The Concept of Organisms As Ecosystem Engineers Ten Years On: Progress, Limitations, and Challenges
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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. -
Evidence from Fossil Crustaceans in Cold-Water C
Klompmaker et al. BMC Evolutionary Biology (2016) 16:132 DOI 10.1186/s12862-016-0694-0 RESEARCH ARTICLE Open Access Evolution of body size, vision, and biodiversity of coral-associated organisms: evidence from fossil crustaceans in cold- water coral and tropical coral ecosystems Adiël A. Klompmaker1,2,3*, Sten L. Jakobsen4 and Bodil W. Lauridsen5 Abstract Background: Modern cold-water coral and tropical coral environments harbor a highly diverse and ecologically important macrofauna of crustaceans that face elevated extinction risks due to reef decline. The effect of environmental conditions acting on decapod crustaceans comparing these two habitats is poorly understood today and in deep time. Here, we compare the biodiversity, eye socket height as a proxy for eye size, and body size of decapods in fossil cold-water and tropical reefs that formed prior to human disturbance. Results: We show that decapod biodiversity is higher in fossiltropicalreefsfromTheNetherlands,Italy,and Spain compared to that of the exceptionally well-preserved Paleocene (Danian) cold-water reef/mound ecosystem from Faxe (Denmark), where decapod diversity is highest in a more heterogeneous, mixed bryozoan-coral habitat instead of in coral and bryozoan-dominated facies. The relatively low diversity at Faxe was not influenced substantially by the preceding Cretaceous/Paleogene extinction event that is not apparent in the standing diversity of decapods in our analyses, or by sampling, preservation, and/or a latitudinal diversity gradient. Instead, the lower availability of food and fewer hiding places for decapods may explain this low diversity. Furthermore, decapods from Faxe are larger than those from tropical waters for half of the comparisons, which may be caused by a lower number of predators, the delayed maturity, and the increased life span of crustaceans in deeper, colder waters. -
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). -
Abiotic Stresses and Its Management in Agriculture Assistant Professor
Abiotic Stresses And Its Management In Agriculture D.Vijayalakshmi Assistant Professor, Department of Crop Physiology, TNAU, Coimbatore Introduction In today‘s climate change sceranios, crops are exposed more frequently to episodes of abiotic stresses such as drought, salinity, elevated temperature, submergence and nutrient deficiencies. These stresses limit crop production. In recent years, advances in physiology, molecular biology and genetics have greatly improved our understanding of crops response to these stresses and the basis of varietal differences in tolerance. This chapter will clearly define the different abiotic stresses and their impacts on agricultural productivity. Stress – Definitions (i) Physical terms Stress is defined as the force per unit area acting upon a material, inducing strain and leading to dimensional change. More generally, it is used to describe the impact of adverse forces, and this is how it is usually applied to biological systems. (ii) Biological terms In the widest biological sense, stress can be any factor that may produce an adverse effect in individual organisms, populations or communities. Stress is also defined as the overpowering pressure that affects the normal functions of individual life or the conditions in which plants are prevented from fully expressing their genetic potential for 361 growth, development and reproduction (Levitt, 1980; Ernst, 1993). (iii) Agricultural terms Stress is defined as a phenomenon that limits crop productivity or destroys biomass (Grime, 1979). Classification Of Stresses It has become traditional for ecologists, physiologists, and agronomists to divide stresses experienced by plants into two major categories: biotic and abiotic. Biotic stresses originate through interactions between organisms, while abiotic stresses are those that depend on the interaction between organisms and the physical environment. -
Host-Plant Genotypic Diversity Mediates the Distribution of an Ecosystem Engineer
University of Tennessee, Knoxville TRACE: Tennessee Research and Creative Exchange Supervised Undergraduate Student Research Chancellor’s Honors Program Projects and Creative Work Spring 4-2006 Genotypic diversity mediates the distribution of an ecosystem engineer Kerri Margaret Crawford University of Tennessee-Knoxville Follow this and additional works at: https://trace.tennessee.edu/utk_chanhonoproj Recommended Citation Crawford, Kerri Margaret, "Genotypic diversity mediates the distribution of an ecosystem engineer" (2006). Chancellor’s Honors Program Projects. https://trace.tennessee.edu/utk_chanhonoproj/949 This is brought to you for free and open access by the Supervised Undergraduate Student Research and Creative Work at TRACE: Tennessee Research and Creative Exchange. It has been accepted for inclusion in Chancellor’s Honors Program Projects by an authorized administrator of TRACE: Tennessee Research and Creative Exchange. For more information, please contact [email protected]. • f" .1' I,'r· ... 4 ....., ' 1 Genotypic diversity mediates the distribution of an ecosystem engineer 2 3 4 5 6 7 Kerri M. Crawfordl, Gregory M. Crutsinger, and Nathan J. Sanders2 8 9 10 11 Department 0/Ecology and Evolutionary Biology, University o/Tennessee, Knoxville, Tennessee 12 37996 13 14 lAuthor for correspondence: email: [email protected]. phone: (865) 974-2976,/ax: (865) 974 15 3067 16 2Senior thesis advisor 17 18 19 20 21 22 23 24 25 26 27 28 29 30 12 April 2006 1 1 Abstract 2 Ecosystem engineers physically modify environments, but much remains to be learned about 3 both their effects on community structure and the factors that predict their occurrence. In this 4 study, we used experiments and observations to examine the effects of the bunch galling midge, 5 Rhopalomyia solidaginis, on arthropod species associated with Solidago altissima. -
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 -
Occupied and Abandoned Structures from Ecosystem Engineering Differentially Facilitate Stream Community Colonization 1, 1 1 BENJAMIN B
Occupied and abandoned structures from ecosystem engineering differentially facilitate stream community colonization 1, 1 1 BENJAMIN B. TUMOLO , LINDSEY K. ALBERTSON, WYATT F. CROSS, 2 3 MELINDA D. DANIELS, AND LEONARD S. SKLAR 1Department of Ecology, Montana State University, P.O. Box 173460, Bozeman, Montana 59717 USA 2Stroud Water Research Center, 970 Spencer Road, Avondale, Pennsylvania 19311 USA 3Department of Geography, Planning and Environment, Concordia University, 1455 De Maisonneuve Boulevard West, Montreal, Quebec, Canada Citation: Tumolo, B. B., L. K. Albertson, W. F. Cross, M. D. Daniels, and L. S. Sklar. 2019. Occupied and abandoned structures from ecosystem engineering differentially facilitate stream community colonization. Ecosphere 10(5):e02734. 10.1002/ecs2.2734 Abstract. Ecosystem engineers transform habitats in ways that facilitate a diversity of species; however, few investigations have isolated short-term effects of engineers from the longer-term legacy effects of their engineered structures. We investigated how initial presence of net-spinning caddisflies (Hydropsychidae) and their structures that provide and modify habitat differentially influence benthic community coloniza- tion in a headwater stream by conducting an in situ experiment that included three treatments: (1) initial engineering organism with its habitat modification structure occupied (hereafter caddisfly); (2) initial habi- tat modification structure alone (hereafter silk); and (3) a control with the initial absence of both engineer and habitat modification structure (hereafter control). Total invertebrate colonization density and biomass was higher in caddisfly and silk treatments compared to controls (~25% and 35%, respectively). However, finer-scale patterns of taxonomy revealed that density for one of the taxa, Chironomidae, was ~19% higher in caddisfly compared to silk treatments. -
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. -
Optimal Control of an Invasive Ecosystem Engineer by David Kling (Presenter), University of California, Davis James Sanchirico
Optimal Control of an Invasive Ecosystem Engineer By David Kling (presenter), University of California, Davis James Sanchirico, University of California, Davis Alan Hastings, University of California, Davis Managing natural systems in the face of global anthropogenic change poses an enormous challenge. Human-mediated changes can greatly complicate resource management by rendering ecosystems unable to return to their natural condition (hysteresis) or by shifting the ecosystem to an entirely new and possibly less beneficial state (regime shift) (Beisner et al. 2003; Scheffer and Carpenter 2003). One common and pervasive example of a complex management problem is the control of invasive introduced species. It is now well-known that nonnative species can have strong negative impacts on ecosystem function and services and on native biodiversity (Chapin et al. 2000; Olson 2006). Researchers have devoted considerable effort towards understanding the economics of invasion control. Previous theoretical work has identified circumstances where the eradication of an invader is optimal (Olson and Roy 2008). Recent work has also investigated the spatial-dynamics of control and characterized how landscape features can drive optimal policies (Epanchin-Niell and Wilen 2009). A key finding from this research is that early intervention, when the population of the invader is small, is a pivotal determinant of the cost- effectiveness of eradication. Despite this progress, a persistent gap in theoretical work by economists on invasions has been left by a reliance on simple models of invader population dynamics that ignore a number of ecological processes that can accompany invasions and that may call for substantially different control strategies. Ecosystem engineers are organisms that have significant impacts on ecosystems through changing key physical characteristics of the system (Cuddington et al.