DOCSLIB.ORG

Management Experiments on Lake Erie Flowering Rush

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Management Experiments on Lake Erie Flowering Rush Bowling Green State University ScholarWorks@BGSU Honors Projects Honors College Spring 4-29-2013 Management Experiments on Lake Erie Flowering Rush Alyssa Dietz Follow this and additional works at: https://scholarworks.bgsu.edu/honorsprojects Repository Citation Dietz, Alyssa, "Management Experiments on Lake Erie Flowering Rush" (2013). Honors Projects. 19. https://scholarworks.bgsu.edu/honorsprojects/19 This work is brought to you for free and open access by the Honors College at ScholarWorks@BGSU. It has been accepted for inclusion in Honors Projects by an authorized administrator of ScholarWorks@BGSU. 1 Management Experiments on Lake Erie Flowering Rush Alyssa Dietz HONORS PROJECT Submitted to the University Honors Program at Bowling Green State University in partial fulfillment of the requirements for graduation with UNIVERSITY HONORS April 29 th , 2013 Advisors: Dr. Helen J. Michaels, Department of Biological Sciences Dr. Enrique Gomezdelcampo, Department of Environment and Sustainability 2 Summary: The issue of invasive species has been a major concern for many Great Lakes ecosystems over the past several decades. Since the first noted invasive animal, the sea lamprey, these fresh water ecosystems have been invaded by over 180 different plants and animals that create over $100 million worth of damage a year (Rosaen et al . 2012). Because the five Great Lakes, along with their rivers, streams, and wetlands are such an interconnected series, the introduction of any invasive species to one of the Great Lakes, such as Lake Erie, means that invaders are likely to spread to all other freshwater ecosystems in the area (Rosaen et al . 2012). With the various ways that many introduced species can alter the nutrient availability, habitat quality, and species richness, many wildlife managers are continuing to develop management strategies that remove or greatly limit the further spread of invasive species. Of major concern are invading aquatic plants whose ranges continue to expand. The purpose of this study was to understand the response of an invasive aquatic plant, Butomus umbellatus L. in Lake Erie wetlands to the combined management strategies of clipping and flooding. These strategies are hoped to be shared with local wetlands managers in better hopes of limiting the impacts and concerns that this invasive has created in local ecosystems. Introduction: Given their diverse morphology, invasive macrophytes, or aquatic plants, have the potential to alter community complexity, change oxygen levels within aquatic systems, and facilitate in the invasion of other exotic species (Schultz and Dibble 2012). Though significantly detrimental to native ecosystems, macrophytes receive very little attention compared to the issues of invasive aquatic animals. One particularly understudied species found in Lake Erie is 3 Butomus umbellatus , commonly known as flowering rush. Originally introduced from Europe for aquatic gardens, B. umbellatus has now spread throughout along the northern United States and Canadian border (Brown and Eckert 2005 ) (Figure 1). Figure 1. The Invasive Range of B. umbellatus spans most of the U.S./Canadian border. Characterized by triangular leaves, B. umbellatus is not a true rush, but is rather a single species belonging to the p lant family Butomaceae ( Brown and Eckert 2005). Though little is known about its specific origin and impacts, the reproduction and life history of B. umbellatus are well known. B. umbellatus has three methods of reproduction and can reproduce sexually or asexually. B. umbellatus can reproduce sexual ly through seed, but there is som e argument over the viability of seeds produced by Nort h American populations ( Kliber and Eckert 2005 ) (Picture 1). It is thought that most populations in this region reproduce dominantly via asexual methods through rhizomes (Picture 2) and vegetative prop agules (Picture 3) (Brown and Eckert 2005 ; Parkinson et al . 2010). These vegetative propagules are pieces of rhizomes that break off from adult plants and form roots while floating. When marsh water levels drop, the vegetative 4 propagules are likely able to establish quickly, potentially giving B. umbellatus a great advantage over smaller native seedlings. Picture 1. Flower of B. umebllatus produce seeds Picture 2. Below ground rhizomes through sexual reproduction. allow for asexual reproduction. Picture 3 . Vegetative propagule growth on the rhizome of an established plants are produced by asexual reproduction. 5 As an invasive, B. umbellatus can alter native vegetation and macroinvertebrate communities (Shultz and Dibble 2012). In Canadian areas, B. umebellatus has begun to threaten native populations of Zizania aquatica (wild rice). With further spread throughout the Great Lakes Region, Canada has designated B. umbellatus as a “principal invasive alien” (White et al . 1993 in Brown and Eckert 2005). In the United States, B. umbellatus has been found in Lake Erie wetlands since the early twentieth century (Brown and Eckert 2005). One particular regional population is located at Ottawa National Wildlife Refuge (ONWR) in Oak Harbor, Ohio. ONWR is a diked wetland ecosystem manager by altering flooding levels necessary for habitat for native shorebird populations. As pilot studies have demonstrated, B. umbellatus is capable of changing macroinvertebrate community richness, greatly reducing this vital food resource for local fish and bird populations (Dietz, unpublished data). With such an impact to the major taxa of the region, ONWR and other local wetland refuges have begun to implement management strategies to control B. umbellatus . Most strategies to remove B. umbellatus have had minimal success in restoring invaded marshes. Common strategies include manually digging out plants, cutting, and the application of herbicides (Parkinson et al . 2010). Digging plants has had mixed results due to the further spread of B. umbellatus after disturbances to the rhizomes (Parkinson et al . 2010). In addition, the application of herbicides has proven inefficient due to the thin emergent leaves of B. umbellatus that reduce the chance of chemicals adhering to the plant (Parkinson et al . 2010). Applied chemicals could wash away and potentially alter the chemical composition of water where they could impact non-target species, such as amphibians. These inefficiencies in current management strategies of B. umbellatus have caused many wildlife managers to search for new ways to successfully manage or eradicate the invasive species. 6 Some of the effective treatments developed for the removal of other aquatic plants include inundation (flooding) and clipping (Kercher and Zedler 2004). Clipping removes leaves and stem tissue critical for photosynthesis and the transportation of oxygen to roots, limiting the future growth of the plant (Mayence et al . 2010). The inclusion of secondary clipping treatments is believed to further limit the development of plants. This second cutting is intended to remove additional growth material after the plant has used its carbohydrate and nutrient reserves but before new leaves have begun to conduct photosynthesis and begin to restore the resources that it took to grow them. Inundation limits both light levels for photosynthesis and oxygen for root respiration. As water depth increases, both of these vital environmental conditions decrease, reducing growth and plant survival (Kercher and Zedler 2004). While some programs treating B. umbellatus with clipping have had little impact on the eradication of the species, a combination of inundation and clipping may be a more effective method in preventing the species’ spread into more southern wetlands (Parkinson et al . 2010). Previously conducted pilot studies investigating the impact of flooding levels alone have suggested that B. umbellatus tended to have lower biomass in higher water depths (Dietz, unpublished data). To develop better management strategies of B. umbellatus in Lake Erie wetlands, this experiment investigated the effects of these alternative management strategies of clipping and inundation through the following experimental questions: 1) How does flooding effect the development and growth of B. umbellatus ? and 2) Do combined treatments of flooding and clipping effectively reduce the growth of B. umbellatus ? Materials and Methods: 7 Two hundred B. umbellatus plants were collected from Ottawa National Wildlife Refuge (ONWR) in Oak Harbor, Ohio in late October 2012. Twenty-four hours following collection, all plants were washed to remove algae and herbivorous invertebrates that could damage the leaves. Senescing leaves were trimmed before the plants were planted in natural clay based cat litter with no chemical additives (Special Kitty Natural Clay Cat Litter). Cat litter was chosen because of its similarity in composition to the clay-based soils of natural marshes. After washing, all plants were vernalized for eleven weeks in a growth chamber at Bowling Green State University. All plants were stored at 8 ˚C with 8 hour photoperiods and were watered every two days to maintain at least one to two inches of standing water throughout dormancy. After eleven weeks of vernalization, plants were placed in the Bowling Green State University greenhouse under supplemental lighting in order to break dormancy. After emergence in early February 2013, plants were again washed and senesced or dead leaves were removed before planting in 11 cm (4.5 in) clear plastic pots containing 300 g of 100% dry clay. Rhizomes of larger plants that
Load more

Recommended publications
  • Introduction to Common Native & Invasive Freshwater Plants in Alaska
    Introduction to Common Native & Potential Invasive Freshwater Plants in Alaska Cover photographs by (top to bottom, left to right): Tara Chestnut/Hannah E. Anderson, Jamie Fenneman, Vanessa Morgan, Dana Visalli, Jamie Fenneman, Lynda K. Moore and Denny Lassuy. Introduction to Common Native & Potential Invasive Freshwater Plants in Alaska This document is based on An Aquatic Plant Identification Manual for Washington’s Freshwater Plants, which was modified with permission from the Washington State Department of Ecology, by the Center for Lakes and Reservoirs at Portland State University for Alaska Department of Fish and Game US Fish & Wildlife Service - Coastal Program US Fish & Wildlife Service - Aquatic Invasive Species Program December 2009 TABLE OF CONTENTS TABLE OF CONTENTS Acknowledgments ............................................................................ x Introduction Overview ............................................................................. xvi How to Use This Manual .................................................... xvi Categories of Special Interest Imperiled, Rare and Uncommon Aquatic Species ..................... xx Indigenous Peoples Use of Aquatic Plants .............................. xxi Invasive Aquatic Plants Impacts ................................................................................. xxi Vectors ................................................................................. xxii Prevention Tips .................................................... xxii Early Detection and Reporting
    [Show full text]
  • Status and Strategy for Flowering Rush (Butomus Umbellatus L.) Management
    State of Michigan’s Status and Strategy for Flowering Rush (Butomus umbellatus L.) Management Scope Invasive flowering rush (Butomus umbellatus L., hereafter FR) has invaded the shores of Michigan waterways since the early 1900’s (Core 1941; Stuckey 1968; Anderson et al. 1974). This document was developed by Central Michigan University and reviewed by Michigan Departments of Environmental Quality and Natural Resources for the purposes of: • Summarizing the current level of understanding on the biology and ecology of FR. • Summarizing current management options for FR in Michigan. • Identifying possible future directions of FR management in Michigan. This document used the current information available in journals, publications, presentations, and experiences of leading researchers and managers to meet its goals. Any chemical, company, or organization that is mentioned was included for its involvement in published, presented, or publically shared information, not to imply endorsement of the chemical, company, or organization. Biology and Ecology I. Identification Flowering rush is an emergent aquatic perennial plant with linear, sword-like leaves, triangular in cross-section, and a showy umble of pink flowers (Figure 1). Rhizomes (i.e. horizonal root-like stems) are fleshy, and leaves have parallel veination and can be submersed or emergent. Submersed leaves are linear and limp, unlike sword-like emergent leaves. Flowering rush blooms from June to August. Flowers are arranged in terminal umbels. Flower parts are found in multiples of three (e.g. six tepals, nine stamen, six carpels) with pink to purple tepals 0.25 – 0.5 in (6 - 11.5 mm) long (eFloras 2008). Each flower produces up to six beaked fruits.
    [Show full text]
  • Columbia Basin Flowering Rush Management Plan
    COLUMBIA BASIN COOPERATIVE WEED MANAGEMENT AREA COLUMBIA BASIN FLOWERING RUSH MANAGEMENT PLAN A regional strategy to address Butomus umbellatus throughout the Columbia Basin www.columbiabasincwma.org Statement of Collaboration: When possible, the partners of the Columbia Basin Cooperative Weed Management Area will strive to communicate and work collaboratively to develop a unified management effort for flowering rush throughout the Columbia Basin. The completion of this document was supported by funding from the National Fish and Wildlife Foundation Suggested citation: Columbia Basin Cooperative Weed Management Area. 2019. Columbia Basin Flowering Rush Management Plan: A regional strategy to address Butomus umbellatus throughout the Columbia Basin. pp 67 www.columbiabasincwma.org Pg. 1 CONTENT Tables ....................................................................................................................................... 3 Figures ..................................................................................................................................... 3 Preface ..................................................................................................................................... 5 Executive Summary .................................................................................................................. 6 Introduction ............................................................................................................................. 7 Scope and Purpose ........................................................................................................................7
    [Show full text]
  • Ecology and Phenology of Flowering Rush in the Detroit Lakes Chain of Lakes, Minnesota
    J. Aquat. Plant Manage. 53: 54–63 Ecology and phenology of flowering rush in the Detroit Lakes chain of lakes, Minnesota MICHELLE D. MARKO, JOHN D. MADSEN, R. A. SMITH, B. SARTAIN, AND C. L. OLSON* ABSTRACT al. 1974, Boutwell 1990, Brown and Eckert 2005). Flowering rush can form monotypic stands that crowd out native Flowering rush, Butomus umbellatus L., has been an plants and interfere with recreational water use and water increasing problem in the Detroit Lakes chain of lakes for flow (Boutwell 1990, Jacobs et al. 2011). In the St. Lawrence more than 40 yr. Flowering rush dominates ecosystems by River region, it was found to be more invasive than purple crowding out native species, including hardstem bulrush, loosestrife (Lythrum salicaria L.; Lavoie 2003). The spread of Schoenoplectus acutus (Muhl. ex Bigelow) A & D Love,¨ a vital flowering rush in irrigation ditches has affected water flow part of native ecosystems. Furthermore, flowering rush and become a management concern for native fish species, creates boating hazards and hampers recreational activities such as cutthroat and bull trout (Jacobs et al. 2011). One on the lakes. The phenological differences between flower- region in Minnesota, the Pelican River Watershed, has been ing rush and the native hardstem bulrush were examined as struggling with flowering rush for over 40 yr as it has spread part of a project to determine best management practices through the Detroit Lakes chain of lakes since the 1960s (T. for controlling this invasive species. Biomass allocation, Guetter, Pelican River Watershed District, pers. comm.). plant height, carbohydrate allocation, and reproductive Since its introduction as an ornamental species in Lake structures of flowering rush were examined in the Detroit Sallie (Becker County, Minnesota), different methods of Lakes system.
    [Show full text]
  • Flowering Rush
    IPANE - Catalog of Species Search Results http://www.lib.uconn.edu/webapps/ipane/browsing.cfm?descriptionid=16 Home | Early Detection | IPANE Species | Data & Maps | Volunteers | About the Project | Related Information Catalog of Species Search Results Butomus umbellatus (Flowering rush ) :: Catalog of Species Search Common Name(s) | Full Scientific Name | Family Name Common | Family Scientific Name | Images | Synonyms | Description | Similar Species | Reproductive/Dispersal Mechanisms | Distribution | History of Introduction in New England | Habitats in New England | Threats | Early Warning Notes | Management Links | Documentation Needs | Additional Information | References | Data Retrieval | Maps of New England Plant Distribution COMMON NAME Flowering rush FULL SCIENTIFIC NAME Butomus umbellatus L. FAMILY NAME COMMON Flowering rush family FAMILY SCIENTIFIC NAME Butomaceae IMAGES Flowers Habit Flowers Fruit Incursion Roots 1 of 5 9/24/2007 3:36 PM IPANE - Catalog of Species Search Results http://www.lib.uconn.edu/webapps/ipane/browsing.cfm?descriptionid=16 Habitat NOMENCLATURE/SYNONYMS Synonyms: Butomus umbellatus f. vallisneriifolius (Sagorski) Gluck DESCRIPTION Botanical Glossary Butomus umbellatus is a perennial, aquatic herb that grows from a fleshy rhizome on freshwater shorelines. It can be found in water several meters deep, and its flowering stem can reach up to 1 m (3.3 ft.) above the surface of the water. The 0.6-0.9 m (2-3 ft.) long ensiform leaves can be erect or floating on the water's surface. The leaves are three angled, fleshy and have twisted ends. The plants flower from the summer to the fall depending on the depth of the water. The flowers are arranged in a bracted umbel. The bracts are purple-tinged, and numerous flowers are on long, slender ascending pedicels.
    [Show full text]
  • DRAFT: WRITTEN FINDINGS of the WASHINGTON STATE NOXIOUS WEED CONTROL BOARD Updated in 2020, Original Draft from 2008
    DRAFT: WRITTEN FINDINGS OF THE WASHINGTON STATE NOXIOUS WEED CONTROL BOARD Updated in 2020, original draft from 2008 Scientific Name: Butomus umbellatus L. Synonyms: Butomus junceus Turcz, Butomus umbellatus L. f. vallisneriifolius (Sagorski) Glnck Common Name: Flowering-rush (sometimes known as grass rush) Family: Butomaceae (Flowering-rush family) Legal Status: Class A noxious weed; Quarantine List (WAC 16-752) Images: left, flowering rush with emergent leaves growing along a shoreline; center, rhizome with leaf bases and developing bud; right, piece of flowering rush rhizome with leaves, all images by Greg Haubrich. Introduction: Flowering rush is an invasive aquatic perennial monocot that is able to exploit a wide range of aquatic habitats. It grows emergent along the shoreline of lakes and rivers out to water depths of 7 m (24 ft.) or more where it is fully submersed. It will grow in still water with muddy substrate to flowing water with rocky substrate and everything in between. It thrives in areas with fluctuating water levels, but also persists and spreads in stable water conditions (Hroudova ́ 1989, Hroudova ́ et al. 1996). It will invade and dominate native plant beds (Madsen et al. 2012, Harms 2020) and can also colonize habitats previously barren of plant growth (Parkinson et al. 2010). When growing submersed, the leaves are stiff relative to other submersed plants, and thus in flowing water they are present higher in the water column. It has been termed an ecosystem engineer for its ability to alter habitat by sediment accretion (Gunderson et al. 2016). These characteristics, along with the rapidly expanding population, have raised concern about potential impacts on habitat and water delivery if flowering rush becomes well established throughout its potential range in western North America.
    [Show full text]
  • Flowering Rush (Butomus Umbellatus)
    Biology, Ecology and Management of Flowering Rush (Butomus umbellatus) EB0201 December 2010 Hilary Parkinson, Research Associate, MSU, Department of Land Resources and Environmental Sciences Jane Mangold, MSU Extension Invasive Plant Specialist, Department of Land Resources and Environmental Sciences Virgil Dupuis, Salish Kootenai College Peter Rice, Research Ecologist, University of Montana, Division of Biological Sciences Table of Contents Flowering rush is a non-native aquatic resembling a large sedge that grows along lake shores and slow Plant Biology . 3 moving water bodies. In Montana it was recorded in Flathead Lake in 1964 and has spread to Thompson Identification . 3 Falls, Noxon Reservoir, Cabinet Gorge, portions of the Flathead River, and the Clark Fork River. Prolific SpeedyWeed ID . 4 growth in irrigation ditches reduces water availability, and dense stands in previously unvegetated Life History . 5 areas inhibit boating, fishing and swimming. Minor disturbances cause the roots to fragment, providing Ecology . 5 long distance dispersal. At this time, control methods are limited. Hand digging has led to mixed results Habitat . 5 as rhizomes fragment easily, increasing dispersal. Studies on chemical control options are ongoing. Spread and Establishment Potential . 5 Damage Potential . 7 Current Status and Distribution . 7 PLANT BIOLOGY Management Alternatives . 8 Identification Mechanical Control . 8 Flowering rush is an aquatic species resembling a large sedge (cover photo) Cultural Control . 9 that may grow as an emergent plant with upright foliage in shallower wa- Biological Control . 9 ters (shoreline to roughly 10 feet [or 3 m]), or a submerged plant with flex- ible leaves suspended in the water column in deeper waters (approximately Chemical Control .
    [Show full text]
  • Habitats Colonized by Non-Native Flowering Rush Butomus Umbellatus (Linnaeus, 1753) in the Niagara River, USA
    Aquatic Invasions (2016) Volume 11, Issue 4: 369–380 DOI: http://dx.doi.org/10.3391/ai.2016.11.4.03 Open Access © 2016 The Author(s). Journal compilation © 2016 REABIC Research Article Habitats colonized by non-native flowering rush Butomus umbellatus (Linnaeus, 1753) in the Niagara River, USA Matthew D. Gunderson1,*, Kevin L. Kapuscinski2, Derek P. Crane3 and John M. Farrell1 1Department of Environmental and Forest Biology, State University of New York College of Environmental Science and Forestry, 1 Forestry Drive, Syracuse, NY 13210, USA 2School of Biological Sciences, CRW225, Lake Superior State University, 650 W. Easterday Avenue, Sault Ste. Marie, MI 49783, USA 3Department of Biology, Coastal Carolina University, 109 Chanticleer Drive East, Conway, SC 29526, USA *Corresponding author E-mail: [email protected] Received: 8 January 2016 / Accepted: 24 May 2016 / Published online: 8 July 2016 Handling editor: Charles Martin Abstract During the summer of 2012, we first observed non-native flowering rush Butomus umbellatus (Linnaeus, 1753) in the upper Niagara River, NY, USA, where this species had previously been undocumented. In a 2013 study, Butomus was present at 33 of 161 (20%) submersed nearshore (≤ 3 m) sites surveyed. It was the species of greatest biomass at 27% of the sites where it was collected, and was observed growing at depths > 3 m. Butomus was disproportionately prevalent in the upper observed ranges of water depth and velocity. Butomus was also closely associated with coarse substrates, differing from canopy-forming species but not other linear-leaved species. Emergence of Butomus from the sediment generally occurred from late-May to early-June, with peak coverage and height occurring in mid- to late-July.
    [Show full text]
  • Flowering Rush (Butomus Umbellatus)
    Flowering Rush (Butomus umbellatus) Best Management Practices in Ontario Foreword These Best Management Practices (BMPs) provide guidance for managing invasive flowering rush (Butomus umbellatus) in Ontario. Funding and leadership for the production of this document was provided by Environment and Climate Change Canada, Canadian Wildlife Service – Ontario (CWS-ON). These BMPs were developed by the Ontario Invasive Plant Council (OIPC) and its partners to facilitate invasive plant control initiatives by individuals and organizations concerned with the protection of biodiversity, agricultural lands, infrastructure, crops and species at risk in Ontario. The intent of this document is to relay specific information relating to aquatic invasive plant control practices that have been recommended by leading professionals across Ontario. This document contains the most up-to-date, effective, and environmentally safe control practices known from research and experience. It complies with current provincial and federal legislation regarding pesticide usage, habitat disturbance and species at risk protection. It is subject to change as legislation is updated or new research findings emerge. The information provided in this BMP is not to be considered legal advice. The timing windows suggested will differ throughout Ontario and by management activity and should be tailored to your region. Interested parties are advised to refer to the applicable legislation to address specific circumstances. Check the website of the OIPC (https://www.ontarioinvasiveplants.ca/) for updates. Simkovic, Vicki. 2020. Flowering Rush (Butomus umbellatus): Best Management Practices in Ontario. Ontario Invasive Plant Council, Peterborough, ON. Edition 1.0 - March 2020 Peterborough, Ontario This document was prepared for Environment and Climate Change Canada, Canadian Wildlife Service - Ontario by the Ontario Invasive Plant Council.
    [Show full text]
  • Management of Flowering Rush in the Detroit Lakes, Minnesota
    J. Aquat. Plant Manage. 54: 61–67 Management of flowering rush in the Detroit Lakes, Minnesota JOHN D. MADSEN, BRADLEY SARTAIN, GRAY TURNAGE, AND MICHELLE MARKO* ABSTRACT (Minnesota) area; in particular, Detroit Lake (Big Detroit, Little Detroit, and Curfman Lakes), Lake Sallie, Lake Flowering rush (Butomus umbellatus) is an invasive aquatic Melissa, and Mill Pond (Marko et al. 2015). It is native to plant introduced to North America from Eurasia in 1897. Europe and Asia and first entered the United States in 1928 Flowering rush can grow either submersed or emergent (Bellaud 2009). Flowering rush has continued to be a from wet soil habitats to waters that are up to 5 m deep. problem in the lake for at least three decades. Flowering rush was first observed in the Detroit Lake In the Detroit Lakes area, the flowering rush has been system in the 1960s, causing significant impact to shoreline determined to be triploid (Kliber and Eckert 2005, Lui et al. and recreational use. Flowering rush is currently found in 2005, Poovey et al. 2012). This is one of two cytotypes in the five basins of the Detroit Lake system: Big Detroit, Little species (Hroudova et al. 1996); the other is diploid. The Detroit, Curfman, Sallie, and Melissa Lakes. Submersed diploid is sexually fertile and self-compatible, whereas the treatments with diquat were used during 2012 on an triploid is predominantly sterile and self-incompatible. In operational scale to control the nuisance impacts of the triploid cytotype, the principal means of spread are flowering rush in waters from 0 to 1.3 m deep.
    [Show full text]
  • Provincial Containment Strategy
    Provincial Containment Strategy Butomus umbellatus (Flowering Rush) Prepared by: B.C. Ministry of Forests, Lands and Natural Resource Operations June 2015 BUTOMUS UMBELLATUS L. PROVINCIAL CONTAINMENT STRATEGY Acknowledgements The Ministry of Forests, Lands and Natural Resource Operations would like to acknowledge the following individuals and organizations for their valuable contributions to this project: Anna and Martin Eastman, Baker Creek Enhancement Society, Bruce Edwards, Cariboo Regional District, Fraser Valley Invasive Plant Council, K.C. Log Booming, and private landowners who provided access to survey sites. The original draft was completed by Crystal Klym, P.Ag. (June 2015). B.C. Invasive Plant Early Detection Rapid Response Program June 2015 B.C. Ministry of Forests, Lands & Natural Resource Operations Page | i BUTOMUS UMBELLATUS L. PROVINCIAL CONTAINMENT STRATEGY Table of Contents Acknowledgements .............................................................................................................. i Background ......................................................................................................................... 1 Extent .................................................................................................................................. 1 Hatzic Lake Survey Results .............................................................................................. 1 Bouchie Lake Survey Results ........................................................................................... 2 Stakeholder
    [Show full text]
  • Connecticut Invasive Plant List January 2004
    CONNECTICUT INVASIVE PLANT LIST JANUARY 2004 This is a list of species that have been determined by floristic analysis to be invasive or potentially invasive in the state of Connecticut, in accordance with PA 03-136. The Invasive Plants Council will generate a second list recommending restrictions on some of these plants. In developing the second list and particular restrictions, the Council will recognize the need to balance the detrimental effects of invasive plants with the agricultural and horticultural value of some of these plants, while still protecting the state's minimally managed habitats. CONNECTICUT INVASIVE PLANT LIST ( Produced by the Connecticut Invasive Plants Council ) Connecticut Public Act No. 03-136 The Connecticut Invasive Plants Council encourages the use of non- invasive alternatives, particularly when planting near parks, natural areas, or other minimally managed habitats. AQUATIC & WETLAND PLANTS Species Common Invasive Potentially name Invasive Butomus umbellatus L. Flowering rush X Cabomba caroliniana A. Fanwort X Gray Callitriche stagnalis Scop. Pond water- X starwort Egeria densa Planchon Brazilian water- X weed †Eichhornia crassipes Common water- X (Mart.) Solms hyacinth Hydrilla verticillata (L.f.) Hydrilla X Royle Iris pseudacorus L. Yellow Iris X Lythrum salicaria L. Purple X loosestrife Marsilea quadrifolia L. European X waterclover Myosotis scorpioides L. Forget-me-not X Myriophyllum aquaticum Parrotfeather X (Vell.) Verdc. Myriophyllum Variable-leaf X heterophyllum Michx. watermilfoil Myriophyllum spicatum L. Eurasian X watermilfoil Najas minor All. Brittle water- X nymph Nelumbo lutea (Willd.) American water X Pers. lotus †Nymphoides peltata Yellow floating X (Gmel.) Kuntze heart †Pistia stratiotes L. Water lettuce X Potamogeton crispus L.
    [Show full text]