Vallisneria Spiralis L
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27April12acquatic Plants
International Plant Protection Convention Protecting the world’s plant resources from pests 01 2012 ENG Aquatic plants their uses and risks Implementation Review and Support System Support and Review Implementation A review of the global status of aquatic plants Aquatic plants their uses and risks A review of the global status of aquatic plants Ryan M. Wersal, Ph.D. & John D. Madsen, Ph.D. i The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of speciic companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned.All rights reserved. FAO encourages reproduction and dissemination of material in this information product. Non-commercial uses will be authorized free of charge, upon request. Reproduction for resale or other commercial purposes, including educational purposes, may incur fees. Applications for permission to reproduce or disseminate FAO copyright materials, and all queries concerning rights and licences, should be addressed by e-mail to [email protected] or to the Chief, Publishing Policy and Support Branch, Ofice of Knowledge Exchange, -
Ecophysiological and Anatomical Responses of Vallisneria Natans to Nitrogen and Phosphorus Enrichment
Knowledge and Management of Aquatic Ecosystems (2012) 405, 05 http://www.kmae-journal.org c ONEMA, 2012 DOI: 10.1051/kmae/2012011 Ecophysiological and anatomical responses of Vallisneria natans to nitrogen and phosphorus enrichment Y. Wa n g (1,2),G.Gao(1),B.Qin(1),X.Wang(1) Received January 4, 2012 Revised March 24, 2012 Accepted April 26, 2012 ABSTRACT Key-words: Here, we describe an experiment using four nitrogen (N) and phospho- nutrient rus (P) concentrations to investigate the effects of nutrient enrichment on enrichment, the submersed macrophyte Vallisneria natans (tape grass) grown in a sand photosynthesis, culture medium. The objective of this study was to examine the influence morphological of nutrient enrichment in the water column on V. natans, especially with characteristics, regard to anatomical structures. The results showed both the absolute anatomical growth rate (AGR) and intrinsic efficiency of light energy conversion of structure, PSII (Fv/Fm) decreased with increasing nutrient levels. Root morphological Vallisneria characteristics, including the total root length (L), root surface area (SA), natans projected root area (PA), total root volume (V), average root diameter (AD), total root length per volume (LPV), total tips (T) and total forks (F), also showed a generally negative relationship with increasing nutrient concen- trations. The anatomical structures of stolons and leaves also changed with nutrient enrichment. The shrinkage of aerenchyma and disappear- ance of starches and chloroplasts were the main structural changes lead- ing to poor growth. These phenomena, especially the anatomical changes, might be the mechanism underlying the effect of nutrient enrichment on V. natans growth. -
Aquarium Plants
Aquarium Plants Kingdom: Plantae Conditions for Customer Ownership We hold permits allowing us to transport these organisms. To access permit conditions, click here. Never purchase living specimens without having a disposition strategy in place. Shipment of aquatic plants is prohibited in Puerto Rico. Shipment of Cabomba is restricted in CA, CT, MA, ME, VT, and WA. In all other cases, the USDA does not require any special permits to receive aquatic plants. However, in order to continue to protect our environment, you must house your aquatic plants in an aquarium. Under no circum- stances should you release your plants into the wild. Primary Hazard Considerations Always wash your hands thoroughly before and after you handle your aquatic plants, or anything it has touched. Availability Aquatic plants are generally available year round, and can be found in freshwater lakes and ponds. They are collected, so shortages may occur. The aquatic plants come packaged in plastic bags. Once received, open package and, using tap water, gently rinse away any debris or broken-off pieces. Some plants come in jars; remove lid and place in tank. Your plants do not need to be acclimated. Aquarium Needs Habitat: • Water from the tap in most cases contains chlorine, which can be detrimental to the health of your plants and aquatic animals. De-chlorinate your water by using a commercial chemical designed to do so, such as Ammonia/Chlorine Detoxifier, or by leaving your water out in an open container for 24–48 hours. Tropical plants need temperatures ranging from 66–77°F. For an aquarium to function well, a Filtration System 21 W 3535 is needed. -
Taxonomy Monocots
Taxonomy Monocots- 1. Typhaceae - commonly called the Cattail Family (aceae ending means family). These are emergent, rhizomatons, found in fresh or brackish waters. • Typha (genus) domingensis (species): This is the species found in AZ. • Typha latifolia 2. Potamogetonaceae - the Pondweed Family. This family is rooted and submerged. • Potamogeton: commonly known as Pondweeds; many species are found. • Ruppia: commonly known as Widgeon grass; found in fresh or brackish waters. • Zannichelia: commonly known as Horned Pondweed; found in fresh or brackish waters. • Zoestra: marine seagrass. • Halodule: marine seagrass. • Cymodocea: marine seagrass. • Phyllospadix: marine seagrass. 3. Najadaceae - the Niad Family. This family is also rooted and submerged; there is only one genus. • Najas marina: commonly known as the spiny niad; found in brackish waters. Typically known as a problem plant because it grows course and very quickly. 4. Hydrocharitaceae - the Frogbit Family. This family is rooted and submerged, and is found in fresh and marine waters. • Anacharis densa: commonly known as Waterweed, also called Elodea. A very common aquarium plant, considered a problem plant in freshwater lakes. • Halophila: found in marine habitats. • Thalassia: commonly known as Turtlegrass (another type of seagrass); found in marine habitats. • Vallisneria: commonly known as Wild Celery, a common food for ducks and other water fowl; found in freshwater. 5. Graminaceae (Poaceae)- the Grass Family. Grasses can be identified by the swollen base of each leaf where it meets the stem. This is called a ligule. There are 22 genera, important ones are listed. Most of these are emergent and rooted. • Phragmites australis: commonly known as the Giant Reed, similar to Arundo; found in freshwater. -
Effects of Water Level Fluctuation on Vallisneria Americana Michx Growth
J. Aquat. Plant Manage. 46: 117-119 NOTES Effects of Water Level Fluctuation on Vallisneria americana Michx Growth CHETTA S. OWENS1, R. M. SMART1 AND G. O. DICK1 INTRODUCTION 122 cm. Water level was maintained by continuous low-flow from nearby Lewisville Lake. Wild celery (Vallisneria americana Michx.) is a native, sub- In July 2003, six containers were harvested from each mersed aquatic plant found in the eastern United States depth, processed into aboveground and belowground mate- westward to South Dakota and south throughout the Gulf rial, and dried at 55 C in a Blue M forced-air oven (General Coast states (Korschgen and Green 1988, USDA 2007). An Signal, Atlanta, GA) to a constant weight. Rosettes (daughter important food source for waterfowl and aquatic mammals plants) were counted and maximum leaf length was mea- (Fassett 1957), wild celery also provides habitat for fish, sedi- sured. At this time, remaining containers from the four ment stabilization benefits, improved water quality and clari- depth treatments were placed at a same depth (91 cm) to ty, and can slow or prevent the invasion of nonindigenous evaluate effects of increasing, stable, and decreasing water aquatic plant species (Smart 1993, 1995, Smart et al. 1994, levels on wild celery growth. After four weeks (August 2003), Smart and Dick 1999). containers were harvested and processed as described above. Numerous constructed reservoirs in the United States are Rosette number, maximum length, aboveground, and be- devoid of aquatic vegetation, exhibit some degree of water lowground biomass means were compared using a one-way level fluctuations, and lack propagule sources for timely nat- ANOVA and LSD (least significant differences) test at p = ural establishment of wild celery to occur (Smart 1993, 1995, 0.05 level of significance (Statistix Analytical Software, Talla- Smart et al. -
The Herbivorous Insect Fauna of a Submersed Weed, Hydrilla Verticillata (Alismatales: Hydrocharitaceae)
SESSION 5 Weeds of Aquatic Systems and Wetlands Proceedings of the X International Symposium on Biological Control of Weeds 307 4-14 July 1999, Montana State University, Bozeman, Montana, USA Neal R. Spencer [ed.]. pp. 307-313 (2000) The Herbivorous Insect Fauna of a Submersed Weed, Hydrilla verticillata (Alismatales: Hydrocharitaceae) C. A. BENNETT1 and G. R. BUCKINGHAM2 1 Department of Entomology and Nematology, University of Florida, and 2 USDA-ARS 1,2 Florida Biological Control Laboratory, P.O. Box 147100, Gainesville, Florida 32614-7100, USA Abstract Although relatively few insects have been reported to feed on submersed aquatic plants, field surveys on Hydrilla verticillata (L. F.) Royle for biological control agents have demonstrated that insect herbivores should be expected when surveying submersed aquatic plants in the native ranges. Beetles, or Coleoptera, especially the weevils (Curculionidae), are important herbivores. Weevils attack submersed plant species both when water is present and when water is absent during dry periods which leave the plants exposed. Pupal success appears to be the major determinant of weevil life cycle strategies. Donaciine leaf beetles (Chrysomelidae) attack the roots or crowns of submersed species, but their feeding and damage is difficult to determine. Leaf-mining Hydrellia flies (Diptera: Ephydridae) are diverse and common on submersed species. Other flies, the midges (Chironomidae), are also common on submersed species, but many utilize the plants only for shelter. However, midge larvae ate the apical meristems on the tips of hydrilla stems. Aquatic caterpillars (Lepidoptera: Pyralidae) are the herbivores most eas- ily observed on submersed species because of their large size and conspicuous damage, but their host ranges might be too broad for use as biological control agents. -
Evolution Along the Crassulacean Acid Metabolism Continuum
Review CSIRO PUBLISHING www.publish.csiro.au/journals/fpb Functional Plant Biology, 2010, 37, 995–1010 Evolution along the crassulacean acid metabolism continuum Katia SilveraA, Kurt M. Neubig B, W. Mark Whitten B, Norris H. Williams B, Klaus Winter C and John C. Cushman A,D ADepartment of Biochemistry and Molecular Biology, MS200, University of Nevada, Reno, NV 89557-0200, USA. BFlorida Museum of Natural History, University of Florida, Gainesville, FL 32611-7800, USA. CSmithsonian Tropical Research Institute, PO Box 0843-03092, Balboa, Ancón, Republic of Panama. DCorresponding author. Email: [email protected] This paper is part of an ongoing series: ‘The Evolution of Plant Functions’. Abstract. Crassulacean acid metabolism (CAM) is a specialised mode of photosynthesis that improves atmospheric CO2 assimilation in water-limited terrestrial and epiphytic habitats and in CO2-limited aquatic environments. In contrast with C3 and C4 plants, CAM plants take up CO2 from the atmosphere partially or predominantly at night. CAM is taxonomically widespread among vascular plants andis present inmanysucculent species that occupy semiarid regions, as well as intropical epiphytes and in some aquatic macrophytes. This water-conserving photosynthetic pathway has evolved multiple times and is found in close to 6% of vascular plant species from at least 35 families. Although many aspects of CAM molecular biology, biochemistry and ecophysiology are well understood, relatively little is known about the evolutionary origins of CAM. This review focuses on five main topics: (1) the permutations and plasticity of CAM, (2) the requirements for CAM evolution, (3) the drivers of CAM evolution, (4) the prevalence and taxonomic distribution of CAM among vascular plants with emphasis on the Orchidaceae and (5) the molecular underpinnings of CAM evolution including circadian clock regulation of gene expression. -
Vallisneria Spiralis L. (Hydrocharitaceae) in Lakes in the Vicinity of Konin (Kujawy Lakeland)
BRC Biodiv. Res. Conserv. 1-2: 154-158, 2006 www.brc.amu.edu.pl Vallisneria spiralis L. (Hydrocharitaceae) in Lakes in the Vicinity of Konin (Kujawy Lakeland) Andrzej Hutorowicz The Stanis≥aw Sakowicz Inland Fisheries Institute, Oczapowskiego 10, 10-719 Olsztyn-Kortowo, Poland, e-mail: [email protected] Abstract: In the last eleven years Vallisneria spiralis L. colonized three lakes situated in the Kujawy Lakeland, i.e. Lake LicheÒskie, Lake Wπsosko-MikorzyÒskie and Lake Pπtnowskie, which in 1958 were included in the open cooling system of heat and power stations. The aim of the studies conducted in 2004 was to determine the seasonal dynamics of this species as dependent upon thermal variations. Phenological observations, temperature measurements, and examinations of changes in the spatial structure of V. spiralis communities at selected localities were performed from the end of April to the end of October. A correlation was observed between the life-cycle of V. spiralis and water temperature. V. spiralis was also found to be tolerant of a short photoperiod. Apart from great vegetative reproduction ability, these were the main factors that decided about the biogeographical success of this species. Key words: Vallisneria spiralis, Hydrocharitaceae, macrophytes, adventitious plant, lake, heated water 1. Introduction sp. This characteristic combination of the above species showed that these communities should be included in Vallisneria spiralis L. ñ a hydrophyte whose natu- the association Potamo perfoliati-Vallisnerietum ral range of occurrence comprises countries of the tropi- spiralis Losev & V. Gloub 1987, described from the cal and subtropical zone in Asia, Africa, America and Lower Volga River Valley (Gπbka 2002). -
Aquatic Plant Identification Guide Submersed (Underwater)
Aquatic Plant Identification Guide Submersed (underwater) Snohomish County Surface Water Management Lake Management Program 425-388-3204 [email protected] www.lakes.surfacewater.info Native Aquatic Plants • Part of a healthy lake system; benefit people and wildlife • Good for fish – provide food and cover, act as a “nursery” for juvenile fish. • Have natural controls - animals that eat them • Usually do not cause major problems Large-Leaf The two most common native Pondweed aquatic plants in Snohomish County are: • Elodea Elodea • Large-Leaf Pondweed Invasive Aquatic Plants • Grow densely, with few natural enemies; adaptable • Out-compete & displace native plants • Create nuisance conditions in lakes: disrupting swimming, fishing, and boating • Once established - high cost to control Submersed invasive plants in Snohomish County include: • Eurasian watermilfoil • Brazilian Elodea • Curly-leaf pondweed Eurasian watermilfoil • Grass-leaved saggitaria You Can Help Prevent Invasive Plants • Prevention is best approach - much cheaper to prevent than eradicate • Clean, drain and dry your boat •Before launching and when leaving Native Milfoils Eurasian watermilfoil Whorls of 4 with more than 14 leaflet pairs • Usually less than 14 leaflet • Most problematic aquatic pairs – stems green plant in Washington • Somewhat stiff plants • Feathery leaves in whorls • Known to be in Crystal of 4 – stems often pink Lake, Lake Loma, Lake • Usually >14 leaflet pairs Serene, Riley Lake, & • Spreads by fragments Shadow Lake Eurasian watermilfoil Myriophyllum spicatum Lakes in Snohomish County with known Eurasian Watermilfoil infestations*: • Lake Goodwin • Nina Lake (Private Lake) • Lake Shoecraft • Silver Lake (City of Everett) • Lake Roesiger • Lake Tye (City of Monroe) • Lake Stevens • Lake Ballinger (City of Mountlake • Gissberg/Twin Lakes Terrace & Edmonds) *Lake Serene and Martha Lake (off 164th) formerly had Eurasian watermilfoil, but the plant has been eradicated through control efforts DO NOT RAKE OR CUT PLANTS - each fragment will create new plants. -
The Biomass and Physiological Responses of Vallisneria Natans (Lour.) Hara to Epiphytic Algae and Different Nitrate-N Concentrations in the Water Column
water Article The Biomass and Physiological Responses of Vallisneria natans (Lour.) Hara to Epiphytic Algae and Different Nitrate-N Concentrations in the Water Column Fenli Min 1,2, Jincheng Zuo 3, Yi Zhang 1, Qingwei Lin 1,2, Biyun Liu 1,*, Jian Sun 1,2, Lei Zeng 1,2, Feng He 1,* and Zhenbin Wu 1 1 State Key Laboratory of Freshwater Ecology and Biotechnology, Institute of Hydrobiology, Chinese Academy of Sciences, Wuhan 430072, China; [email protected] (F.M.); [email protected] (Y.Z.); [email protected] (Q.L.); [email protected] (J.S.); [email protected] (L.Z.); [email protected] (Z.W.) 2 University of Chinese Academy of Sciences, Beijing 100049, China 3 School of Life Science, Ludong University, Yantai 264025, China; [email protected] * Correspondence: [email protected] (B.L.); [email protected] (F.H.); Tel.: +86-27-6878-0038 (B.L.); +86-27-6878-0832 (F.H.) Received: 4 September 2017; Accepted: 2 November 2017; Published: 22 November 2017 Abstract: Increasing N concentration and the high density of epiphytic algae are both key factors leading to the decline of submerged macrophytes in many eutrophic lakes. In order to investigate the impacts of increased nitrate-N concentration and the growth of epiphytic algae on the decline of submerged vegetation, we conducted a 2 × 4 factorial experiment with the submerged macrophyte Vallisneria natans (Lour.) Hara by measuring the biomass of plants and some physiological indexes in leaves of V. natans under four nitrate-N concentrations in the water column (0.5, 2.5, 5, and 10 mg/L) and two epiphytic groups (epiphytic algae group and no epiphytic algae group). -
American Eelgrass (Vallisneria Americana) ERSS
American Eelgrass (Vallisneria americana) Ecological Risk Screening Summary U.S. Fish & Wildlife Service, July 2020 Revised, January 2021 Web Version, 4/8/2021 Organism Type: Plant Overall Risk Assessment Category: Uncertain Photo: mfeaver. Licensed under Attribution-Non Commercial 4.0 International (CC BY-NC 4.0). Available: https://www.inaturalist.org/photos/58892818. (July 2020). 1 Native Range and Status in the United States Native Range From Maiz-Tome (2016): “The species is widespread across eastern North America, northern Mesoamerica and the Caribbean (eMonocot Team 2015).” 1 From Randhawa (2018): “The native range of Vallisneria americana incudes Asia, Australia, North America, Central America, and South America.” “Vallisneria americana is widely distributed in eastern North America and is present in Canada, Cuba, Dominican Republic, Guatemala, Haiti, Honduras, Jamaica, Mexico and the United States. (IUCN Red List of Threatened Species).” Status in the United States Vallisneria americana is native to parts of the contiguous United States. According to Nature Serve (2021) Vallisneria americana is native to the following states: Alabama, Arizona, Arkansas, Connecticut, Delaware, District of Columbia, Florida, Georgia, Idaho, Illinois, Indiana, Iowa, Kentucky, Louisiana, Maine, Maryland, Massachusetts, Michigan, Minnesota, Mississippi, Missouri, Nebraska, Nevada, New Hampshire, New Jersey, New Mexico, New York, North Carolina, North Dakota, Ohio, Oklahoma, Oregon, Pennsylvania, Rhode Island, South Carolina, South Dakota, Tennessee, Texas, Vermont, Virginia, Washington, West Virginia, and Wisconsin. From Randhawa (2018): “Vallisneria americana was observed growing in water district pond in Shasta county [sic] in 2007. Vallisneria species have been intercepted by county and at CDFA border stations in 2011, 2016 and 2018. This species is introduced to California.” “Vallisneria americana has been observed growing in a man-made pond in a very limited area of California. -
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