Non-Native Invasive Species
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What Characteristics Do All Invasive Species Share That Make Them So
Invasive Plants Facts and Figures Definition Invasive Plant: Plants that have, or are likely to spread into native or minimally managed plant systems and cause economic or environmental harm by developing self-sustaining populations and becoming dominant or disruptive to those systems. Where do most invasive species come from? How do they get here and get started? Most originate long distances from the point of introduction Horticulture is responsible for the introduction of approximately 60% of invasive species. Conservation uses are responsible for the introduction of approximately 30% of invasive species. Accidental introductions account for about 10%. Of all non-native species introduced only about 15% ever escape cultivation, and of this 15% only about 1% ever become a problem in the wild. The process that leads to a plant becoming an invasive species, Cultivation – Escape – Naturalization – Invasion, may take over 100 years to complete. What characteristics make invasive species so successful in our environment? Lack predators, pathogens, and diseases to keep population numbers in check Produce copious amounts of seed with a high viability of that seed Use successful dispersal mechanisms – attractive to wildlife Thrive on disturbance, very opportunistic Fast-growing Habitat generalists. They do not have specific or narrow growth requirements. Some demonstrate alleleopathy – produce chemicals that inhibit the growth of other plants nearby. Have longer photosynthetic periods – first to leaf out in the spring and last to drop leaves in autumn Alter soil and habitat conditions where they grow to better suit their own survival and expansion. Why do we care? What is the big deal? Ecological Impacts Impacting/altering natural communities at a startling rate. -
Fact Sheet on Health and Biodiversity
Living in harmony with nature Health and Biodiversity We rely on biodiversity to stay healthy. Biodiversity sustains our food supply, is a source of medicines, and supports the provision of clean air and fresh water while also contributing to economic development, cultural and spiritual enrichment. It is now also widely recognized that biodiversity is affected by climate change, with negative consequences for human well-being, but biodiversity, through the ecosystem services it supports, also makes an important contribution to both climate change mitigation and adaptation. As all people require freedom from illness as well as social, emotional, physical, spiritual and cultural well-being, we cannot have healthy societies without biodiversity. Changes to biodiversity can have severe and unpredictable effects on the health of all living things, including people. Clearing new land, for example, can bring people into closer contact with wildlife that may transmit their diseases to humans and also promote the spread of disease from humans to animals. It may also reduce populations of predators that hold disease-carrying organisms in check. In addition, clearing of land may bring about the loss of plants and other organisms useful in medical research or that may contain substances used as medicines. People in developing countries face particularly heavy health burdens from a loss of biodiversity, with impacts on food supply and quality, medicines, and cultural and religious values. It has been estimated that approximately 80% of the world’s population from developing countries rely mainly on traditional medicines derived from plants and that 25% of prescriptions dispensed in United States pharmacies contained plant extracts or active ingredients derived from plants. -
A Survey of the Nation's Lakes
A Survey of the Nation’s Lakes – EPA’s National Lake Assessment and Survey of Vermont Lakes Vermont Agency of Natural Resources Department of Environmental Conservation - Water Quality Division 103 South Main 10N Waterbury VT 05671-0408 www.vtwaterquality.org Prepared by Julia Larouche, Environmental Technician II January 2009 Table of Contents List of Tables and Figures........................................................................................................................................................................... ii Introduction................................................................................................................................................................................................. 1 What We Measured..................................................................................................................................................................................... 4 Water Quality and Trophic Status Indicators.......................................................................................................................................... 4 Acidification Indicator............................................................................................................................................................................ 4 Ecological Integrity Indicators................................................................................................................................................................ 4 Nearshore Habitat Indicators -
Food Web Invaders
TEACHER LESSON PLAN Food Web Invaders Grade Length Subjects/strands Topics 4th–8th grade 20–30 minutes Discover how a food Observation, applica- web works by making tion, comparing similari- a live model of biotic ties and differences, gen- components, using the eralization, kinesthetic people in your class. concept development, Then explore how an psycho-motor develop- invasive species disrupts ment that balance. BACKGROUND INTRODUCTION Students will have been introduced to the idea of an ecosystem, and the basic relationships in an ecosys- In this fun, active-learning, game about food webs, tem such as producers and consumers, herbivores and each student is assigned to be a plant or animal that carnivores, predator/prey pairs, and some of the inter- can be found in aquatic ecosystems. Then, they learn relationships of their behavior and adaptations. Middle about the relationships between organisms as they pass school students will have been introduced to the idea of a ball of yarn between students (organisms) that have a limiting factors, and later the idea of carrying capac- predator/prey relationship. As the ball of yarn unravels ity. Students will also be familiar with the concept of a and the string is stretched between the many predator/ food chain with a variety of trophic levels. At the inter- prey relationships in the room, the large and complex mediate level, this could include videos, field activities food web network is reveals visually and symbolically and artwork, as well as reading and writing activities in the room. In the final step, an invasive species is from student magazines and textbooks. -
Assessing Ecosystem Health D.J
REVIEWS Assessing ecosystem health D.J. Rapport, R. Costanza and A.J. McMichael here is now abundant evi- Evaluating ecosystem health in relation to health in terms of ‘system organiz- dence that many human- the ecological, economic and human ation, resilience and vigor, as well dominated ecosystems, in- health spheres requires integrating human as the absence of signs of ecosys- Tcluding various biophysical values with biophysical processes, an tem distress24. The definition also systems at regional and global lev- integration that has been explicitly includes the presence of essential els, have become highly stressed avoided by conventional science. The field functions and key attributes that and dysfunctional1. The ‘services’ is advancing with the articulation of the sustain life systems (Box 1). provided by these ecosystems are linkages between human activity, regional A healthy ecosystem is defined extremely important to human wel- and global environmental change, as being ‘stable and sustainable’; fare2–5. As stressed ecosystems reduction in ecological services and the maintaining its organization and have become highly degraded1,6–9, consequences for human health, autonomy over time and its re- they have also become incapable economic opportunity and human silience to stress24. Assessment of of supplying services to the same communities. Increasing our these properties in large-scale sys- level as in the past5,10. The ca- understanding of these interactions will tems through specific indicators pacity of the environment to sus- involve more active collaboration between of resilience, organization and tain economic activity4,10 and hu- the ecological, social and health vigor has been attempted for the man health11–15 is, therefore, being sciences. -
For-75: an Ecosystem Approach to Natural Resources Management
FOR-75 An Ecosystems Approach to Natural Resources Management Thomas G. Barnes, Extension Wildlife Specialist ur nation—and especially Kentucky—has an The glade cress Oabundance of renewable natural resources, including timber, wildlife, and water. These re- sources have allowed us to build a strong nation and economy, creating one of the highest stan- dards of living in the world. As our nation grew and prospered during the past 200 years, we ex- tracted those natural resources through agricul- ture, forestry, mining, urban or industrial expansion, and other developments. Ultimately, we affected the amount of wild lands that native plants and animals need for survival. In the past, natural resources agencies have ral- The glade cress grows in Jefferson and Bullitt counties lied public support for declining wildlife popula- and nowhere else in the world. tions. In the 1930s, Congress passed the Federal Aid to Wildlife Resto- Table 1. Selected Ecosystem Declines in the ration Act, also called including the bald eagle, brown pelican, peregrine United States the Pittman-Robertson falcon, and American alligator, have recovered % Decline (loss) or Act, and state wildlife from the brink of extinction. However, numerous Ecosystem or Community Degradation agencies received fund- other species and unique habitats are declining, Pacific Northwest Old Growth Forest 90 ing to restore numerous and the list of endangered and threatened organ- Northeastern Pine Barrens 48 wildlife species that isms continues to grow every year. Why are these Tall Grass Prairie 961 were in trouble, includ- additional species in trouble, while other species Palouse Prairie 98 ing white-tailed deer, are increasing their populations and ranges? Where did we go wrong? Why, almost immedi- Blackbelt Prairies 98 wild turkeys, wood ducks, elk, and prong- ately after passage of the Endangered Species Act, Midwestern Oak Savanna 981 horn antelope. -
Ecosystem Health Demystified: an Ecological Concept Determined By
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Lincoln University Research Archive Ecosystem health demystified © An ecological concept determined by economic means By E. J. S. Hearnshaw1, R. Cullen1 and K. F. D. Hughey2 1Commerce Division, Lincoln University, 2Environment, Society and Design Division, Lincoln University Abstract This paper addresses “ecosystem health”, a concept recently popularised as the way forward in evaluating nature. The concept is often defined in vague expressions and is being seen more as a broad societal aspiration rather than a specific performance measure of ecosystem management. As such, the paper aims to demystify ecosystem health, that is, to demarcate an accurate and feasible characterisation of the concept. To achieve this aim an examination of the various viewpoints of nature is undertaken. Models of ecosystem health, such as the notions of naturalness, genetic fitness, climax, diversity, stability and keystone species are each considered and subsequently deemed inappropriate, especially when viewing ecosystems as “complex self-organising systems”. Complex self-organising systems are non-linear dynamic systems that have multiple steady states and have emergent and chaotic properties. One model that captures this self- organisation process is Holling’s adaptive cycle. However, when investigating this model it was concluded that there is no means to determining which phase within a system state, or state within a system is ecologically “better”. Therefore, ecosystem health cannot be considered in a positive manner established by scientific objectivity. Rather, the concept must be determined in a normative fashion through it is suggested the elicitation of subjective societal values, so to define an optimal management strategy. -
Ecological Cascades Emanating from Earthworm Invasions
502 REVIEWS Side- swiped: ecological cascades emanating from earthworm invasions Lee E Frelich1*, Bernd Blossey2, Erin K Cameron3,4, Andrea Dávalos2,5, Nico Eisenhauer6,7, Timothy Fahey2, Olga Ferlian6,7, Peter M Groffman8,9, Evan Larson10, Scott R Loss11, John C Maerz12, Victoria Nuzzo13, Kyungsoo Yoo14, and Peter B Reich1,15 Non- native, invasive earthworms are altering soils throughout the world. Ecological cascades emanating from these invasions stem from rapid consumption of leaf litter by earthworms. This occurs at a midpoint in the trophic pyramid, unlike the more familiar bottom- up or top- down cascades. These cascades cause fundamental changes (“microcascade effects”) in soil morphol- ogy, bulk density, and nutrient leaching, and a shift to warmer, drier soil surfaces with a loss of leaf litter. In North American temperate and boreal forests, microcascade effects can affect carbon sequestration, disturbance regimes, soil and water quality, forest productivity, plant communities, and wildlife habitat, and can facilitate other invasive species. These broader- scale changes (“macrocascade effects”) are of greater concern to society. Interactions among these fundamental changes and broader-scale effects create “cascade complexes” that interact with climate change and other environmental processes. The diversity of cascade effects, combined with the vast area invaded by earthworms, leads to regionally important changes in ecological functioning. Front Ecol Environ 2019; 17(9): 502–510, doi:10.1002/fee.2099 lthough society usually -
Recruitment of Three Non-Native Invasive Plants Into a Fragmented Forest in Southern Illinois Emily D
Forest Ecology and Management 190 (2004) 119–130 Recruitment of three non-native invasive plants into a fragmented forest in southern Illinois Emily D. Yatesa, Delphis F. Levia Jr.b,*, Carol L. Williamsa aDepartment of Geography, Southern Illinois University, Carbondale, IL 62901-4514, USA bDepartment of Geography, Center for Climatic Research, University of Delaware, Newark, DE 19716, USA Received 28 July 2003; received in revised form 10 September 2003; accepted 11 November 2003 Abstract Plant invasions are a current threat to biodiversity conservation, second only to habitat loss and fragmentation. Density and heights of three invasive plants, Rosa multiflora, Lonicera japonica, and Elaeagnus umbellata, were examined between edges and adjacent interiors of forest sites in southern Illinois. Density (stems mÀ2) and heights (cm) of invasive plants were obtained in plots along transects at edge and interior sampling locations within forest sites. The effect of species, sampling location, and site shape index on invasive plant density was investigated, as well as differences in heights of invasive plants in edge vs. interior sampling locations. Species, sampling location, and fragment shape index were significant factors influencing invasive plant density at study sites. Density for all three species ranged from 0 to 18 stems mÀ2. All three species invaded interiors of sites, however, R. multiflora and L. japonica had significantly greater densities in edge as opposed to interior transects. These two species also had significant differences in density among site shape indices. Density of E. umbellata was not significantly different between edge and interior sampling locations or among site shape indices. Mean heights of all three invasive plants were higher in edge transects, however, this relationship was only significant for L. -
Effects of Nonindigenous Invasive Species on Water Quality and Quantity
Effects of Nonindigenous Invasive Species on Water Quality and Quantity Frank H. McCormick1, Glen C. Contreras2, and Agency (EPA), more than one-third of all States have waters Sherri L. Johnson3 that are listed for invasive species under section 303d of the Clean Water Act of 1977. Nonindigenous species cause ecological damage, human health risks, or economic losses. Abstract Invasive species are degrading a suite of ecosystem services that the national forests and grasslands provide, including Physical and biological disruptions of aquatic systems recreational fishing, boating, and swimming; municipal, caused by invasive species alter water quantity and water industrial, and agricultural water supply; and forest products. quality. Recent evidence suggests that water is a vector for Degradation of these services results in direct economic the spread of Sudden Oak Death disease and Port-Orford- losses, costs to replace the services, and control costs. Losses, cedar root disease. Since the 1990s, the public has become damages, and control costs are estimated to exceed $178 billion increasingly aware of the presence of invasive species in annually (Daily et al. 2000a, 2000b). Although agriculture is the Nation’s waters. Media reports about Asian carp, zebra the segment of the economy most affected ($71 billion per mussels (Dreissena polymorpha), golden algae (Prynmesium year), costs to other segments, such as tourism, fisheries, and parvum), cyanobacteria (Anabaena sp., Aphanizomenon sp., water supply, total $67 billion per year. Although more difficult and Microcystis sp.), and New Zealand mud snail have raised to quantify, losses of these ecosystem functions also reduce public awareness about the economic and ecological costs of the quality of life. -
Beltrami County
2017 Beltrami County Lake Prioritization and Protection Planning Document RMBEL [Company22796 County name] Highway 6 Detroit Lakes, MN 56501 1/1/2017 (218) 846-1465 www.rmbel.info Date: April 4, 2017 To: Beltrami County Environmental Services 701 Minnesota Ave NW # 113, Bemidji, MN 56601 Subject: Beltrami County Lake Prioritization and Planning Document From: Moriya Rufer RMB Environmental Laboratories, Inc 22796 County Highway 6 Detroit Lakes, MN 56501 218-846-1465 [email protected] www.rmbel.info Authors: Moriya Rufer, RMBEL, oversight and report Emelia Hauck, RMBEL, mapping and data analysis Andrew Weir, RMBEL, data analysis Acknowledgements Organization and oversight Brent Rud, Beltrami County Zach Gutknecht, Beltrami County Dan Steward, BWSR Jeff Hrubes, BWSR Funding provided by Board of Water and Soil Resources Beltrami County Organizations contributing data and information Minnesota Department of Natural Resources (DNR) Minnesota Pollution Control Agency (MPCA) Beltrami County Red Lake Department of Natural Resources Beltrami County Lakes Summary 2017, RMB Environmental Laboratories 1 of 32 Table of Contents Beltrami County Data Assessment Summary Report Introduction ............................................................................................................................. 3 Data Availability....................................................................................................................... 3 Trophic State Index ................................................................................................................ -
State of the Amazon: Freshwater Connectivity and Ecosystem Health WWF LIVING AMAZON INITIATIVE SUGGESTED CITATION
REPORT LIVING AMAZON 2015 State of the Amazon: Freshwater Connectivity and Ecosystem Health WWF LIVING AMAZON INITIATIVE SUGGESTED CITATION Macedo, M. and L. Castello. 2015. State of the Amazon: Freshwater Connectivity and Ecosystem Health; edited by D. Oliveira, C. C. Maretti and S. Charity. Brasília, Brazil: WWF Living Amazon Initiative. 136pp. PUBLICATION INFORMATION State of the Amazon Series editors: Cláudio C. Maretti, Denise Oliveira and Sandra Charity. This publication State of the Amazon: Freshwater Connectivity and Ecosystem Health: Publication editors: Denise Oliveira, Cláudio C. Maretti, and Sandra Charity. Publication text editors: Sandra Charity and Denise Oliveira. Core Scientific Report (chapters 1-6): Written by Marcia Macedo and Leandro Castello; scientific assessment commissioned by WWF Living Amazon Initiative (LAI). State of the Amazon: Conclusions and Recommendations (chapter 7): Cláudio C. Maretti, Marcia Macedo, Leandro Castello, Sandra Charity, Denise Oliveira, André S. Dias, Tarsicio Granizo, Karen Lawrence WWF Living Amazon Integrated Approaches for a More Sustainable Development in the Pan-Amazon Freshwater Connectivity Cláudio C. Maretti; Sandra Charity; Denise Oliveira; Tarsicio Granizo; André S. Dias; and Karen Lawrence. Maps: Paul Lefebvre/Woods Hole Research Center (WHRC); Valderli Piontekwoski/Amazon Environmental Research Institute (IPAM, Portuguese acronym); and Landscape Ecology Lab /WWF Brazil. Photos: Adriano Gambarini; André Bärtschi; Brent Stirton/Getty Images; Denise Oliveira; Edison Caetano; and Ecosystem Health Fernando Pelicice; Gleilson Miranda/Funai; Juvenal Pereira; Kevin Schafer/naturepl.com; María del Pilar Ramírez; Mark Sabaj Perez; Michel Roggo; Omar Rocha; Paulo Brando; Roger Leguen; Zig Koch. Front cover Mouth of the Teles Pires and Juruena rivers forming the Tapajós River, on the borders of Mato Grosso, Amazonas and Pará states, Brazil.