Erroneous Identities of Potamogeton Hybrids Corrected by Molecular Analysis of Plants from Type Clones
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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 -
WETLAND PLANTS – Full Species List (English) RECORDING FORM
WETLAND PLANTS – full species list (English) RECORDING FORM Surveyor Name(s) Pond name Date e.g. John Smith (if known) Square: 4 fig grid reference Pond: 8 fig grid ref e.g. SP1243 (see your map) e.g. SP 1235 4325 (see your map) METHOD: wetland plants (full species list) survey Survey a single Focal Pond in each 1km square Aim: To assess pond quality and conservation value using plants, by recording all wetland plant species present within the pond’s outer boundary. How: Identify the outer boundary of the pond. This is the ‘line’ marking the pond’s highest yearly water levels (usually in early spring). It will probably not be the current water level of the pond, but should be evident from the extent of wetland vegetation (for example a ring of rushes growing at the pond’s outer edge), or other clues such as water-line marks on tree trunks or stones. Within the outer boundary, search all the dry and shallow areas of the pond that are accessible. Survey deeper areas with a net or grapnel hook. Record wetland plants found by crossing through the names on this sheet. You don’t need to record terrestrial species. For each species record its approximate abundance as a percentage of the pond’s surface area. Where few plants are present, record as ‘<1%’. If you are not completely confident in your species identification put’?’ by the species name. If you are really unsure put ‘??’. After your survey please enter the results online: www.freshwaterhabitats.org.uk/projects/waternet/ Aquatic plants (submerged-leaved species) Stonewort, Bristly (Chara hispida) Bistort, Amphibious (Persicaria amphibia) Arrowhead (Sagittaria sagittifolia) Stonewort, Clustered (Tolypella glomerata) Crystalwort, Channelled (Riccia canaliculata) Arrowhead, Canadian (Sagittaria rigida) Stonewort, Common (Chara vulgaris) Crystalwort, Lizard (Riccia bifurca) Arrowhead, Narrow-leaved (Sagittaria subulata) Stonewort, Convergent (Chara connivens) Duckweed , non-native sp. -
A Key to Common Vermont Aquatic Plant Species
A Key to Common Vermont Aquatic Plant Species Lakes and Ponds Management and Protection Program Table of Contents Page 3 Introduction ........................................................................................................................................................................................................................ 4 How To Use This Guide ....................................................................................................................................................................................................... 5 Field Notes .......................................................................................................................................................................................................................... 6 Plant Key ............................................................................................................................................................................................................................. 7 Submersed Plants ...................................................................................................................................................................................... 8-20 Pipewort Eriocaulon aquaticum ...................................................................................................................................................................... 9 Wild Celery Vallisneria americana .................................................................................................................................................................. -
Ogden's Pondweed (Potamogeton Ogdenii) Conservation and Research Plan for New England
Species at Risk Act Recovery Strategy Series Adopted under Section 44 of SARA Recovery Strategy for Ogden’s Pondweed (Potamogeton ogdenii) in Canada Ogden’s Pondweed 2016 Recommended citation: Environment Canada. 2016. Recovery Strategy for Ogden’s Pondweed (Potamogeton ogdenii) in Canada. Species at Risk Act Recovery Strategy Series. Environment Canada, Ottawa. 15 pp. + Annexes. For copies of the recovery strategy, or for additional information on species at risk, including the Committee on the Status of Endangered Wildlife in Canada (COSEWIC) Status Reports, residence descriptions, action plans, and other related recovery documents, please visit the Species at Risk (SAR) Public Registry1. Cover illustration: © C.B. Hellquist Également disponible en français sous le titre « Programme de rétablissement du potamot d’Ogden (Potamogeton ogdenii) au Canada » © Her Majesty the Queen in Right of Canada, represented by the Minister of the Environment, 2016. All rights reserved. ISBN 978-0-660-03379-2 Catalogue no. En3-4/207-2016E-PDF Content (excluding the illustrations) may be used without permission, with appropriate credit to the source. 1 http://www.registrelep-sararegistry.gc.ca RECOVERY STRATEGY FOR OGDEN’S PONDWEED (Potamogeton ogdenii) IN CANADA 2016 Under the Accord for the Protection of Species at Risk (1996), the federal, provincial, and territorial governments agreed to work together on legislation, programs, and policies to protect wildlife species at risk throughout Canada. In the spirit of cooperation of the Accord, the Government of Ontario has given permission to the Government of Canada to adopt the Recovery Strategy for Ogden’s Pondweed (Potamogeton ogdenii) in Ontario (Part 2) under Section 44 of the Species at Risk Act (SARA). -
Factors Known to Control the Distribution and Growth of Lotic Aquatic Ma- Crophytes Include Turbulence, Light, Surface-Water
Aquatic Botany, 31 (1988) 1-12 1 Elsevier Science Publishers B.V., Amsterdam -- Printed in The Netherlands INTERSTITIAL WATER PATTERNS: A FACTOR INFLUENCING THE DISTRIBUTIONS OF SOME LOTIC AQUATIC VASCULAR MACROPHYTES SHARON L. FORTNER and DAVID S. WHITE ~ Great Lakes Research Division, Program in Water Resource Science and Biological Station, University of Michigan, Ann Arbor, M148109 (U.S.A.) (Accepted for publication 15 February 1988) ABSTRACT Fortner, S.L. and White, D.S., 1988. Interstitial water patterns: a factor influencing the distri- butions of some lotic aquatic vascular macrophytes. Aquat. Bot., 31: 1-12. The distributions of 9 species of aquatic vascular macrophytes were examined in relation to interstitial water patterns (based on temperature) in the beds of three northern Michigan (U.S.A.) streams. Ranunculus septentrionalis Poir., Caltha palustris L. and Nasturtium officinale R.Br. were associated with areas of groundwater discharge. Sparganium chlorocarpum Rydb., Veronica catenata Penn., Potamogeton fili/ormis Pers. and P. richardsonii (Benn.) Rydb. occurred most often at the downstream end of a hyporheic zone (corresponding to the foot of a riffle) where interstitial water was of surface origin. Sagittaria lati[olia Willd. occurred where interstitial tem- peratures were cool; the water origin was not determined. Potamogeton gramineus L. occurred most often where interstitial temperatures were warm, primarily at the upstream ends and middles of hyporheic zones (heads of riffles) in areas of surface-water infiltration. Complex patterns of interstitial water movement and related physicochemical complexity combined with differences in plant requirements, in part, may determine observed local distributions. INTRODUCTION Factors known to control the distribution and growth of lotic aquatic ma- crophytes include turbulence, light, surface-water chemistry, surface-water temperature, flow, sediment structure and chemistry, and other biota (Spence, 1967; Peltier and Welch, 1968; Kullberg, 1974; Hutchinson, 1975; Beal 1977; Haslam, 1978). -
2014 Aquatic Plant Survey Report.Pdf
Lake Iroquois Aquatic Plant Survey Prepared For: Lake Iroquois Association Prepared By: George W. Knoecklein Northeast Aquatic Research, LLC Mansfield, CT February 13, 2015 1 | Page Northeast Aquatic Research Background Lake Iroquois is situated in northwestern Vermont and is bordered by the towns of Hinesberg, Williston, and Richmond. The lake has a surface area of approximately 244 acres with maximum and average depths of 37 feet and 19 feet, respectively (LIA SOTL Report). Lake Iroquois is considered to be a eutrophic lake by LIA due to phosphorus concentrations that exceed the threshold of 14 ppb, and chlorophyll-a concentrations that exceed the threshold of 7 ppb. 2014 Project Goal Northeast Aquatic Research (NEAR) was showers. Due to these factors, venturing hired to conduct an aquatic plant survey of out to the center of the lake to investigate Lake Iroquois in order to provide an plant growth around the center island was accurate, up-to-date estimate of the omitted due to rough water, however coverage of invasive Eurasian milfoil. This shoreline surveying was completed without invasive non-native aquatic plant was problem. reported (LIA SOTL Report) to be first Map 1 – Locations of waypoints made discovered in Lake Iroquois in 1990 near during NEAR 2014 survey the state fishing access. Our survey was conducted on September 11, 2014 and consisted of observing aquatic plant species presence and growth form at 136 locations (waypoints) around the shoreline of the lake, Map 1. Waypoints were typically made at regular 200 feet intervals. Plant cover between points was observed for similarity to last made point. -
Phenotypic Plasticity in Potamogeton (Potamogetonaceae )
Folia Geobotanica 37: 141–170, 2002 PHENOTYPIC PLASTICITY IN POTAMOGETON (POTAMOGETONACEAE ) Zdenek Kaplan Institute of Botany, Academy of Sciences of the Czech Republic, CZ-252 43 Prùhonice, Czech Republic; fax +420 2 6775 0031, e-mail [email protected] Keywords: Classification, Cultivation experiments, Modification, Phenotype, Taxonomy, Variability, Variation Abstract: Sources of the extensive morphological variation of the species and hybrids of Potamogeton were studied, especially from the viewpoint of the stability of the morphological characters used in Potamogeton taxonomy. Transplant experiments, the cultivation of clones under different values of environmental factors, and the cultivation of different clones under uniform conditions were performed to assess the proportion of phenotypic plasticity in the total morphological variation. Samples from 184 populations of 41 Potamogeton taxa were grown. The immense range of phenotypic plasticity, which is possible for a single clone, is documented in detail in 14 well-described examples. The differences among distinct populations of a single species observed in the field were mostly not maintained when grown together under the same environmental conditions. Clonal material cultivated under different values of environmental factors produced distinct phenotypes, and in a few cases a single genotype was able to demonstrate almost the entire range of morphological variation in an observed trait known for that species. Several characters by recent literature claimed to be suitable for distinguishing varieties or even species were proven to be dependent on environmental conditions and to be highly unreliable markers for the delimitation of taxa. The unsatisfactory taxonomy that results when such classification of phenotypes is adopted is illustrated by three examples from recent literature. -
DCR Guide to Aquatic Plants in Massachusetts
A GUIDE TO AQUATIC PLANTS IN MASSACHUSETTS Contacts: Massachusetts Department of Conservation and Recreation, Lakes & Ponds Program www.mass.gov/lakesandponds Massachusetts Department of Environmental Protection www.mass.gov/dep Northeast Aquatic Nuisance Species Panel www.northeastans.org Massachusetts Congress of Lakes & Ponds Associations (COLAP) www.macolap.org '-I... Printed on Recycled Paper 2016 A Guide to Aquatic Plants in Massachusetts Common Name Scientific Name Page No. Submerged Plants ........................................................................................................................9 Arrowhead .............................................................Sagittaria .......................................................................11 Bladderwort...........................................................Utricularia ......................................................................17 Common Bladderwort ...................................Utricularia vulgaris ........................................................18 Flatleaf Bladderwort ......................................Utricularia intermedia ....................................................18 Little Floating Bladderwort ............................Utricularia radiata .........................................................18 Purple Bladderwort........................................Utricularia purpurea.......................................................18 Burreed..................................................................Sparganium -
A Morphological, Anatomical and Isozyme Study of Potamogeton ×Schreberi: Confirmation of Its Recent Occurrence in Germany and First Documented Record in France
Preslia, Praha, 76: 141–161, 2004 141 A morphological, anatomical and isozyme study of Potamogeton ×schreberi: confirmation of its recent occurrence in Germany and first documented record in France Morfologie, anatomie lodyhy a isozymová spektra u Potamogeton ×schreberi: potvrzení současného výsky- tu v Německu a první údaj pro Francii Zdeněk K a p l a n1 & Peter Wo l f f 2 1Institute of Botany, Academy of Sciences of the Czech Republic, CZ-252 43 Průhonice, Czech Republic, e-mail: [email protected]; 2Richard-Wagner-Str. 72, Dudweiler, D-66125 Saarbrücken, Germany Kaplan Z. & Wolff P. (2004): A morphological, anatomical and isozyme study of Potamogeton ×schreberi: confirmation of its recent occurrence in Germany and first documented record in France. – Preslia, Praha, 76: 141–161. A combined study of morphology, stem anatomy and isozyme patterns was used to reveal the iden- tity of sterile plants from two rivers on the Germany/France border. A detailed morphological exam- ination proved that the putative hybrid is clearly intermediate between Potamogeton natans and P. nodosus. The stem anatomy had characteristics of both species. The most compelling evidence came from the isozyme analysis. The additive “hybrid” banding patterns of the six enzyme systems studied indicate inheritance from P.natans and P.nodosus. In contrast, other morphologically simi- lar hybrids were excluded: P. ×gessnacensis (= P.natans × P.polygonifolius) by all the enzyme sys- tems, P. ×fluitans (= P. lucens × P. natans) by AAT, EST and 6PGDH, and P. ×sparganiifolius (= P.gramineus × P.natans) by AAT and EST. All samples of P. ×schreberi are of a single multi-en- zyme phenotype, suggesting that they resulted from a single hybridization event and that the pres- ent-day distribution of P. -
Potamogetonaceae Pondweed Family
Potamogetonaceae pondweed family Only two genera form the pondweeds, numbering about 90 species worldwide. All have perfect flowers arranged in a spike or head. Perianth is absent; flowers are four-merous. Some species exhibit Page | 1421 heterophyllous leaves. An important character is the presence or absence of lacunae, rows of colourless cells on either side of the central axis. All perennial, they are an important food source for waterfowl. (Haynes and Hellquist, 1996, 2000) Stipular sheaths of submersed leaves free from base of leaf blade, or adnate <½ Potamogeton length of stipule; leaves both submersed and floating or all submersed, submersed blades translucent, not channelled, flattened; peduncle stiff, if long enough then projecting inflorescence above surface of water. Stipular sheaths of submersed leaves adnate to base of leaf blade for 2/3 or more Stuckenia length of stipule; leaves all submersed, blades opaque, channelled, turgid; peduncle flexible, not projecting inflorescence above surface of water. Potamogeton L. pondweeds Herbaceous aquatic species, they are found in estuarine waters or fresh water. The leaves may be aerial, emergent, floating or wholly submerged. All are alternate along the rooting stems. The flower spikes are sheathed by stipules in bud, expanding upon a peduncle to the surface as they mature. Fruit is a drupe, soon becoming compressed. Hybridization is common as are sterile plants. The following key is of some field value, if material is mature. Morphological characters are often not sufficient to separate some of the more difficult species and their hybrids. Key to species A. Plants heterophyllous, floating and submerged. B B. Leaves large, submerged 4-6mm wide, >25 veins, may be Potamogeton amplifolius plicate. -
Control of Potamogeton Crispus and Myriophyllum Spicatum in Crystal Lake, Middletown, CT
The Connecticut Agricultural Experiment Station, New Haven, CT Control of Potamogeton crispus and Myriophyllum spicatum in Crystal Lake, Middletown, CT 2006 - 2008 Bulletin Gregory J. Bugbee January 2009 Prepared for the Connecticut Department of Environmental Protection Pursuant to aquatic vegetation control permit # 07147 Table of Contents 1. Introduction……………………………………………………………….……. 3 2. Objectives ……………………………………………………………………… 4 3. Materials and Methods ………………………………………………………. 5 Visual surveys…………..…………………………………………………….. 5 Transects………………..…………………………………………………….. 5 Georeferenced grid …..…..………………………………………………….. 7 Water chemistry ………….………………………………………………….. 7 Installation and removal of limnobarriers …….……………………………. 8 Application of herbicide ……………………………………….…………….. 8 6. Results and Discussion …………..…...............................................…….. 8 Visual Survey ……………………………………………………………….... 8 Transects ……………………………………………….…………………….. 8 Georeferenced grid ………………………………………………………….. 9 Presence of Protected Plant Species …………………………………..… 14 Water Chemistry ………………………………………………………….… 14 8. Conclusions ………………………………………………………………... 16 9. Acknowledgements ……………………………………………………….. 16 10. References …………………………………………………………..…….. 17 11. Appendix. ……………………………………………………………..…….. 18 Chain of custody – water chemistry …………………………………………19 Herbicide Permit ……………………………………………………………….21 2 Control of Potamogeton crispus and Myriophyllum spicatum in Crystal Lake, Middletown, CT 2006-2008 Figure 1. Potamogeton crispus reaching surface in Crystal Lake. Introduction: -
Massachusetts 2012 Final State Wetland Plant List
MASSACHUSETTS 2012 FINAL STATE WETLAND PLANT LIST Lichvar, R.W. 2012. The National Wetland Plant List. ERDC/CRREL TR‐12‐11. Hanover, NH: U.S. Army Corps of Engineers, Cold Regions Research and Engineering Laboratory. http://acwc.sdp.sirsi.net/client/search/asset:asset?t:ac=$N/1012381 User Notes: 1) Plant species not listed are considered UPL for wetland delineation purposes. 2) A few UPL species are listed because they are rated FACU or wetter in at least one Corps region. 3) Some state boundaries lie within two or more Corps Regions. If a species occurs in one of the regions but not the other, its rating will be shown in one column and the other column will show a dash. For example, there are two Corps regions in North Dakota, the GP and the MW. Agrostis exarata occurs in the GP but not the MW, so it is listed as: Species Authorship GP MW Common Name Agrostis exarata Trin. FACW ‐ Spiked Bent Species Authorship NCNE Common Name Abies balsamea (L.) P. Mill. FAC Balsam Fir Abies concolor (Gord. & Glend.) Lindl. ex Hildebr. UPL White Fir Abutilon theophrasti Medik. FACU Velvetleaf Acalypha gracilens Gray FACU Slender Three‐Seed‐Mercury Acalypha rhomboidea Raf. FACU Common Three‐Seed‐Mercury Acalypha virginica L. FACU Virginia Three‐Seed‐Mercury Acer negundo L. FAC Ash‐Leaf Maple Acer nigrum Michx. f. FACU Black Maple Acer pensylvanicum L. FACU Striped Maple Acer platanoides L. UPL Norway Maple Acer rubrum L. FAC Red Maple Acer saccharinum L. FACW Silver Maple Acer saccharum Marsh. FACU Sugar Maple Acer spicatum Lam.