The Effects of Introduced Tilapias on Native Biodiversity
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First Report of the Non-Native Midas Cichlid, Amphilophus Citrinellus (Gunther, 1864), in Laguna De Bay, Philippines
First Report of the Non-native Midas Cichlid, Amphilophus citrinellus (Gunther, 1864), in Laguna de Bay, Philippines Item Type article Authors Poniente, Jennifer A.; Dela Peña, John T.; Pol, Romualdo M.; Zapanta, Levita H.; Santos, Mudjekeewis D. DOI 10.31398/tpjf/26.2.2019A0007 Download date 04/10/2021 12:53:05 Link to Item http://hdl.handle.net/1834/41171 The Philippine Journal of Fisheries 26(2): 55-60 July - December 2019 DOI: 10.31398/tpjf/26.2.2019A0007 SHORT COMMUNICATION First report of the Non-native Midas Cichlid, Amphilophus citrinellus (Gunther, 1864), in Laguna de Bay, Philippines Jennifer A. Poniente1, John T. Dela Peña1, Romualdo M. Pol2, Levita H. Zapanta2+ and Mudjekeewis D. Santos1* 1Genetic Fingerprinting Laboratory, National Fisheries Research and Development Institute, Quezon City, Philippines 2National Inland Fisheries Technology Center, Bureau of Fisheries and Aquatic Resources, Tanay, Rizal, Philippines ABSTRACT In recent years, increasing global trade, travel, and transport had rapidly increased the rate of introduction and diversity of non-native fish species. Once established, some introduced fish species can become aggressive and dangerously invasive. Here, we provide the first report of the occurrence of a non-native Midas cichlid Amphilophus citrinellus in Laguna de Bay using morphological analysis and genetic marker, specifically the mitochondrial gene cytochrome c oxidase subunit 1 (CO1). The results provide important information on the presence of another invasive species in Laguna de Bay that needs to be addressed since this species can competitively exclude, predate, and displace native species. E-mail address: [email protected]* Keywords: Amphilophus citrinellus, non-native fish, Received: October 3, 2019 Laguna de Bay, invasive species, cichlid Accepted: December 17, 2019 on-native species may cause changes in the (1976) reported that the natural food supply of the ecosystems to which they are introduced lake could sustain the rearing of milkfish in the lake. -
Field Guide to the Nonindigenous Marine Fishes of Florida
Field Guide to the Nonindigenous Marine Fishes of Florida Schofield, P. J., J. A. Morris, Jr. and L. Akins Mention of trade names or commercial products does not constitute endorsement or recommendation for their use by the United States goverment. Pamela J. Schofield, Ph.D. U.S. Geological Survey Florida Integrated Science Center 7920 NW 71st Street Gainesville, FL 32653 [email protected] James A. Morris, Jr., Ph.D. National Oceanic and Atmospheric Administration National Ocean Service National Centers for Coastal Ocean Science Center for Coastal Fisheries and Habitat Research 101 Pivers Island Road Beaufort, NC 28516 [email protected] Lad Akins Reef Environmental Education Foundation (REEF) 98300 Overseas Highway Key Largo, FL 33037 [email protected] Suggested Citation: Schofield, P. J., J. A. Morris, Jr. and L. Akins. 2009. Field Guide to Nonindigenous Marine Fishes of Florida. NOAA Technical Memorandum NOS NCCOS 92. Field Guide to Nonindigenous Marine Fishes of Florida Pamela J. Schofield, Ph.D. James A. Morris, Jr., Ph.D. Lad Akins NOAA, National Ocean Service National Centers for Coastal Ocean Science NOAA Technical Memorandum NOS NCCOS 92. September 2009 United States Department of National Oceanic and National Ocean Service Commerce Atmospheric Administration Gary F. Locke Jane Lubchenco John H. Dunnigan Secretary Administrator Assistant Administrator Table of Contents Introduction ................................................................................................ i Methods .....................................................................................................ii -
MANAGEMENT and VALUE CHAIN of NILE TILAPIA CULTURED in PONDS of SMALL-SCALE FARMERS in MOROGORO REGION, TANZANIA Sebastian W. Ch
MANAGEMENT AND VALUE CHAIN OF NILE TILAPIA CULTURED IN PONDS OF SMALL-SCALE FARMERS IN MOROGORO REGION, TANZANIA Sebastian W. Chenyambuga , Nazael A. Madalla and Berno V. Mnembuka Department of Animal Science, Sokoine University of Agriculture, P.O. Box 3004, Morogoro, Tanzania. Abstract A study was carried out to assess production performance and value chain of Nile tilapia grown in ponds of small-scale farmers in Morogoro region, Tanzania. Information was collected through individual interviews of 30 fish farmers. The main reasons for culturing fish were provision of animal protein food for home consumption (66.7%) and generation of income (23.3%). Fish farming contributed 10.6% of household annual income and was ranked second to crop production (50%). The majority of the farmers were fertilizing their ponds with chicken manure (30.0%) and cattle manure (23.3%). Most farmers (73.3%) cultured pure stand of Nile tilapia and only few (26.7%) practiced polyculture of Nile tilapia and African catfish. All farmers depended on natural food as a source of feed for their fish. Moreover, the farmers were feeding maize bran (96.7%), vegetables (66.7%), and kitchen leftovers (13.3%) as supplementary feeds. Men were responsible for purchasing and stocking fingerlings (60.0%), feeding (40.0%), pond maintenance (53.3%), harvesting (60.0%) and selling (43.3%). Women were mainly involved in fish processing (76.7%). The average period from stocking to harvesting was 5.75 ± 0.18 months for Nile tilapia and the mean yield was 6,946.2 kg/ha per year. About 22.2% of the harvested fish were consumed at home and the remaining (77.8%) were sold. -
Disease List for Aquaculture Health Certificate
Quarantine Standard for Designated Species of Imported/Exported Aquatic Animals [Attached Table] 4. Listed Diseases & Quarantine Standard for Designated Species Listed disease designated species standard Common name Disease Pathogen 1. Epizootic haematopoietic Epizootic Perca fluviatilis Redfin perch necrosis(EHN) haematopoietic Oncorhynchus mykiss Rainbow trout necrosis virus(EHNV) Macquaria australasica Macquarie perch Bidyanus bidyanus Silver perch Gambusia affinis Mosquito fish Galaxias olidus Mountain galaxias Negative Maccullochella peelii Murray cod Salmo salar Atlantic salmon Ameirus melas Black bullhead Esox lucius Pike 2. Spring viraemia of Spring viraemia of Cyprinus carpio Common carp carp, (SVC) carp virus(SVCV) Grass carp, Ctenopharyngodon idella white amur Hypophthalmichthys molitrix Silver carp Hypophthalmichthys nobilis Bighead carp Carassius carassius Crucian carp Carassius auratus Goldfish Tinca tinca Tench Sheatfish, Silurus glanis European catfish, wels Negative Leuciscus idus Orfe Rutilus rutilus Roach Danio rerio Zebrafish Esox lucius Northern pike Poecilia reticulata Guppy Lepomis gibbosus Pumpkinseed Oncorhynchus mykiss Rainbow trout Abramis brama Freshwater bream Notemigonus cysoleucas Golden shiner 3.Viral haemorrhagic Viral haemorrhagic Oncorhynchus spp. Pacific salmon septicaemia(VHS) septicaemia Oncorhynchus mykiss Rainbow trout virus(VHSV) Gadus macrocephalus Pacific cod Aulorhynchus flavidus Tubesnout Cymatogaster aggregata Shiner perch Ammodytes hexapterus Pacific sandlance Merluccius productus Pacific -
A Practical Handbook for Determining the Ages of Gulf of Mexico And
A Practical Handbook for Determining the Ages of Gulf of Mexico and Atlantic Coast Fishes THIRD EDITION GSMFC No. 300 NOVEMBER 2020 i Gulf States Marine Fisheries Commission Commissioners and Proxies ALABAMA Senator R.L. “Bret” Allain, II Chris Blankenship, Commissioner State Senator District 21 Alabama Department of Conservation Franklin, Louisiana and Natural Resources John Roussel Montgomery, Alabama Zachary, Louisiana Representative Chris Pringle Mobile, Alabama MISSISSIPPI Chris Nelson Joe Spraggins, Executive Director Bon Secour Fisheries, Inc. Mississippi Department of Marine Bon Secour, Alabama Resources Biloxi, Mississippi FLORIDA Read Hendon Eric Sutton, Executive Director USM/Gulf Coast Research Laboratory Florida Fish and Wildlife Ocean Springs, Mississippi Conservation Commission Tallahassee, Florida TEXAS Representative Jay Trumbull Carter Smith, Executive Director Tallahassee, Florida Texas Parks and Wildlife Department Austin, Texas LOUISIANA Doug Boyd Jack Montoucet, Secretary Boerne, Texas Louisiana Department of Wildlife and Fisheries Baton Rouge, Louisiana GSMFC Staff ASMFC Staff Mr. David M. Donaldson Mr. Bob Beal Executive Director Executive Director Mr. Steven J. VanderKooy Mr. Jeffrey Kipp IJF Program Coordinator Stock Assessment Scientist Ms. Debora McIntyre Dr. Kristen Anstead IJF Staff Assistant Fisheries Scientist ii A Practical Handbook for Determining the Ages of Gulf of Mexico and Atlantic Coast Fishes Third Edition Edited by Steve VanderKooy Jessica Carroll Scott Elzey Jessica Gilmore Jeffrey Kipp Gulf States Marine Fisheries Commission 2404 Government St Ocean Springs, MS 39564 and Atlantic States Marine Fisheries Commission 1050 N. Highland Street Suite 200 A-N Arlington, VA 22201 Publication Number 300 November 2020 A publication of the Gulf States Marine Fisheries Commission pursuant to National Oceanic and Atmospheric Administration Award Number NA15NMF4070076 and NA15NMF4720399. -
Oreochromis Rukwaensis) Ecological Risk Screening Summary
Lake Rukwa Tilapia (Oreochromis rukwaensis) Ecological Risk Screening Summary U.S. Fish & Wildlife Service, March 2012 Revised, July 2018 Web Version, 6/4/2020 Organism Type: Fish Overall Risk Assessment Category: Uncertain 1 Native Range and Status in the United States Native Range From Froese and Pauly (2018): “Africa: Lake Rukwa in Tanzania.” From Shechonge et al. (2019): “Oreochromis rukwaensis (Hilgendorf & Pappenheim 1903) previously known only from Lake Rukwa was present in an upstream section of the Ruaha river system, where a major exploited population was recorded at the Mtera Dam Lake [Tanzania].” Status in the United States No records of Oreochromis rukwaensis occurrences in the United States were found. No information on trade of O. rukwaensis in the United States was found. 1 The Florida Fish and Wildlife Conservation Commission has listed the tilapia, Oreochromis rukwaensis as a prohibited species. Prohibited nonnative species (FFWCC 2020), "are considered to be dangerous to the ecology and/or the health and welfare of the people of Florida. These species are not allowed to be personally possessed or used for commercial activities." Means of Introductions in the United States No records of Oreochromis rukwaensis occurrences in the United States were found. Remarks No additional remarks. 2 Biology and Ecology Taxonomic Hierarchy and Taxonomic Standing According to Eschmeyer et al. (2018), Oreochromis rukwaensis (Hilgendorf and Pappenheim 1903) is the current valid name of this species. From ITIS (2018): Kingdom Animalia -
Gene Flow in the Environment – Genetic Pollution? G.R
Gene flow in the environment Gene flow in the environment – genetic pollution? G.R. Squire, N. Augustin, J. Bown1, J.W. Crawford, G. Dunlop, J. Graham, J.R. Hillman, B. Marshall, D. Marshall, G. Ramsay, D.J. Robinson, J. Russell, C. Thompson & G. Wright iological invasions have had profound effects on affect plants and animals, injure us? Will crops in gen- Bhuman society from the earliest times. The spread eral, and GM ones in particular, reduce even more the of the black death in the Middle Ages, the devasta- biological diversity of arable farmland? Will they con- tions of potato blight, the effects on indigenous taminate other crops, cause more pesticide to be used, species by grey squirrels, dutch elm disease and flat- rather than less as some companies claim? worms have all been seen as detrimental to man or the environment. Others are seen as bringing benefits: An increasing number of people have a stake in the most of our crops evolved elsewhere in the world and debate - pressure groups, farmers, farm advisers, con- many culinary and medicinal herbs were brought to sumers, agrochemical companies and government. Britain by the Romans. Perhaps the greatest invasion Opinions are too often polarised. In this confronta- is the import of vast numbers of exotic plants to gar- tional atmosphere, the need is for clear, independent dens and greenhouses. Ecological invasions are an fact, answers and comment. A part of the debate is intrinsic part of ecology and evolution and we only ethical, but independent research is essential on ques- consider them bad if they impoverish our health, tions that science can legitimately address. -
What Characteristics Do All Invasive Species Share That Make Them So
Invasive Plants Facts and Figures Definition Invasive Plant: Plants that have, or are likely to spread into native or minimally managed plant systems and cause economic or environmental harm by developing self-sustaining populations and becoming dominant or disruptive to those systems. Where do most invasive species come from? How do they get here and get started? Most originate long distances from the point of introduction Horticulture is responsible for the introduction of approximately 60% of invasive species. Conservation uses are responsible for the introduction of approximately 30% of invasive species. Accidental introductions account for about 10%. Of all non-native species introduced only about 15% ever escape cultivation, and of this 15% only about 1% ever become a problem in the wild. The process that leads to a plant becoming an invasive species, Cultivation – Escape – Naturalization – Invasion, may take over 100 years to complete. What characteristics make invasive species so successful in our environment? Lack predators, pathogens, and diseases to keep population numbers in check Produce copious amounts of seed with a high viability of that seed Use successful dispersal mechanisms – attractive to wildlife Thrive on disturbance, very opportunistic Fast-growing Habitat generalists. They do not have specific or narrow growth requirements. Some demonstrate alleleopathy – produce chemicals that inhibit the growth of other plants nearby. Have longer photosynthetic periods – first to leaf out in the spring and last to drop leaves in autumn Alter soil and habitat conditions where they grow to better suit their own survival and expansion. Why do we care? What is the big deal? Ecological Impacts Impacting/altering natural communities at a startling rate. -
Latitudinal Shifts of Introduced Species: Possible Causes and Implications
Biol Invasions (2012) 14:547–556 DOI 10.1007/s10530-011-0094-8 ORIGINAL PAPER Latitudinal shifts of introduced species: possible causes and implications Qinfeng Guo • Dov F. Sax • Hong Qian • Regan Early Received: 26 January 2011 / Accepted: 22 August 2011 / Published online: 4 September 2011 Ó Springer Science+Business Media B.V. (outside the USA) 2011 Abstract This study aims to document shifts in the those in their native ranges. Only a small fraction of latitudinal distributions of non-native species relative species examined (i.e.\20% of animals and\10% of to their own native distributions and to discuss plants) have expanded their distributions in their possible causes and implications of these shifts. We exotic range beyond both high- and low-limits of used published and newly compiled data on inter- their native latitudes. Birds, mammals and plants continentally introduced birds, mammals and plants. tended to shift their exotic ranges in similar ways. In We found strong correlations between the latitudinal addition, most non-native species (65–85% in differ- distributions occupied by species in their native and ent groups) have not reached the distributional extent exotic ranges. However, relatively more non-native observed in their native ranges. The possible drivers species occur at latitudes higher than those in their of latitudinal shifts in the exotic range may include native ranges, and fewer occur at latitudes lower than climate change, greater biotic resistance at lower latitudes, historical limitations on ranges in native regions, and the impacts of humans on species Electronic supplementary material The online version of this article (doi:10.1007/s10530-011-0094-8) contains distributions. -
Lake Chala Tilapia (Oreochromis Hunteri) Ecological Risk Screening Summary
Lake Chala Tilapia (Oreochromis hunteri) Ecological Risk Screening Summary U.S. Fish & Wildlife Service, March 2012 Revised, June 2018 Web Version, 12/15/2020 Organism Type: Fish Overall Risk Assessment Category: Uncertain Photo: D. H. Eccles. Licensed under Creative Commons BY-NC 3.0. Available: http://www.fishbase.org/photos/PicturesSummary.php?StartRow=0&ID=2032&what=species&T otRec=2. (June 18, 2018). 1 Native Range and Status in the United States Native Range From Froese and Pauly (2018a): “Africa: endemic to Lake Chala [Seegers et al. 2003].” 1 Status in the United States No records of Oreochromis hunteri in trade or in the wild in the United States were found. The Florida Fish and Wildlife Conservation Commission has listed the tilapia Oreochromis hunteri as a prohibited species. Prohibited nonnative species (FFWCC 2018), "are considered to be dangerous to the ecology and/or the health and welfare of the people of Florida. These species are not allowed to be personally possessed or used for commercial activities. All species in the genus Oreochromis are considered regulated Type A species in Washington. Regulated Type A species (Washington State Senate 2019) are “nonnative aquatic animal species that pose a low to moderate invasive risk that can be managed based on intended use or geographic scope of introduction, have a beneficial use, and are a priority for department-led or department-approved management of the species' beneficial use and invasive risks.” Possession of any species of tilapia is prohibited without permit in the State of Louisiana (Louisiana State Legislature 2019). O. amphimelas falls within Group I of New Mexico’s Department of Game and Fish Director’s Species Importation List (New Mexico Department of Game and Fish 2010). -
Climatic Effects on Lake Basins. Part I: Modeling Tropical Lake Levels
15 JUNE 2011 R I C K O E T A L . 2983 Climatic Effects on Lake Basins. Part I: Modeling Tropical Lake Levels MARTINA RICKO AND JAMES A. CARTON Department of Atmospheric and Oceanic Science, University of Maryland, College Park, College Park, Maryland CHARON BIRKETT Earth System Science Interdisciplinary Center, University of Maryland, College Park, College Park, Maryland (Manuscript received 28 December 2009, in final form 9 December 2010) ABSTRACT The availability of satellite estimates of rainfall and lake levels offers exciting new opportunities to estimate the hydrologic properties of lake systems. Combined with simple basin models, connections to climatic variations can then be explored with a focus on a future ability to predict changes in storage volume for water resources or natural hazards concerns. This study examines the capability of a simple basin model to estimate variations in water level for 12 tropical lakes and reservoirs during a 16-yr remotely sensed observation period (1992–2007). The model is constructed with two empirical parameters: effective catchment to lake area ratio and time delay between freshwater flux and lake level response. Rainfall datasets, one reanalysis and two satellite-based observational products, and two radar-altimetry-derived lake level datasets are explored and cross checked. Good agreement is observed between the two lake level datasets with the lowest correlations occurring for the two small lakes Kainji and Tana (0.87 and 0.89). Fitting observations to the simple basin model provides a set of delay times between rainfall and level rise ranging up to 105 days and effective catchment to lake ratios ranging between 2 and 27. -
Morphological Development of Embryos and Juveniles in the Mozambique Tilapia, Oreochromis Mossambicus As a Direct Developmental Fish Under Rearing Conditions
SUISANZOSHOKU 51(3), 295-306 (2003) Morphological Development of Embryos and Juveniles in the Mozambique Tilapia, Oreochromis mossambicus as a Direct Developmental Fish under Rearing Conditions Katsunori TACHIHARA*1,2 and Emi OBARA*1 (Accepted June 17, 2003) Abstract: The Mozambique tilapia, Oreochromis mossambicus is one of the species introduced to Okinawa Island. This species breeds widely in the rivers of the island. In order to understand the biological aspects of O. mossambicus under the natural conditions of the island, a detailed observa- tion of early morphological development was done under rearing conditions. The development of O . mossambicus was studied; it consisted of an embryonic phase of approximately 88 hours and 30 minutes, a free embryonic phase of about 12 days, followed by the juvenile period. The embryo became free-swimming on the sixth day of the free embryonic phase. The osteological develop- ment using enzyme-cleared specimens indicated that after reaching the juvenile stage, develop- ment of almost basic bones was complete 25 days after hatching. Key words: Oreochromis mossambicus; Direct development; Early life history; Okinawa Island The Mozambique tilapia, Oreochromis mos- sambicus is a freshwater fish, which has been Materials and Methods introduced to Okinawa Island1-3). The species is endemic to southern African rivers, lagoons Three mouthbreeding females (122.7 to and lakes, and ranges from the lower Zambezi 124.7 mm in standard length) harboring newly system in the north to the Bushmans River fertilized ova were collected from the Onaha in the south4). This species was introduced to River, Nishihara, Okinawa, Japan, on June 4, Okinawa Island in 1954 from Taiwan as a source 1997, using a cast net (mesh size: 1•~1 cm).