Chinese Mitten Crab (Eriocheir Sinensis) in San Francisco Bay
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Eriocheir Sinensis Potential in RI COASTAL WATERS Chinese Mitten Crab Invader
GUIDE TO MARINE INVADERS Eriocheir sinensis Potential IN RI COASTAL WATERS Chinese mitten crab Invader PHYSICAL DESCRIPTION • Dense fuzzy patches on claws of adults and larger juveniles (>1 inch) • Regenerated claws and claws of smaller juveniles may not have fuzz • Claws are equally sized and white-tipped • Four lateral spines on each side of carapace (shell); notch between the eyes • Carapace light-brown to olive green color; width up to 4 in (10 cm) • Sharp-tipped walking legs of adult over twice as long as carapace width Lee Mecum, CDF&G notch Adult Eriocheir sinensis fuzzy claws with HABITAT PREFERENCE white pincers • Catadromous life cycle: begins as estuarine larva, migrates into freshwater streams for 1-4 years, then returns to coast to reproduce 4 lateral • Burrows in the bottom and banks of freshwater rivers and estuaries spines • Tolerates a wide range of temperatures • Able to survive in highly altered and polluted aquatic habitats • Adept at walking on land and around barriers • Nondiscriminating omnivores that consume plants and prey on fish and benthic invertebrates (clams, worms, shrimp) 1 2 3 4 5 6 © Rob Gough, DFBW 7 8 GUIDE TO MARINE INVADERS Eriocheir sinensis Potential IN RI COASTAL WATERS Chinese mitten crab Invader INVASION STATUS & ECOLOGICAL CONCERNS Native to east Asia, Eriocheir sinensis has achieved a global distribution that includes several countries in central and western Europe and most recently the U.S. Pacific and Atlantic coasts. In 1992, it was found reproducing in San Francisco Bay. By 1998, E.sinensis had spread throughout the bay and has since expanded upstream into the Sacramento and San Joaquin Rivers. -
Eriocheir Sinensis Potential in the GULF of MAINE Chinese Mitten Crab Invader
GUIDE TO MARINE INVADERS Eriocheir sinensis Potential IN THE GULF OF MAINE Chinese mitten crab Invader PHYSICAL DESCRIPTION • Dense fuzzy patches on claws of adults and larger juveniles (>1 inch) • Regenerated claws and claws of smaller juveniles may not have fuzz • Claws are equally sized and white-tipped • Four lateral spines on each side of carapace (shell); notch between the eyes • Carapace light-brown to olive green color; width up to 4 in (10 cm) • Sharp-tipped walking legs of adult over twice as long as carapace width Lee Mecum, CDF&G notch Adult Eriocheir sinensis fuzzy claws with HABITAT PREFERENCE white pincers • Catadromous life cycle: begins as estuarine larva, migrates into freshwater streams for 1-4 years, then returns to coast to reproduce 4 lateral • Burrows in the bottom and banks of freshwater rivers and estuaries spines • Tolerates a wide range of temperatures • Able to survive in highly altered and polluted aquatic habitats • Adept at walking on land and around barriers • Nondiscriminating omnivores that consume plants and prey on fish and benthic invertebrates (clams, worms, shrimp) Rob Gough 1 2 3 4 5 6 7 8 GUIDE TO MARINE INVADERS Eriocheir sinensis Potential IN THE GULF OF MAINE Chinese mitten crab Invader INVASION STATUS & ECOLOGICAL CONCERNS Native to east Asia, Eriocheir sinensis has achieved a global distribution that includes several countries in central and western Europe and most recently the U.S. Pacific and Atlantic coasts. In 1992, it was found reproducing in San Francisco Bay. By 1998, E.sinensis had spread throughout the bay and has since expanded upstream into the Sacramento and San Joaquin Rivers. -
Environmental DNA (Edna)
fenvs-08-612253 December 1, 2020 Time: 20:27 # 1 ORIGINAL RESEARCH published: 07 December 2020 doi: 10.3389/fenvs.2020.612253 Environmental DNA (eDNA) Monitoring of Noble Crayfish Astacus astacus in Lentic Environments Offers Reliable Presence-Absence Surveillance – But Fails to Predict Population Density Stein I. Johnsen1†, David A. Strand2*†, Johannes C. Rusch2,3 and Trude Vrålstad2 1 Norwegian Institute for Nature Research, Lillehammer, Norway, 2 Norwegian Veterinary Institute, Oslo, Norway, 3 Department of Biosciences, University of Oslo, Oslo, Norway Noble crayfish is the most widespread native freshwater crayfish species in Europe. It is threatened in its entire distribution range and listed on the International Union for Edited by: Concervation Nature- and national red lists. Reliable monitoring data is a prerequisite for Ivana Maguire, University of Zagreb, Croatia implementing conservation measures, and population trends are traditionally obtained Reviewed by: from catch per unit effort (CPUE) data. Recently developed environmental DNA Michael Sweet, (eDNA) tools can potentially improve the effort. In the past decade, eDNA monitoring University of Derby, United Kingdom Chloe Victoria Robinson, has emerged as a promising tool for species surveillance, and some studies have University of Guelph, Canada established that eDNA methods yield adequate presence-absence data for crayfish. *Correspondence: There are also high expectations that eDNA concentrations in the water can predict David A. Strand biomass or relative density. However, eDNA studies for crayfish have not yet been [email protected] able to establish a convincing relationship between eDNA concentrations and crayfish †These authors have contributed equally to this work density. This study compared eDNA and CPUE data obtained the same day and with high sampling effort, and evaluated whether eDNA concentrations can predict Specialty section: relative density of crayfish. -
How the Red Swamp Crayfish Took Over the World Running Title Invasion
1 Title 2 One century away from home: how the red swamp crayfish took over the world 3 Running Title 4 Invasion history of Procambarus clarkii 5 Authors 6 Francisco J. Oficialdegui1*, Marta I. Sánchez1,2,3, Miguel Clavero1 7 8 Affiliations 9 1. Estación Biológica de Doñana (EBD-CSIC). Avenida Américo Vespucio 26, 10 Isla de la Cartuja. 41092. Seville, Spain 11 2. Instituto Universitario de Investigación Marina (INMAR) Campus de Excelencia 12 Internacional/Global del Mar (CEI·MAR) Universidad de Cádiz. Puerto Real, 13 Cadiz (Spain). 14 3. Present address: Departamento de Biología Vegetal y Ecología, Facultad de 15 Biología, Universidad de Sevilla, Apartado 1095, 41080, Seville, Spain 16 17 Contact: [email protected] Francisco J. Oficialdegui. Department of Wetland 18 Ecology. Estación Biológica de Doñana (EBD-CSIC). C/Américo Vespucio 26. Isla de 19 la Cartuja. 41092. Seville (Spain). Phone: 954466700. ORCID: 0000-0001-6223-736X 20 21 Marta I. Sánchez. [email protected] ORCID: 0000-0002-8349-5410 22 Miguel Clavero. [email protected] ORCID: 0000-0002-5186-0153 23 24 Keywords: Alien species; GBIF; Global translocations; Historical distributions; 25 iNaturalist; Invasive species; Pathways of introduction; Procambarus clarkii; 26 1 27 ABSTRACT 28 The red swamp crayfish (Procambarus clarkii) (hereafter RSC), native to the southern 29 United States and north-eastern Mexico, is currently the most widely distributed 30 crayfish globally as well as one of the invasive species with most devastating impacts 31 on freshwater ecosystems. Reconstructing the introduction routes of invasive species 32 and identifying the motivations that have led to those movements, is necessary to 33 accurately reduce the likelihood of further introductions. -
THE DISTRIBUTION of NATIVE and INTRODUCED SPECIES of CRAYFISH in AUSTRIA MANFRED POCKL (Dr M. Pockl, Department of Limnology, In
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Aquatic Commons 4 MANFRED POCKL THE DISTRIBUTION OF NATIVE AND INTRODUCED SPECIES OF CRAYFISH IN AUSTRIA MANFRED POCKL (Dr M. Pockl, Department of Limnology, Institute of Zoology, University of Vienna, and State Government of Lower Austria, Experts for the Conservation of Nature, Landhausplatz 1, A-3109 St Pölten, Austria.) Introduction Crayfish are the largest invertebrates found in European freshwaters north of the Mediterannean region, where river-crabs (Potamon) also occur. Some crayfish attain body lengths greater than 25 cm and exceed 350 g in weight. These decapod crustaceans are omnivores, feeding on a wide variety of small invertebrates, fish, algae and higher aquatic plants, including some riparian vegetation. They also scavenge on dead and dying plants and animals. However, their quantitative role in the trophic economy of streams and lakes is not well understood, especially in relation to population biomass and potential competition with fish. Like the latter, however, crayfish have long been prized by man as a source of food, and in parts of Europe some species have been exploited commercially for many centuries. The most notable of these is the fishery based on the red-clawed or noble crayfish Astacus astacus, which was decimated by the lethal plague fungus Aphanomyces astaci in the late 19th and early 20th centuries. Importations of relatively large species from North America, which are resistant to the fungus but can act as carriers, has led to concerns for the continued existence and conservation of native European species, several of which are now listed as endangered species. -
Top 10 Species Groups in Global Aquaculture 2018
Top 10 species groups in global aquaculture 2018 FAO Fisheries and Aquaculture Department reduce to 10,5pt so until note in p.2 his factsheet presents the top 10 species groups in global aquaculture 2018 (Table 1) and Tfeatures one of the fastest growing species groups: crayfishes (Table 2). The ranking of all 63 species groups in global aquaculture 2018 is illustrated on the back cover. More information about the top 10 species groups at regional and national level can be found in a more comprehensive factsheet as Supplementary Materials.1 The comprehensive factsheet also elaborates on the species grouping methodology used in the ranking exercise. Top 10 species groups in world aquaculture 2018 In 2018, 438 ASFIS – Aquatic Sciences and Fisheries Information System – species items2 were farmed in 196 countries/territories with 115 million tonnes of world production, an increase of 2.3 million tonnes (2.04 percent) from the 2017 level (Table 1). There has been no significant change on the top 10 list between 2017 and 2018 (Table 1).3 The top four items remained unchanged, while marine shrimps and prawns moved up from #6 to #5 switching positions with oysters. Scallops (#10 in 2017) dropped down to #11 in 2018 because of the 2.3 percent decline in its production quantity. WAPI FACTSHEET WAPI Half of the top 10 species groups grew faster than the average 2.04 percent growth for all species between 2017 and 2018: freshwater fishes nei (#10; 16.58 percent), marine shrimps and prawns (#5; 5.04 percent), oysters (#6; 4.64 percent), carps, barbels and other cyprinids (#1; 3.87 percent) and brown seaweeds (#3; 3.4 percent). -
California Freshwater Shrimparesmall.Females Areusually (Corpus)
Endangered SpecU.S. Environmental iesFacts Protection Agency California Freshwater Shrimp Syncaris pacifica Description and Ecology Status Endangered, listed October 31, 1988. of Marin, Sonoma and Napa counties. They are still found in all three counties but in much fewer numbers and fewer Critical Habitat Not designated. streams. The distribution of the shrimp has been separated Appearance The California freshwater shrimp is a 10- into four drainage units: 1) tributary streams of the lower legged crustacean belonging to the atyid family. Of the three Russian River drainage, that flow westward to the Pacific other atyid members in North America, two are also listed Ocean, 2) coastal streams flowing westward directly into as endangered (Kentucky cave shrimp (Palaemonias ganteri) the Pacific Ocean, 3) streams draining into Tomales Bay, Female California freshwater shrimp with egg s, courtes y of Larr y Serpa and Alabama cave shrimp (Palaemonias alabamae)) and one and 4) streams flowing southward into San Pablo Bay. While which once inhabited coastal streams in California is believed California freshwater shrimp in laboratories can tolerate The California freshwater shrimp to be extinct (Pasadena shrimp (Syncaris pasadenae)). brackish waters, they are unable to tolerate ocean salinities. is an endangered species. These species were believed to have been isolated from a It is thought that the isolated streams that harbor these Endangered species are marine environment during the Jurassic period. They are shrimp were once connected, but later separated by geologic plants and animals that are anatomically distinguished from other shrimp by the length of uplift and rising sea level. in immediate danger of their pincer-like claws (chelae) and the bristles (setae) at the Habitat Within the low elevation-low gradient streams tips of the first two chelae. -
The Crayfish Plague Pathogen Can Infect Freshwater- Inhabiting Crabs
Freshwater Biology (2014) 59, 918–929 doi:10.1111/fwb.12315 The crayfish plague pathogen can infect freshwater- inhabiting crabs ,1 †,‡,1 †,‡ § JIRISVOBODA* , DAVID A. STRAND ,TRUDEVRALSTAD ,FREDERIC GRANDJEAN ,LENNART ¶ † †† EDSMAN , PAVEL KOZAK**, ANTONIN KOUBA**, ROSA F. FRISTAD , SEVAL BAHADIR KOCA AND ADAM PETRUSEK* *Faculty of Science, Department of Ecology, Charles University in Prague, Prague, Czech Republic †Norwegian Veterinary Institute, Oslo, Norway ‡Department of Biosciences, Microbial Evolution Research Group, University of Oslo, Oslo, Norway §Laboratoire Ecologie et Biologie des interactions, equipe Ecologie, Evolution, Universite de Poitiers, Symbiose UMR-CNRS 6556, Poitiers Cedex, France ¶Department of Aquatic Resources, Institute of Freshwater Research, Swedish University of Agricultural Sciences, Drottningholm, Sweden **Faculty of Fisheries and Protection of Waters, South Bohemian Research Center of Aquaculture and Biodiversity of Hydrocenoses, University of South Bohemia in Ceske Budejovice, Vodnany, Czech Republic ††Egirdir Fisheries Faculty, Suleyman€ Demirel University, Isparta, Turkey SUMMARY 1. The oomycete Aphanomyces astaci is generally considered a parasite specific to freshwater crayfish, and it has become known as the crayfish plague pathogen. Old experimental work that reported transmission of crayfish plague to the Chinese mitten crab Eriocheir sinensis, and the ability of A. astaci to grow in non-decapod crustaceans, has never been tested properly. 2. We re-evaluated the host range of A. astaci by screening for the presence of A. astaci in two crab species cohabiting with infected crayfish in fresh waters, as well as in other higher crustaceans from such localities. The animals were tested with species-specific quantitative PCR, and the pathogen determination was confirmed by sequencing of an amplified fragment of the nuclear internal tran- scribed spacer. -
The Chinese Mitten Crab Eriocheir Sinensis (Decapoda: Grapsidae)
The Chinese mitten OCEANOLOGIA, 42 (3), 2000. pp. 375–383. crab Eriocheir sinensis 2000, by Institute of (Decapoda: Grapsidae) Oceanology PAS. from Polish waters* KEYWORDS Catadromous species Eriocheir sinensis Non-indigenous organism Monika Normant Anna Wiszniewska Anna Szaniawska Institute of Oceanography, University of Gdańsk, al. Marszałka J. Piłsudskiego 46, PL–81–378 Gdynia, Poland; e-mail: [email protected] Manuscript received 2 June 2000, reviewed 19 June 2000, accepted 30 June 2000. Abstract The Chinese mitten crab Eriocheir sinensis Milne-Edwards, 1854 is a newcomer to the Baltic Sea. Previous studies have shown that since the 1940s single large specimens of this species have been caught annually in Polish waters. The invasion of the Chinese mitten crab has been reported from many European countries, including Poland, where it is especially abundant in the Odra Estuary. Of 186 specimens captured in Lake Dąbie in August 1998, 45% were females and 55% males. The carapace width of these crabs varied between 53 and 88 mm and the average wet weight was 169 ± 45.3 g. 1. Introduction New species, sometimes from very remote regions, have appeared in recent decades in the Baltic Sea. The introduction of these organisms to the Baltic is primarily the result of human activity, most often during the dumping of ballast water from ships (Ingle 1986). One of these immigrants to the Baltic is the Chinese mitten crab Eriocheir sinensis Milne-Edwards, 1854, so named because of the dense patches of hair on the claws of * The research was supported by grant No. 0915/P04/98/15 from the Polish State Committee for Scientific Research. -
The Biological Resources Section Provides Background Information
4.5 BIOLOGICAL RESOURCES The Biological resources section provides background information on sensitive biological resources within Napa County, the regulations and programs that provide for their protection, and an assessment of the potential impacts to biological resources of implementing the Napa County General Plan Update. This section is based upon information presented in the Biological Resources Chapter of the Napa County Baseline Data Report (Napa County, BDR 2005). Additional information on the topics presented herein can be found in these documents. Both documents are incorporated into this section by reference. This section addresses biological resources other than fisheries which are separately addressed in Section 4.6. 4.5.1 SETTING REGIONAL SETTING The Napa County is located in the Coast Ranges Geomorphic Province. This province is bounded on the west by the Pacific Ocean and on the east by the Great Valley geomorphic province. A dominant characteristic of the Coast Ranges Province is the general northwest- southeast orientation of its valleys and ridgelines. In Napa County, located in the eastern, central section of the province, this trend consists of a series of long, linear, major and lesser valleys, separated by steep, rugged ridge and hill systems of moderate relief that have been deeply incised by their drainage systems. The County is located within the California Floristic Province, the portion of the state west of the Sierra Crest that is known to be particularly rich in endemic plant species (Hickman 1993, Stein et al. 2000). LOCAL SETTING The County’s highest topographic feature is Mount St. Helena, which is located in the northwest corner of the County and whose peak elevation is 4,343 feet. -
Koura, Paranephrops Planifrons) in the Lower North Island, New Zealand
Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and private study only. The thesis may not be reproduced elsewhere without the permission of the Author. Habitat determinants and predatory interactions of the endemic freshwater crayfish (Koura, Paranephrops planifrons) in the Lower North Island, New Zealand. A thesis presented in partial fulfillment of the requirements for the degree of Masters of Science in Ecology at Massey University, Palmerston North, New Zealand. Logan Arthur Brown 2009 Acknowledgements My gratitude goes to all those who helped me throughout my thesis. The completion of this has taken many years and is thanks to the efforts of many who have helped me with fieldwork, made suggestions on ways to carry out experiments and been there for general support. A special thanks must go to my partner Emma who has put up with me for three years trying to complete this, also to my family and friends for their support. Thanks to my supervisor Associate Professor Russell Death for helping come up with the original topic and the comments provided on drafts. Thanks also to Fiona Death for proof reading final drafts of my thesis. The following people gave up their time to come and help me in the field. Matt Denton-Giles, Emma Round, Charlotte Minson, Jono Tonkin, Nikki Atkinson, Travis Brown, Jan Brown, Ray Brown, Peter Bills, Hannah Bills, Caitlin Bills, Brayden Bills, Hannah Rainforth, Shaun Nielson, Jess Costall, Emily Atkinson, Nikki McArthur, Carol Nicholson, Abby Deuel, Amy McDonald, Kiryn Weaver, Cleland Wallace, and Lorraine Cook. -
Elias Kane Science Fair Final Draft I. Problem: Which Environmental
Elias Kane Science Fair Final Draft I. Problem: Which environmental factor: pH, or the presence of the pesticide methoprene most inhibits the American lobster’s (Homarus americanus) growth rate as modeled by the Red Swamp crayfish (Procambarus clarkii)? II. Collected Information Long Island Sound serves as a prime habitat for thousands of species due to its relatively protected waters and stable environmental conditions. The American lobster (Homarus americanus) is one of the most integral scavengers of Long Island Sound. In addition, the American lobster is a backbone fishery of much of northeastern North America. Prior to 1999, in combined Connecticut and New York waters, the total lobster catch was between 7-11.7 million pounds. In 2004, the total lobster catch had fallen to 1.6 million pounds (Balcom &Howell, 2006, p. 1). This is due to a large American lobster die-off in late fall of 1999. Long Island Sound is in the southern extent of the American lobster’s range. Due to this fact, the temperature is considered likely to cause the organisms stress. Die-offs of the American lobster population have happened in the past, just never in the same magnitude as that of 1999 (Balcom & Howell, 2006, p. 5). Temperature as well as many other factors worked together to cause this particularly massive die-off. Several harmful variables in Long Island Sound led to the death of millions of lobsters. Climate change, in the form of temperature rise and ocean acidification, pesticide, shell disease, and parasitic amoebae which cause paramoebiasis, all led to this die-off (Balcom & Howell, 2006, p.