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"National List of Vascular Plant Species That Occur in Wetlands: 1996 National Summary."
Intro 1996 National List of Vascular Plant Species That Occur in Wetlands The Fish and Wildlife Service has prepared a National List of Vascular Plant Species That Occur in Wetlands: 1996 National Summary (1996 National List). The 1996 National List is a draft revision of the National List of Plant Species That Occur in Wetlands: 1988 National Summary (Reed 1988) (1988 National List). The 1996 National List is provided to encourage additional public review and comments on the draft regional wetland indicator assignments. The 1996 National List reflects a significant amount of new information that has become available since 1988 on the wetland affinity of vascular plants. This new information has resulted from the extensive use of the 1988 National List in the field by individuals involved in wetland and other resource inventories, wetland identification and delineation, and wetland research. Interim Regional Interagency Review Panel (Regional Panel) changes in indicator status as well as additions and deletions to the 1988 National List were documented in Regional supplements. The National List was originally developed as an appendix to the Classification of Wetlands and Deepwater Habitats of the United States (Cowardin et al.1979) to aid in the consistent application of this classification system for wetlands in the field.. The 1996 National List also was developed to aid in determining the presence of hydrophytic vegetation in the Clean Water Act Section 404 wetland regulatory program and in the implementation of the swampbuster provisions of the Food Security Act. While not required by law or regulation, the Fish and Wildlife Service is making the 1996 National List available for review and comment. -
Macrophyte Structure in Lotic-Lentic Habitats from Brazilian Pantanal
Oecologia Australis 16(4): 782-796, Dezembro 2012 http://dx.doi.org/10.4257/oeco.2012.1604.05 MACROPHYTE STRUCTURE IN LOTIC-LENTIC HABITATS FROM BRAZILIAN PANTANAL Gisele Catian2*, Flávia Maria Leme2, Augusto Francener2, Fábia Silva de Carvalho2, Vitor Simão Galletti3, Arnildo Pott4, Vali Joana Pott4, Edna Scremin-Dias4 & Geraldo Alves Damasceno-Junior4 2Master, Program in Plant Biology, Federal University of Mato Grosso do Sul, Center for Biological Sciences and Health, Biology Department. Cidade Universitária, s/no – Caixa Postal: 549 – CEP: 79070-900, Campo Grande, MS, Brazil. 3Master, Program in Ecology and Conservation, Federal University of Mato Grosso do Sul, Center for Biological Sciences and Health, Biology Department. Cidade Universitária, s/no – Caixa Postal: 549 – CEP: 79070-900, Campo Grande, MS, Brazil. 4Lecturer, Program in Plant Biology, Federal University of Mato Grosso do Sul, Center for Biological Sciences and Health, Biology Department. Cidade Universitária, s/no – Caixa Postal: 549 – CEP: 79070-900, Campo Grande, MS, Brazil. E-mail: [email protected]*, [email protected], [email protected], [email protected], [email protected], arnildo. [email protected], [email protected], [email protected], [email protected] ABSTRACT The goal of this study was to compare the vegetation structure of macrophytes in an anabranch-lake system. Sampling was carried out at flood in three types of aquatic vegetation, (wild-rice, floating meadow and Polygonum bank) in anabranch Bonfim (lotic) and in lake Mandioré (lentic) in plots along transects, to estimate the percent coverage and record life forms of species. We collected 59 species in 50 genera and 28 families. -
The Jepson Manual: Vascular Plants of California, Second Edition Supplement II December 2014
The Jepson Manual: Vascular Plants of California, Second Edition Supplement II December 2014 In the pages that follow are treatments that have been revised since the publication of the Jepson eFlora, Revision 1 (July 2013). The information in these revisions is intended to supersede that in the second edition of The Jepson Manual (2012). The revised treatments, as well as errata and other small changes not noted here, are included in the Jepson eFlora (http://ucjeps.berkeley.edu/IJM.html). For a list of errata and small changes in treatments that are not included here, please see: http://ucjeps.berkeley.edu/JM12_errata.html Citation for the entire Jepson eFlora: Jepson Flora Project (eds.) [year] Jepson eFlora, http://ucjeps.berkeley.edu/IJM.html [accessed on month, day, year] Citation for an individual treatment in this supplement: [Author of taxon treatment] 2014. [Taxon name], Revision 2, in Jepson Flora Project (eds.) Jepson eFlora, [URL for treatment]. Accessed on [month, day, year]. Copyright © 2014 Regents of the University of California Supplement II, Page 1 Summary of changes made in Revision 2 of the Jepson eFlora, December 2014 PTERIDACEAE *Pteridaceae key to genera: All of the CA members of Cheilanthes transferred to Myriopteris *Cheilanthes: Cheilanthes clevelandii D. C. Eaton changed to Myriopteris clevelandii (D. C. Eaton) Grusz & Windham, as native Cheilanthes cooperae D. C. Eaton changed to Myriopteris cooperae (D. C. Eaton) Grusz & Windham, as native Cheilanthes covillei Maxon changed to Myriopteris covillei (Maxon) Á. Löve & D. Löve, as native Cheilanthes feei T. Moore changed to Myriopteris gracilis Fée, as native Cheilanthes gracillima D. -
Tropical Forages
Tropical Forages Hymenachne amplexicaulis Scientific name Hymenachne amplexicaulis (Rudge) Nees Synonyms Aquatic or sub-aquatic perennial with coarse culms Leaves to >3cm wide with stem- Basionym: Panicum amplexicaule Rudge clasping auricles at base Family/tribe Family: Poaceae (alt. Gramineae) subfamily: Panicoideae tribe: Paspaleae subtribe: Otachyriinae. Morphological description A perennial, stoloniferous/rhizomatous grass, with robust, erect or ascending culms 1–2.5 m high and to Aquatic culm with nodal rooting (cv. >12 mm thick, and prostrate stems that run on wet Olive) ground, or float on water, developing adventitious roots. Stems glabrous, pithy. Leaves glossy green in colour, Inflorescence a narrow spike-like largely glabrous; sheaths often spongy; blades mostly panicle linear-lanceolate, 10–45 cm long and to >3 cm wide, cordate, auriculate and clasping at base; ligule an eciliate membrane, 1–2.5 mm long. Panicle narrow, spikelike, cylindrical, 20–50 cm long, 1–2 cm across, sometimes with 2 to a few long, upright branches. Spikelets lanceolate, dorsi-ventrally compressed, upright, 3–4 (–5) mm long and 1 mm diameter; c. 2.3 million seeds/kg. Caryopsis ellipsoid, easily detached, 1–2 mm long and 0.6 mm diameter. Prolific seed production Note: Morphologically similar to, but distinct from Hymenachne acutigluma (Steud.) Gilliland, which is native to Continental Asia, Malesia and Australasia. Leaves and inflorescence Similar species H. amplexicaulis: leaf base cordate-auriculate, stem- clasping (amplexicaul). H. acutigluma (Steud.) Gilliland (syn. Hymenachne pseudointerrupta Müll. Hal.): leaf base rounded to sub- cordate. Native to S and SE Asia, and northern Australia. Checking maturity in seed production Common names area (cv. -
Specificity in Legume-Rhizobia Symbioses
International Journal of Molecular Sciences Review Specificity in Legume-Rhizobia Symbioses Mitchell Andrews * and Morag E. Andrews Faculty of Agriculture and Life Sciences, Lincoln University, PO Box 84, Lincoln 7647, New Zealand; [email protected] * Correspondence: [email protected]; Tel.: +64-3-423-0692 Academic Editors: Peter M. Gresshoff and Brett Ferguson Received: 12 February 2017; Accepted: 21 March 2017; Published: 26 March 2017 Abstract: Most species in the Leguminosae (legume family) can fix atmospheric nitrogen (N2) via symbiotic bacteria (rhizobia) in root nodules. Here, the literature on legume-rhizobia symbioses in field soils was reviewed and genotypically characterised rhizobia related to the taxonomy of the legumes from which they were isolated. The Leguminosae was divided into three sub-families, the Caesalpinioideae, Mimosoideae and Papilionoideae. Bradyrhizobium spp. were the exclusive rhizobial symbionts of species in the Caesalpinioideae, but data are limited. Generally, a range of rhizobia genera nodulated legume species across the two Mimosoideae tribes Ingeae and Mimoseae, but Mimosa spp. show specificity towards Burkholderia in central and southern Brazil, Rhizobium/Ensifer in central Mexico and Cupriavidus in southern Uruguay. These specific symbioses are likely to be at least in part related to the relative occurrence of the potential symbionts in soils of the different regions. Generally, Papilionoideae species were promiscuous in relation to rhizobial symbionts, but specificity for rhizobial genus appears to hold at the tribe level for the Fabeae (Rhizobium), the genus level for Cytisus (Bradyrhizobium), Lupinus (Bradyrhizobium) and the New Zealand native Sophora spp. (Mesorhizobium) and species level for Cicer arietinum (Mesorhizobium), Listia bainesii (Methylobacterium) and Listia angolensis (Microvirga). -
22. Tribe ERAGROSTIDEAE Ihl/L^Ä Huameicaozu Chen Shouliang (W-"^ G,), Wu Zhenlan (ß^E^^)
POACEAE 457 at base, 5-35 cm tall, pubescent. Basal leaf sheaths tough, whit- Enneapogon schimperianus (A. Richard) Renvoize; Pap- ish, enclosing cleistogamous spikelets, finally becoming fi- pophorum aucheri Jaubert & Spach; P. persicum (Boissier) brous; leaf blades usually involute, filiform, 2-12 cm, 1-3 mm Steudel; P. schimperianum Hochstetter ex A. Richard; P. tur- wide, densely pubescent or the abaxial surface with longer comanicum Trautvetter. white soft hairs, finely acuminate. Panicle gray, dense, spike- Perennial. Culms compactly tufted, wiry, erect or genicu- hke, linear to ovate, 1.5-5 x 0.6-1 cm. Spikelets with 3 fiorets, late, 15^5 cm tall, pubescent especially below nodes. Basal 5.5-7 mm; glumes pubescent, 3-9-veined, lower glume 3-3.5 mm, upper glume 4-5 mm; lowest lemma 1.5-2 mm, densely leaf sheaths tough, lacking cleistogamous spikelets, not becom- villous; awns 2-A mm, subequal, ciliate in lower 2/3 of their ing fibrous; leaf blades usually involute, rarely fiat, often di- length; third lemma 0.5-3 mm, reduced to a small tuft of awns. verging at a wide angle from the culm, 3-17 cm, "i-^ mm wide, Anthers 0.3-0.6 mm. PL and &. Aug-Nov. 2« = 36. pubescent, acuminate. Panicle olive-gray or tinged purplish, contracted to spikelike, narrowly oblong, 4•18 x 1-2 cm. Dry hill slopes; 1000-1900 m. Anhui, Hebei, Liaoning, Nei Mon- Spikelets with 3 or 4 florets, 8-14 mm; glumes puberulous, (5-) gol, Ningxia, Qinghai, Shanxi, Xinjiang, Yunnan [India, Kazakhstan, 7-9-veined, lower glume 5-10 mm, upper glume 7-11 mm; Kyrgyzstan, Mongolia, Pakistan, E Russia; Africa, America, SW Asia]. -
Wetland Weeds: West Indian Marsh Grass (Hymenachne Amplexicaulis)1 Rodrigo Diaz, William A
ENY693 Wetland Weeds: West Indian Marsh Grass (Hymenachne amplexicaulis)1 Rodrigo Diaz, William A. Overholt, Brent Sellers, and James P. Cuda2 Wetlands (including swamps, bogs, marshes, mires and for the fauna that can be found in Florida wetlands. Among lagoons) are important ecosystems that are found on every the important wetland plants are bur-marigold, maiden- continent except Antarctica. Wetlands are recognized as cane, American lotus, pickerelweed, soft rush, alligator valuable sources, sinks, and transformers of a multitude flag, scarlet rosemallow, hurricane-grass, fragrant waterlily, of chemical, biological, and genetic materials (Mitsch and lizards tail, red ludwigia, banana lily, and giant foxtail. Gosselink 1993), and play an increasingly important role in today’s world due to urban and agricultural pollution Invasion of exotic species poses a serious threat to Florida’s and modification of natural landscapes. Wetlands not only sensitive ecosystems. International trade, tourism, and perform hydrologic and chemical services, which clean pol- agricultural and urban disturbance have increased the luted water, protect shorelines, prevent floods and recharge probability of establishment of exotic plants. Exotic plant ground water aquifers, but also support a great variety of species in Florida wetlands spread rapidly due to floods, biodiversity and complex food chains. large interconnected waterway systems, and increased use of commercial and recreational boats. Fertilizer and Florida’s wetlands constitute one of the world’s largest sediment runoff from agricultural lands and waste water aquatic habitats. In a survey conducted in the 1980s, Dahl from beef and dairy operations contribute to successful (1990) reported that Florida had lost 9.3 million acres of establishment of aquatic exotic plants. -
Plant Conservation Alliance®S Alien Plant Working Group Burma Reed Neyraudia Reynaudiana
FACT SHEET: BURMA REED Burma Reed Neyraudia reynaudiana (Kunth) Keng ex A.S. Hitchc. Grass family (Poaceae) NATIVE RANGE Southeast Asia and Indomalaya (Japan, southern China, Viet Nam, Laos, Cambodia, Thailand, Malaya, Myanmar (Burma), Bhutan, Nepal, and eastern India) DESCRIPTION Burma reed, also known as silk reed, cane grass, and false reed, is a tall, perennial, large-plumed grass that grows in clumps in sunny upland areas. Stems, including the flower stalks are from 3 to 15 feet in height, depending on soil and moisture conditions. The leaves are 8 to 10 inches long and hairless, except for a single line of horizontal hairs at the juncture of the upper and lower portions of the leaf. Stems are approximately ½ inch in width, are round, solid, and have nodes (stem-leaf junctures) every 3 to 5 inches along the stem. The flower plumes, which can be up to 3 feet long, are composed of many hundreds of tiny flowers and have a shimmery, silky appearance. Flowering occurs in April and October, each clump producing an average of forty stalks and twelve to twenty flowering plumes. Burma reed resembles several other tall grasses, including common reed (Phragmites communis), giant reed (Arundo donax), pampas grass (Cortaderia selloana) and sugar cane (Saccharum officinarum). ECOLOGICAL THREAT Burma reed damages native ecosystems by crowding and shading out understory plant species and by creating conditions for extremely hot and destructive wildfires. In southern Florida (Miami-Dade County), it is a serious threat to the globally imperiled pine rocklands community whose pine canopy was largely destroyed in 1992 by Hurricane Andrew. -
Exempted Trees List
Prohibited Plants List The following plants should not be planted within the City of North Miami. They do not require a Tree Removal Permit to remove. City of North Miami, 2017 Comprehensive List of Exempted Species Pg. 1/4 Scientific Name Common Name Abrus precatorius Rosary pea Acacia auriculiformis Earleaf acacia Adenanthera pavonina Red beadtree, red sandalwood Aibezzia lebbek woman's tongue Albizia lebbeck Woman's tongue, lebbeck tree, siris tree Antigonon leptopus Coral vine, queen's jewels Araucaria heterophylla Norfolk Island pine Ardisia crenata Scratchthroat, coral ardisia Ardisia elliptica Shoebutton, shoebutton ardisia Bauhinia purpurea orchid tree; Butterfly Tree; Mountain Ebony Bauhinia variegate orchid tree; Mountain Ebony; Buddhist Bauhinia Bischofia javanica bishop wood Brassia actino-phylla schefflera Calophyllum antillanum =C inophyllum Casuarina equisetifolia Australian pine Casuarina spp. Australian pine, sheoak, beefwood Catharanthus roseus Madagascar periwinkle, Rose Periwinkle; Old Maid; Cape Periwinkle Cestrum diurnum Dayflowering jessamine, day blooming jasmine, day jessamine Cinnamomum camphora Camphortree, camphor tree Colubrina asiatica Asian nakedwood, leatherleaf, latherleaf Cupaniopsis anacardioides Carrotwood Dalbergia sissoo Indian rosewood, sissoo Dioscorea alata White yam, winged yam Pg. 2/4 Comprehensive List of Exempted Species Scientific Name Common Name Dioscorea bulbifera Air potato, bitter yam, potato vine Eichhornia crassipes Common water-hyacinth, water-hyacinth Epipremnum pinnatum pothos; Taro -
Sesbania Punicea (Cav.) Benth
A WEED REPORT from the book Weed Control in Natural Areas in the Western United States This WEED REPORT does not constitute a formal recommendation. When using herbicides always read the label, and when in doubt consult your farm advisor or county agent. This WEED REPORT is an excerpt from the book Weed Control in Natural Areas in the Western United States and is available wholesale through the UC Weed Research & Information Center (wric.ucdavis.edu) or retail through the Western Society of Weed Science (wsweedscience.org) or the California Invasive Species Council (cal-ipc.org). Sesbania punicea (Cav.) Benth. Red sesbania Family: Fabaceae Range: Not widespread in the western United States. Occurs throughout the southeast from Virginia to eastern Texas and a few localities in California. Habitat: Riparian corridors, coastal plains and disturbed sites such as roadsides, ditches, canals and areas adjacent to ornamental plantings. In regions with long, dry summers, red sesbania invades moist areas. Survives occasional freezes but not harsh winters. It is most likely to spread to wildlands adjacent to or downstream from ornamental plantings. Origin: Native to South America (Argentina, Brazil, Paraguay, and Uruguay). Introduced to the United States as an ornamental. Impacts: Red sesbania grows rapidly and forms dense stands so thick that access to riparian areas becomes difficult to impossible. It displaces native vegetation used by wildlife and contributes to bank erosion and flooding. Large infestations can decrease water flow and reduce recreational uses. Sesbania can fix nitrogen, which enables the plant to colonize and dominate areas with poor soil. Increased soil nitrogen fertility gives a competitive advantage to other non-native weeds that thrive on high nitrogen levels. -
Evaluation of Fluazifop-P-Butyl and Sethoxydim for Hymenachne Amplexicaulis Control in Mixed and Monotypic Emergent Plant Communities
J. Aquat. Plant Manage. 58: 105–111 Evaluation of fluazifop-P-butyl and sethoxydim for Hymenachne amplexicaulis control in mixed and monotypic emergent plant communities KAITLYN QUINCY AND STEPHEN F. ENLOE* ABSTRACT and West Indian marsh grass [Hymenachne amplexicaulis (Rudge) Nees] have been shown to displace native plant West Indian marsh grass, Hymenachne amplexicaulis,isan species and form dense, monotypic stands (Tarver 1979, invasive grass species that forms monotypic stands in Lambert et al. 2010, Enloe et al. 2018). Proliferation of Florida’s freshwater marshes. It is typically managed using invasive grasses can have negative effects on the greater broad-spectrum herbicides that can have significant non- wetland community by promoting secondary invasions and target impacts. Grass-specific herbicides (graminicides), altering ecosystem processes including nutrient cycling, sethoxydim and fluazifop-P-butyl, represent an opportunity biomass accumulation, and water flow (Dudley 1998, to control H. amplexicaulis and reduce nontarget impacts. Meyerson et al. 2000, Houston and Duivenvoorden 2002, Plots were established in a monotypic H. amplexicaulis stand Flory and Clay 2010, Flory and Bauer 2014). West Indian in November 2017 by applying fluazifop-P-butyl at 0.42 or À1 À1 marsh grass (WIMG) is a relatively new threat and is 1.12 kg ha or sethoxydim at 5.04 kg ha , each with MSO at becoming particularly problematic in the hydrologically 1% v/v. Both graminicides significantly reduced H. amplex- fluctuating wetlands in the Kissimmee River and Kissimmee icaulis cover by 85% to 90% at 6 mo after initial treatment Chain of Lakes in Central Florida. (MAT1), but by 9 MAT1, this control fell to 52 to 68% when WIMG is one of the 81 highly invasive Category I species compared to nontreated plots. -
Sesbania Punicea (Brazilian Rattlebox) Management Information
Sesbania punicea (Brazilian rattlebox) Management Information Prepared by the IUCN SSC Invasive Species Specialist Group Contents 1.0 Introduction...................................................................................................Page 1 2.0 Preventative Measures..................................................................................Page 1 3.0 Physical Control............................................................................................Page 2 4.0 Chemical Control...........................................................................................Page 2 5.0 Physical / Chemical Follow Up Techniques ................................................Page 3 6.0 Biological Control...........................................................................................Page 3 7.0 References.......................................................................................................Page 4 8.0 Appendix...........................................................................................................Page 6 1.0 Introduction Commonly known as Brazilian rattlebox, Sesbania punicea is a deciduous, leguminous shrub that grows up to 4m tall (Hoffmann & Moran, 1998). It has been widely distributed from its native range in South America as an attractive ornamental species (Hoffmann & Moran, 1991a; Csurhes & Edwards, 1998). Escapes from cultivation have led to naturalisation in some areas as in southern United States and South Africa; where it has formed dense thickets in riparian and wetland