Quarantine Testing of an Insect for Biocontrol of Tibouchina Herbacea
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Mysore Raspberry Rubus Niveus Thimbleberry Rubus Rosifolius
Big Island Invasive Species Committee (BIISC) Hawaii‘i Island Weed ID Card – DRAFT– v20030508 • Local/Common Name: None • Scientific Name: Rubus glaucus • Family : Rosaceae (Rose Family) • Origin and Status: – Invasive weed in Hawai‘i – Native to ? – First introduced to into Hawai‘i in ? • Description: Rubus glaucus is a raspberry plant with long thorny vines. Its leaves are compound, consisting of 3 oblong-shaped leaflets that have a pointy tip. The stems are white, almost as if coated with flour, and have sparse long thorns. The flowers are white, with 5 tiny petals, and tending to occur in clusters along the stems. Its fruits are red when ripe and are about 1” long. • Distribution: R. glaucus is currently found in the Volcano area along disturbed roadsides and abandoned fields. • Other Information: R. glaucus is a rambling vine. This means, like other vines, that it tends to grow up and over other plants. It ends up smothering whatever is growing beneath it. It can also grow out and along the ground instead of erect. Birds have been witnessed eating the berries from this plant. • Contact: Rubus glaucus Prepared by MLC/KFB Big Island Invasive Species Committee (BIISC) Local/Common Name: Hill or Mysore Raspberry Hawaii‘i Island Weed ID Card – DRAFT– v20030508 Scientific Name: Rubus niveus Family : Rosaceae (Rose Family) Origin and Status: ?Invasive weed in Hawai‘i ?Native from India, southeastern Asia, the Philippines, and Indonesia ?First introduced to into Hawai‘i in 1965 Description: Rubus niveus is a stout shrub that grows up to 6 ½ ft. tall . The compound leaves have 5 to 9 leaflets that are oval- shaped with pointed tips and thorns located on the underside. -
Cocoa Beach Maritime Hammock Preserve Management Plan
MANAGEMENT PLAN Cocoa Beach’s Maritime Hammock Preserve City of Cocoa Beach, Florida Florida Communities Trust Project No. 03 – 035 –FF3 Adopted March 18, 2004 TABLE OF CONTENTS SECTION PAGE I. Introduction ……………………………………………………………. 1 II. Purpose …………………………………………………………….……. 2 a. Future Uses ………….………………………………….…….…… 2 b. Management Objectives ………………………………………….... 2 c. Major Comprehensive Plan Directives ………………………..….... 2 III. Site Development and Improvement ………………………………… 3 a. Existing Physical Improvements ……….…………………………. 3 b. Proposed Physical Improvements…………………………………… 3 c. Wetland Buffer ………...………….………………………………… 4 d. Acknowledgment Sign …………………………………..………… 4 e. Parking ………………………….………………………………… 5 f. Stormwater Facilities …………….………………………………… 5 g. Hazard Mitigation ………………………………………………… 5 h. Permits ………………………….………………………………… 5 i. Easements, Concessions, and Leases …………………………..… 5 IV. Natural Resources ……………………………………………..……… 6 a. Natural Communities ………………………..……………………. 6 b. Listed Animal Species ………………………….…………….……. 7 c. Listed Plant Species …………………………..…………………... 8 d. Inventory of the Natural Communities ………………..………….... 10 e. Water Quality …………..………………………….…..…………... 10 f. Unique Geological Features ………………………………………. 10 g. Trail Network ………………………………….…..………..……... 10 h. Greenways ………………………………….…..……………..……. 11 i Adopted March 18, 2004 V. Resources Enhancement …………………………..…………………… 11 a. Upland Restoration ………………………..………………………. 11 b. Wetland Restoration ………………………….…………….………. 13 c. Invasive Exotic Plants …………………………..…………………... 13 d. Feral -
Low-Maintenance Landscape Plants for South Florida1
ENH854 Low-Maintenance Landscape Plants for South Florida1 Jody Haynes, John McLaughlin, Laura Vasquez, Adrian Hunsberger2 Introduction regular watering, pruning, or spraying—to remain healthy and to maintain an acceptable aesthetic This publication was developed in response to quality. A low-maintenance plant has low fertilizer requests from participants in the Florida Yards & requirements and few pest and disease problems. In Neighborhoods (FYN) program in Miami-Dade addition, low-maintenance plants suitable for south County for a list of recommended landscape plants Florida must also be adapted to—or at least suitable for south Florida. The resulting list includes tolerate—our poor, alkaline, sand- or limestone-based over 350 low-maintenance plants. The following soils. information is included for each species: common name, scientific name, maximum size, growth rate An additional criterion for the plants on this list (vines only), light preference, salt tolerance, and was that they are not listed as being invasive by the other useful characteristics. Florida Exotic Pest Plant Council (FLEPPC, 2001), or restricted by any federal, state, or local laws Criteria (Burks, 2000). Miami-Dade County does have restrictions for planting certain species within 500 This section will describe the criteria by which feet of native habitats they are known to invade plants were selected. It is important to note, first, that (Miami-Dade County, 2001); caution statements are even the most drought-tolerant plants require provided for these species. watering during the establishment period. Although this period varies among species and site conditions, Both native and non-native species are included some general rules for container-grown plants have herein, with native plants denoted by †. -
Native Trees and Plants for Birds and People in the Caribbean Planting for Birds in the Caribbean
Native Trees and Plants for Birds and People in the Caribbean Planting for Birds in the Caribbean If you’re a bird lover yearning for a brighter, busier backyard, native plants are your best bet. The Caribbean’s native trees, shrubs and flowers are great for birds and other wildlife, and they’re also a part of the region’s unique natural heritage. There’s no better way to celebrate the beauty, culture and birds of the Caribbean than helping some native plants get their roots down. The Habitat Around You Habitat restoration sounds like something that is done by governments in national parks, but in reality it can take many forms. Native plants can turn backyards and neighborhood parks into natural habitats that attract and sustain birds and other wildlife. In the Caribbean, land is precious—particularly the coastal areas where so many of us live. Restoring native habitat within our neighborhoods allows us to share the land with native plants and animals. Of course, it doesn’t just benefit the birds. Native landscaping makes neighborhoods more beautiful and keeps us in touch with Caribbean traditions. Why Native Plants? Many plants can help birds and beautify neighborhoods, but native plants really stand out. Our native plants and animals have developed over millions of years to live in harmony: pigeons eat fruits and then disperse seeds, hummingbirds pollinate flowers while sipping nectar. While many plants can benefit birds, native plants almost always do so best due to the partnerships they have developed over the ages. In addition to helping birds, native plants are themselves worthy of celebration. -
Native Landscape Plants for South Florida1
Archival copy: for current recommendations see http://edis.ifas.ufl.edu or your local extension office. ENH 875 Native Landscape Plants for South Florida1 John McLaughlin, Laura Vasquez, and Jody Haynes, 2 Introduction maintenance (i.e., regular watering, pruning, or use of pesticides) to remain healthy and maintain an Native plants were once thought of by many acceptable aesthetic quality. It is also important to Florida gardeners, nurserymen, and landscapers as note here that not all native plants have the same being appropriate only for informal gardens or in requirements, and any plant put in the wrong place highly specific and often difficult garden situations, may either present problems or require more such as boggy or coastal areas (Osorio, 2001). maintenance. In addition, all landscape trees Because of this negative (mis)perception, Florida including Florida natives require, to varying degrees, native plants have in the past received a cool appropriate routine pruning in order to encourage reception. In recent years, however, the positive structurally sound growth. Any comments below features of native plants have been increasingly regarding resistance to windstorms assume that an recognized and appreciated - especially in central and appropriate pruning program is in place. north Florida. A previous publication, ENH854 The Florida Yards & Neighborhoods (FYN) (http://edis.ifas.ufl.edu/EP107), listed over 350 program has been encouraging the use of native and non-native low-maintenance plant species Florida-Friendly Landscaping principles in south for south Florida landscapes. The present publication Florida since February 2000. The FYN program does was developed as a supplement to ENH854, but also not restrict its recommendations to native plants, but serves as a good stand-alone reference: both for those rather recommends putting the right plant in the right already committed to adding native plants to their place. -
Woody and Herbaceous Plants Native to Haiti for Use in Miami-Dade Landscapes1
Woody and Herbaceous Plants Native to Haiti For use in Miami-Dade Landscapes1 Haiti occupies the western one third of the island of Hispaniola with the Dominican Republic the remainder. Of all the islands within the Caribbean basin Hispaniola possesses the most varied flora after that of Cuba. The plants contained in this review have been recorded as native to Haiti, though some may now have been extirpated due in large part to severe deforestation. Less than 1.5% of the country’s original tree-cover remains. Haiti’s future is critically tied to re- forestation; loss of tree cover has been so profound that exotic fast growing trees, rather than native species, are being used to halt soil erosion and lessen the risk of mudslides. For more information concerning Haiti’s ecological plight consult references at the end of this document. For present purposes all of the trees listed below are native to Haiti, which is why non-natives such as mango (the most widely planted tree) and other important trees such as citrus, kassod tree (Senna siamea) and lead tree (Leucanea leucocephala) are not included. The latter two trees are among the fast growing species used for re-forestation. The Smithsonian National Museum of Natural History’s Flora of the West Indies was an invaluable tool in assessing the range of plants native to Haiti. Not surprisingly many of the listed trees and shrubs 1 John McLaughlin Ph.D. U.F./Miami-Dade County Extension Office, Homestead, FL 33030 Page | 1 are found in other parts of the Caribbean with some also native to South Florida. -
Plant List: M.E. Depalma Park Picture Botanical Name Common Name Picture Botanical Name Common Name Salvia Coccinea Tropical
Plant List: M.E. DePalma Park Picture Botanical Name Picture Botanical Name Common Name Common Name Salvia coccinea Muhlenbergia capillaris Tropical Sage (red) pink Florida Muhly Grass Blooms: Year-round Blooms: Mid Summer - Fall Attracts Butterflies, Hummingbirds and Painted Buntings Florida Native Florida Native Psychotria nervosa Arachis glabrata Wild Coffee Perennial peanut Blooms: Spring-Summer Fruits: Fall Blooms: Year-round Berries are a food source for birds Native to Argentina, Brazil and Paraguay Male Butterflies need the alkaloids found in this plant, in order to mature sexually. Florida Native Callicarpa americana Gaillardia pulchella Beautyberry Blanket Flower Blooms: late Summer Fruits: Fall Blooms: Year-round Berries are a food source for birds Butterfly nectar plant Florida Native Florida Native Chrysobalanus icaco Stachytarpheta jamaicensis Cocoplum Blue Porterweed Blooms: Spring-Summer Fruits: Fall Blooms: Year-round Berries are a food source for birds Butterfly nectar plant Florida Native Florida Native Asclepias curassavica Pentas lanceolata Mexican Butterfly Weed, Blood-flower or Scarlet Milkweed Egyptian starflower Blooms: Year-round Blooms: Year-round Butterfly nectar plant for Butterflies especially Queens and These may be red, white, lavender, purple, or shades Monarchs of pink. Some are two-toned. All are extremely Monarch larval plant attractive to butterflies, and the red and dark pink varieties delight hummingbirds. Butterfly nectar plant Mimosa strigillosa Loropetalum Sensitive Plant Chinese Fringe Flower Blooms: Year-round Butterfly nectar plant Butterfly nectar plant Native to Japan and southeastern Asia including Florida Native groundcover southern China. Coreopsis_leavenworthii Coreopsis lanceolata Tickseed Lance leafed coreopsis Blooms: Year-round Butterfly nectar plant Butterfly nectar plant Florida Native Florida Native Lantana involucrata. -
UFFLORIDA IFAS Extension
ENH854 UFFLORIDA IFAS Extension Low-Maintenance Landscape Plants for South Florida1 Jody Haynes, John McLaughlin, Laura Vasquez, Adrian Hunsberger2 Introduction The term "low-maintenance" refers to a plant that does not require frequent maintenance-such as This publication was developed in response to regular watering, pruning, or spraying-to remain requests from participants in the Florida Yards & healthy and to maintain an acceptable aesthetic Neighborhoods (FYN) program in Miami-Dade quality. A low-maintenance plant has low fertilizer County for a list of recommended landscape plants requirements and few pest and disease problems. In suitable for south Florida. The resulting list includes addition, low-maintenance plants suitable for south over 350 low-maintenance plants. The following Florida must also be adapted to--or at least information is included for each species: common tolerate-our poor, alkaline, sand- or limestone-based name, scientific name, maximum size, growth rate soils. (vines only), light preference, salt tolerance, and other useful characteristics. An additional criterion for the plants on this list was that they are not listed as being invasive by the Criteria Florida Exotic Pest Plant Council (FLEPPC, 2001), or restricted by any federal, state, or local laws This section will describe the criteria by which (Burks, 2000). Miami-Dade County does have plants were selected. It is important to note, first, that restrictions for planting certain species within 500 even the most drought-tolerant plants require feet of native habitats they are known to invade watering during the establishment period. Although (Miami-Dade County, 2001); caution statements are this period varies among species and site conditions, provided for these species. -
Biological Control Potential of Miconia Calvescens Using Three Fungal Pathogens
BIOLOGICAL CONTROL POTENTIAL OF MICONIA CALVESCENS USING THREE FUNGAL PATHOGENS Eloise M. Killgore Biological Control Section, Hawai'i Department of Agriculture, P. 0. Box 22159, Honolulu, Hawai'i 96823-2159, U.S.A. Emai I: eloiseki/[email protected] Abstract. Biological control of miconia (Miconia calvescens) became a management option as soon as the severity of its threat to Hawaiian ecosystems was recognized. No weed in Hawai'i has received as much publicity, attention, and funding for control. Three fungal pathogens have been considered as potential agents. Co/letotrichum gloesoporioides f. sp. miconiae was assessed within six months, the petition for release approved within eight months and the fungus released on the islands of Hawai'i and Maui in 1997. It is established on Hawai'i and has spread to other areas. Its effectiveness is under evaluatlon. Pseudocercospora tamonae causes extensive damage to leaves, attacks other melastomes and the seedlings of some Myrtaceae but only fruits on miconia. It is very uncertain whether this species will be approved for release. Coccodiella myconae produces large wart-like growths that deform leaves considerably. It appears to be an obligate parasite of miconia but hyperparasitized by another species tentatively identified as Sagenomella alba. It has proven difficult to transfer from one plant to another where it does not sporulate. Further work on this species is in progress. Key words: Biological control of weeds, Coccodiella myconae, Colletotrichum gloeosporioides f. sp. miconiae, invasive species, Melastomataceae, Miconia celvescens, Pseudocercospora tamonae, Sagenomella alba. THE TARGET WEED, MICONIA CALVESCENS Early Considerations Davis (1978) first expressed concern about the threat of Miconia calvescens DC (Myrtales, Melastomataceae) in Hawai'i. -
Euselasia Chrysippe As a Potential Biocontrol for Miconia Calvescens in Hawaiʻi Kenneth P
Euselasia chrysippe as a potential biocontrol for Miconia calvescens in Hawaiʻi Kenneth P. Puliafico,1* Jeselyn Calderón-Ayala,1,2 Nancy L. Chaney,1 Edward Bufil,1 M. Tracy Johnson1 1 Institute of Pacific Islands Forestry, PSW Research Station, USDA Forest Service, Volcano, Hawaii * [email protected] 2 KUPU-Hawaii: Hawaii Youth Conservation Corps / Americorps Programs Biology and Rearing Miconia Biocontrol Euselasia chrysippe (Lepidoptera: Riodinidae) is a small butterfly whose caterpillars Biological control is considered a feed on several Miconia species in its native Costa Rica. Larvae hatch from large egg critical tool for long term management masses (up to 115 eggs) (A), feed (B,C) and molt (D) in unison, moving between feeding of Miconia calvescens, a neotropical sites in single-file processions (E). This gregarious behavior is thought to improve feeding tree that is a major threat to Hawaiian on tough leaves, optimize foraging, and deter enemies. After 6 instars, larvae move off the forest ecosystems. Explorations in plant to pupate in smaller groups. Development from egg to adult is completed in about 2 Costa Rica and Brazil yielded several months, and adult females emerge one day prior to males from the same cohort (F). promising natural enemies which are Butterflies live up to 2 months along forest edges and gaps where Miconia calvescens A B being evaluated now for host occurs. C specificity. Our strategy is to develop Euselasia eggs from Costa Rica were hatched and larvae reared on Miconia plants in the a suite of biocontrol agents attacking G Hawai’i Volcanoes National Park Quarantine facility. -
FY2015 HISC Miconia Report 20160801
Final Report on FY2015 HISC Project: Technical support of miconia biocontrol research in Volcano, Hawaii Tracy Johnson, Kenneth Puliafico, USDA Forest Service The development of biocontrol of Miconia was progressed with the completion of host specificity testing of Euselasia chrysippe, leaf-eating gregarious caterpillars from Costa Rica. Results of feeding tests with 73 different plant species were consistent with field observations in the native range: these caterpillars fed on several species within the plant family Melastomataceae but did not feed on other plants within the Order Myrtales or beyond (see attached poster). No feeding damage was observed on any native Hawaiian plants in these highly conservative no-choice host specificity tests. Based on these results we are preparing publications and the petition for release of this promising agent. Larval feeding by Euselasia is expected to reduce miconia’s growth rate and spread in Hawaiian ecosystems. In addition to feeding tests on a wide range of plants, long term larval survival of Euselasia was examined on eight melastomes. Caterpillars were found to complete development only on miconia and its closest relatives (within the tribe Miconieae). Larvae did not survive well on Clidemia hirta, however, which is a close relative of miconia but has leaves protected by dense trichomes. These results indicate that the actual host range of E. chrysippe would be restricted to M. calvescens and Tetrazygia bicolor in Hawaii. Our Pacific partners are concerned about the safety of this potential agent since they have native Melastoma species, but the long term no-choice tests indicate that representatives of this genus were not acceptable to the caterpillars. -
Implementing Early Detection in Hawai”I, Year One
Implementing Early Detection in Hawai”i, Year One Final Report prepared for: Hawaii Invasive Species Council Research and Technology Program Department of Land and Natural Resources, Division of Forestry and Wildlife Prepared by: Clyde T. Imada, Danielle Frohlich, Alex Lau, and Ryan Smith December 2007 Hawaii Biological Survey Report 2007-016 Implementing Early Detection in Hawai”i, Year One TABLE OF CONTENTS Table of Contents ........................................................................................................................................... i Executive Summary ....................................................................................................................................... 1 I. Introduction ................................................................................................................................................ 2 II. Detection Plan Model ............................................................................................................................... 4 IIa. Building a Target Species List .................................................................................................. 4 IIb. High-risk Sites and Survey Methodology ................................................................................. 6 IIc. Prioritizing for Control ............................................................................................................. 8 IId. Targeted Roadside Surveys ...................................................................................................