Turtles 14 Seagrasses 14 Data Sources 15 Discussion paper: A Global Ch'en'iew of Tropical Marine, Coastal and Small Island Ecosystems and the World Heritage List List Of Tables, Figures And Maps Table Title Page Table 1 Tropical marine, coastal and small island ecosystems sites currently on the World 16 Heritage list Table 2 Tropical marine, coastal and small island ecosystems sites currently included either 20 in a State Party potential World Heritage list or which have been nominated but not inscribed.