Bioindicator-Based Method for Valuing Marine Ecosystem Services
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Biocultural Indicators to Support Locally Led Environmental Management and Monitoring
Copyright © 2019 by the author(s). Published here under license by the Resilience Alliance. DeRoy, B. C., C. T. Darimont, and C. N. Service. 2019. Biocultural indicators to support locally led environmental management and monitoring. Ecology and Society 24(4):21. https://doi.org/10.5751/ES-11120-240421 Synthesis Biocultural indicators to support locally led environmental management and monitoring Bryant C. DeRoy 1,2, Chris T. Darimont 1,2 and Christina N. Service 1,2,3 ABSTRACT. Environmental management (EM) requires indicators to inform objectives and monitor the impacts or efficacy of management practices. One common approach uses “functional ecological” indicators, which are typically species whose presence or abundance are tied to functional ecological processes, such as nutrient productivity and availability, trophic interactions, and habitat connectivity. In contrast, and used for millennia by Indigenous peoples, biocultural indicators are rooted in local values and place- based relationships between nature and people. In many landscapes today where Indigenous peoples are reasserting sovereignty and governance authority over natural resources, the functional ecological approach to indicator development does not capture fundamental values and ties to the natural world that have supported social-ecological systems over the long term. Accordingly, we argue that the development and use of biocultural indicators to shape, monitor, and evaluate the success of EM projects will be critical to achieving ecological and social sustainability today. We have provided a framework composed of criteria to be considered when selecting and applying meaningful and efficacious biocultural indicators among the diverse array of potential species and values. We used a case study from a region now referred to as coastal British Columbia, Canada, to show how the suggested application of functional ecological indicators by the provincial government created barriers to the development of meaningful cogovernance. -
Do We Need to Use Bats As Bioindicators?
biology Perspective Do We Need to Use Bats as Bioindicators? Danilo Russo * , Valeria B. Salinas-Ramos , Luca Cistrone, Sonia Smeraldo, Luciano Bosso * and Leonardo Ancillotto Wildlife Research Unit, Dipartimento di Agraria, Università degli Studi di Napoli Federico II, Via Università, 100, 80055 Portici, Italy; [email protected] (V.B.S.-R.); [email protected] (L.C.); [email protected] (S.S.); [email protected] (L.A.) * Correspondence: [email protected] (D.R.); [email protected] (L.B.) Simple Summary: Bioindicators are organisms that react to the quality or characteristics of the environment and their changes. They are vitally important to track environmental alterations and take action to mitigate them. As choosing the right bioindicators has important policy implications, it is crucial to select them to tackle clear goals rather than selling specific organisms as bioindicators for other reasons, such as for improving their public profile and encourage species conservation. Bats are a species-rich mammal group that provide key services such as pest suppression, pollination of plants of economic importance or seed dispersal. Bats show clear reactions to environmental alterations and as such have been proposed as potentially useful bioindicators. Based on the rel- atively limited number of studies available, bats are likely excellent indicators in habitats such as rivers, forests, and urban sites. However, more testing across broad geographic areas is needed, and establishing research networks is fundamental to reach this goal. Some limitations to using bats as bioindicators exist, such as difficulties in separating cryptic species and identifying bats in flight from their calls. -
Assessing Biological Integrity in Running Waters a Method and Its Rationale
Assessing Biological Integrity in Running Waters A Method and Its Rationale James R. Karr Kurt D. Fausch Paul L. Angermeier Philip R. Yant Isaac J. Schlosser Jordan Creek ---------------- ] Excellent !:: ~~~~~~~~~;~~;~~ ~ :: ,. JPoor --------------- 111 1C tE 2A 28 20 3A SO 3E 4A 48 4C 40 4E Station Illinois Natural History Survey Special Publication 5 September 1986 Printed by authority of the State of Illinois Illinois Natural History Survey 172 Natural Resources Building 607 East Peabody Drive Champaign, Illinois 61820 The Illinois Natural History Survey is pleased to publish this report and make it available to a wide variety of potential users. The Survey endorses the concepts from which the Index of Biotic Integrity was developed but cautions, as the authors are careful to indicate, that details must be tailored to lit the geographic region in which the Index is to be used. Glen C. Sanderson, Chair, Publications Committee, Illinois Natural History Survey R. Weldon Larimore of the Illinois Natural History Survey took the cover photos, which show two reaches ofJordan Creek in east-central Illinois-an undisturbed site and a site that shows the effects of grazing and agricultural activity. Current affiliations of the authors are listed below: James R. Karr, Deputy Director, Smithsonian Tropical Research Institute, Balboa, Panama Kurt D. Fausch, Department of Fishery and Wildlife Biology, Colorado State University, Fort Collins Paul L. Angermeier, Department of Fisheries and Wildlife Sciences, Virginia Polytechnic Institute and State University, Blacksburg Philip R. Yant, Museum of Zoology, University of Michigan, Ann Arbor Isaac J. Schlosser, Department of Biology, University of North Dakota, Grand Forks VDP-1-3M-9-86 ISSN 0888-9546 Assessing Biological Integrity in Running Waters A Method and Its Rationale James R. -
Urban Areas Have Ecological Integrity(3-8)
Can urban areas have ecological integrity? Reed F. Noss INTRODUCTION The question of whether urban areas can offer a habitat and wildlife within and around urban areas, semblance of the natural world – a vestige (at least) where most people live. But, if we embark on this of ecological integrity – is an important one to many venture, how do we know if we are succeeding? people who live in these areas. As more and more of There are both social and biological measures of the world becomes urbanized, this question becomes success. The social measures include increased highly relevant to the broader mission of maintain- awareness of and appreciation for native wildlife ing the Earth’s biological diversity. and healthy ecosystems. The biological measures are Most people, especially when young, are attracted the subject of my talk this morning; I will focus on to the natural world and living things, Ed Wilson adaptation of the ecological integrity concept to called this attraction “biophilia.” And entire books urban and suburban areas and the role of connectiv- have been written about it – one, for example, by ity (i.e. wildlife corridors) in promoting ecological Steve Kellert, who also appears in this morning’s integrity. program. Personally, I share Wilson’s speculation that biophilia has a genetic basis. Some people are Urban Ecological Integrity biophilic than others. This tendency is very likely Ecological integrity is what we might call an heritable, although it certainly is influenced by the “umbrella concept,” embracing all that is good and environment, particularly by early experiences. My right in ecosystems. -
2.0 Managing Native Mesic Forest Remnants
2.0 MANAGING NATIVE MESIC FOREST REMNANTS Photo by Amy Tsuneyoshi 2.1 RESTORATION CONCEPTS AND PRINCIPLES The word restore means “to bring back…into a former or original state” (Webster’s New Collegiate Dictionary 1977). For the purposes of this book, forest restoration assumes that some semblance of a native forest remains and the restoration process is one of removing the causes for that degradation and returning the forest back to a former intact native state. More formally, restoration is defined as: The return of an ecosystem to its historical trajectory by removing or modifying a specific disturbance, and thereby allowing ecological processes to bring about an independent recovery (Society for Ecological Restoration International Science and Policy Working Group 2004). The term native integrity used throughout this book refers to this continuum of intactness. An area very high in native integrity is fully intact. James Karr (1996) defines biological integrity as: The ability to support and maintain a balanced, integrated, adaptive biological system having the full range of elements (genes, species, and assemblages) and processes (mutation, demography, biotic interactions, nutrient and energy dynamics, and metapopulation processes) expected in the natural habitat of a region. This standard of biological integrity is admittedly beyond the reach of many restoration projects given some of the irreversible effects of invasive plants and animals as well as a lack of knowledge of how an ecosystem worked in the first place. Nonetheless, the goal of a restoration effort should be a restored native area that is healthy, viable, and self-sustaining requiring a minimum amount of active management in the long-term. -
Assessment of the Biological Integrity of the Native Vegetative Community in a Surface Flow Constructed Wetland Treating Industrial Park Contaminants
OnLine Journal of Biological Sciences 7 (1): 21-29, 2007 ISSN 1608-4217 © 2007 Science Publications Assessment of The Biological Integrity of The Native Vegetative Community In A Surface Flow Constructed Wetland Treating Industrial Park Contaminants 1C. C. Galbrand, 2A. M. Snow, 2A. E. Ghaly and 1R. Côté 1School of Resources and Environmental Studies 2Department of Process Engineering and Applied Sciences Dalhousie University, Halifax, Nova Scotia, Canada, B3J 2X4 Abstract: A study was conducted to evaluate the biological integrity of a constructed wetland receiving landfill leachate and stormwater runoff from the Burnside Industrial Park, Dartmouth, Nova Scotia. The biological integrity of the constructed wetland was tested in the second growing season using vegetative community monitoring. The metrics analyzed were species diversity, species heterogeneity (dominance) and exotic/invasive species abundance. There was no significant difference in the plant species diversity between the constructed wetland and the reference site. However, the constructed wetland supported a higher plant species richness than the reference site. The top three species in the constructed wetland were tweedy’s rush (Juncus brevicaudatus), soft rush (Juncus effusus) and fowl mannagrass (Glyceria striata). In total, these three species occupied 46.4% of the sampled population. The top three species in the reference site were soft rush (Juncus effusus), sweetgale (Myrica gale) and woolgrass (Scirpus cyperinus). In total, these three species occupied a more reasonable 32.6% of the sampled population. The reference site supported greater biological integrity as it had greater heterogeneity and a smaller abundance of exotic and invasive species compared to the constructed wetland (3.8% versus 10.7%). -
Ascendency As Ecological Indicator for Environmental Quality Assessment at the Ecosystem Level: a Case Study
Hydrobiologia (2006) 555:19–30 Ó Springer 2006 H. Queiroga, M.R. Cunha, A. Cunha, M.H. Moreira, V. Quintino, A.M. Rodrigues, J. Seroˆ dio & R.M. Warwick (eds), Marine Biodiversity: Patterns and Processes, Assessment, Threats, Management and Conservation DOI 10.1007/s10750-005-1102-8 Ascendency as ecological indicator for environmental quality assessment at the ecosystem level: a case study J. Patrı´ cio1,*, R. Ulanowicz2, M. A. Pardal1 & J. C. Marques1 1IMAR- Institute of Marine Research, Department of Zoology, Faculty of Sciences and Technology, University of Coimbra, 3004-517, Coimbra, Portugal 2Chesapeake Biological Laboratory, Center for Environmental and Estuarine Studies, University of Maryland, Solomons, Maryland, 20688-0038, USA (*Author for correspondence: E-mail: [email protected]) Key words: network analysis, ascendency, eutrophication, estuary Abstract Previous studies have shown that when an ecosystem consists of many interacting components it becomes impossible to understand how it functions by focussing only on individual relationships. Alternatively, one can attempt to quantify system behaviour as a whole by developing ecological indicators that combine numerous environmental factors into a single value. One such holistic measure, called the system ‘ascen- dency’, arises from the analysis of networks of trophic exchanges. It deals with the joint quantification of overall system activity with the organisation of the component processes and can be used specifically to identify the occurrence of eutrophication. System ascendency analyses were applied to data over a gradient of eutrophication in a well documented small temperate intertidal estuary. Three areas were compared along the gradient, respectively, non eutrophic, intermediate eutrophic, and strongly eutrophic. Values of other measures related to the ascendency, such as the total system throughput, development capacity, and average mutual information, as well as the ascendency itself, were clearly higher in the non-eutrophic area. -
ECOLOGICAL FOOTPRINT AN]) Appropriathd CARRYING CAPACITY: a TOOL for PLANNING TOWARD SUSTAINABILITY
ECOLOGICAL FOOTPRINT AN]) APPROPRIAThD CARRYING CAPACITY: A TOOL FOR PLANNING TOWARD SUSTAINABILITY by MATHIS WACKERNAGEL Dip!. Ing., The Swiss Federal Institute of Technology, ZUrich, 1988 A THESIS SUBMITTED IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF DOCTOR OF PHILOSOPHY in THE FACULTY OF GRADUATE STUDIES (School of Community and Regional Planning) We accept this thesis as conforming to the r ired standard THE UNIVERSITY OF BRITISH COLUMBIA October 1994 © Mathis Wackernagel, 1994 advanced In presenting this thesis in partial fulfilment of the requirements for an Library shall make it degree at the University of British Columbia, I agree that the that permission for extensive freely available for reference and study. I further agree copying of this thesis for scholarly purposes may be granted by the head of my department or by his or her representatives. It is understood that copying or publication of this thesis for financial gain shall not be allowed without my written permission. (Signature) ejb’i’t/ Pios-ii’ii &toof of C iwivry Gf (i l r€dva k hi di’e The University of British Columbia Vancouver, Canada Date O 6) ) DE-6 (2/88) ABSThACT There is mounting evidence that the ecosystems of Earth cannot sustain current levels of economic activity, let alone increased levels. Since some consume Earth’s resources at a rate that will leave little for future generations, while others still live in debilitating poverty, the UN’s World Commission on Environment and Economic Development has called for development that is sustainable. The purpose of this thesis is to further develop and test a planning tool that can assist in translating the concern about the sustainability crisis into public action. -
Using Indicators of Biotic Integrity for Assessment of Stream Condition
Michigan Technological University Digital Commons @ Michigan Tech Dissertations, Master's Theses and Master's Dissertations, Master's Theses and Master's Reports - Open Reports 2014 USING INDICATORS OF BIOTIC INTEGRITY FOR ASSESSMENT OF STREAM CONDITION Stephanie A. Ogren Michigan Technological University Follow this and additional works at: https://digitalcommons.mtu.edu/etds Part of the Biology Commons, and the Ecology and Evolutionary Biology Commons Copyright 2014 Stephanie A. Ogren Recommended Citation Ogren, Stephanie A., "USING INDICATORS OF BIOTIC INTEGRITY FOR ASSESSMENT OF STREAM CONDITION", Dissertation, Michigan Technological University, 2014. https://doi.org/10.37099/mtu.dc.etds/753 Follow this and additional works at: https://digitalcommons.mtu.edu/etds Part of the Biology Commons, and the Ecology and Evolutionary Biology Commons USING INDICATORS OF BIOTIC INTEGRITY FOR ASSESSMENT OF STREAM CONDITION By Stephanie A. Ogren A DISSERTATION Submitted in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY In Biological Sciences MICHIGAN TECHNOLOGICAL UNIVERSITY 2014 This dissertation has been approved in partial fulfillment of the requirements for the Degree of DOCTOR OF PHILOSOPHY in Biological Sciences Department of Biological Sciences Dissertation Advisor: Dr. Casey J Huckins Committee Member: Dr. Rodney A. Chimner Committee Member: Dr. Amy M. Marcarelli Committee Member: Dr. Eric B. Snyder Department Chair: Dr. Chandrashekhar Joshi Table of Contents Preface ............................................................................................................................................ -
Final Policy on Biological Assessments and Criteria
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON, D.C. 20460 OFFICEOF WATER MEMORANDUM SUBJECT: Final Policy on Biological Assessments and Criteria Text Rick Brandes, Chief Water Quality and Industrial Permits Branch (EN-336) TO: Regional Permits Branch Chiefs (I-X) I have enclosed for your information and use a copy of the recently issued "Policy on Biological Assessments and Criteria". This policy was signed by Tudor Davies on June 19, 1991. The content of the policy is also stated in the Technical Support Document for Water Quality-based Toxics Control. One aspect of the policy expresses that water quality standards are to be independently applied. This means that any single assessment method (chemical criteria, toxicity testing, or biocriteria) can provide conclusive evidence that water quality standards are not attained. Apparent conflicts between the three methods should be rare. They can occur because each assessment method is sensitive to different types and ranges of impacts. Therefore, a demonstration of water quality standards nonattain- ment using one assessment method does not necessarily require confirmation with a second method; nor can the failure of a second method to confirm impact, by itself, negate the results of the initial assessment. If you have any questions about the policy, please call Jim Pendergast at FTS 475-9536 or Kathy Smith at FTS 465-9521. Attachment UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON. D.C. 20460 Text MEMORANDUM Text SUBJECT: Transmittal of Final Policy on Biological Assessments and Criteria FROM: Tudor T. Davies, Director Office of Science and Technology (WH-551) TO: Water Management Division Directors Regions I-X Attached is EPA's "Policy on the Use of Biological Assessments and Criteria in the Water Quality Program" (Attachment A): This policy is a significant step toward addressing all pollution problems within a watershed. -
6 Developing Metrics and Indexes of Biological Integrity
United States Environmental Office of Water EPA 822-R-02-016 Protection Agency Washington, DC 20460 March 2002 Methods for evaluating wetland condition #6 Developing Metrics and Indexes of Biological Integrity United States Environmental Office of Water EPA 822-R-02-016 Protection Agency Washington, DC 20460 March 2002 Methods for evaluating wetland condition #6 Developing Metrics and Indexes of Biological Integrity Major Contributors Natural Resources Conservation Service, Wetland Science Institute Billy M. Teels Oregon State University Paul Adamus Prepared jointly by: The U.S. Environmental Protection Agency Health and Ecological Criteria Division (Office of Science and Technology) and Wetlands Division (Office of Wetlands, Oceans, and Watersheds) United States Environmental Office of Water EPA 822-R-02-016 Protection Agency Washington, DC 20460 March 2002 Notice The material in this document has been subjected to U.S. Environmental Protection Agency (EPA) technical review and has been approved for publication as an EPA document. The information contained herein is offered to the reader as a review of the “state of the science” concerning wetland bioassessment and nutrient enrichment and is not intended to be prescriptive guidance or firm advice. Mention of trade names, products or services does not convey, and should not be interpreted as conveying official EPA approval, endorsement, or recommendation. Appropriate Citation U.S. EPA. 2002. Methods for Evaluating Wetland Condition: Developing Metrics and Indexes of Biological Integrity. Office of Water, U.S. Environmental Protection Agency, Washington, DC. EPA-822-R-02-016. Acknowledgments EPA acknowledges the contributions of the following people in the writing of this module: Billy M. -
Bioindicator
Bioindicator INTRODUCTION A bioindicator is any species (an indicator species) or group of species whose function, population, or status can reveal the qualitative status of the environment. For example, copepods and other small water crustaceans that are present in many water bodies can be monitored for changes (biochemical, physiological, or behavioural) that may indicate a problem within their ecosystem. Bioindicators can tell us about the cumulative effects of different pollutants in the ecosystem and about how long a problem may have been present, which physical and chemical testing cannot. A biological monitor or biomonitor is an organism that provides quantitative information on the quality of the environment around it. Therefore, a good biomonitor will indicate the presence of the pollutant and can also be used in an attempt to provide additional information about the amount and intensity of the exposure. A biological indicator is also the name given to a process for assessing the sterility of an environment through the use of resistant microorganism strains (eg. Bacillus or Geobacillus). Biological indicators can be described as the introduction of a highly resistant microorganisms to a given environment before sterilization, tests are conducted to measure the effectiveness of the sterilization processes. As biological indicators use highly resistant microorganisms, any sterilization process that renders them inactive will have also killed off more common, weaker pathogens. The advantages associated with using Bioindicators are as follows: (a) Biological impacts can be determined. (b) To monitor synergetic and antagonistic impacts of various pollutants on a creature. (c) Early stage diagnosis as well as harmful effects of toxins to plants, as well as human beings, can be monitored.