Crustacea: Branchiopoda: Anostraca
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Fig. Ap. 2.1. Denton Tending His Fairy Shrimp Collection
Fig. Ap. 2.1. Denton tending his fairy shrimp collection. 176 Appendix 1 Hatching and Rearing Back in the bowels of this book we noted that However, salts may leach from soils to ultimately if one takes dry soil samples from a pool basin, make the water salty, a situation which commonly preferably at its deepest point, one can then "just turns off hatching. Tap water is usually unsatis- add water and stir". In a day or two nauplii ap- factory, either because it has high TDS, or because pear if their cysts are present. O.K., so they won't it contains chlorine or chloramine, disinfectants always appear, but you get the idea. which may inhibit hatching or kill emerging If your desire is to hatch and rear fairy nauplii. shrimps the hi-tech way, you should get some As you have read time and again in Chapter 5, guidance from Brendonck et al. (1990) and temperature is an important environmental cue for Maeda-Martinez et al. (1995c). If you merely coaxing larvae from their dormant state. You can want to see what an anostracan is like, buy some guess what temperatures might need to be ap- Artemia cysts at the local aquarium shop and fol- proximated given the sample's origin. Try incu- low directions on the container. Should you wish bation at about 3-5°C if it came from the moun- to find out what's in your favorite pool, or gather tains or high desert. If from California grass- together sufficient animals for a study of behavior lands, 10° is a good level at which to start. -
Phylogenetic Analysis of Anostracans (Branchiopoda: Anostraca) Inferred from Nuclear 18S Ribosomal DNA (18S Rdna) Sequences
MOLECULAR PHYLOGENETICS AND EVOLUTION Molecular Phylogenetics and Evolution 25 (2002) 535–544 www.academicpress.com Phylogenetic analysis of anostracans (Branchiopoda: Anostraca) inferred from nuclear 18S ribosomal DNA (18S rDNA) sequences Peter H.H. Weekers,a,* Gopal Murugan,a,1 Jacques R. Vanfleteren,a Denton Belk,b and Henri J. Dumonta a Department of Biology, Ghent University, Ledeganckstraat 35, B-9000 Ghent, Belgium b Biology Department, Our Lady of the Lake University of San Antonio, San Antonio, TX 78207, USA Received 20 February 2001; received in revised form 18 June 2002 Abstract The nuclear small subunit ribosomal DNA (18S rDNA) of 27 anostracans (Branchiopoda: Anostraca) belonging to 14 genera and eight out of nine traditionally recognized families has been sequenced and used for phylogenetic analysis. The 18S rDNA phylogeny shows that the anostracans are monophyletic. The taxa under examination form two clades of subordinal level and eight clades of family level. Two families the Polyartemiidae and Linderiellidae are suppressed and merged with the Chirocephalidae, of which together they form a subfamily. In contrast, the Parartemiinae are removed from the Branchipodidae, raised to family level (Parartemiidae) and cluster as a sister group to the Artemiidae in a clade defined here as the Artemiina (new suborder). A number of morphological traits support this new suborder. The Branchipodidae are separated into two families, the Branchipodidae and Ta- nymastigidae (new family). The relationship between Dendrocephalus and Thamnocephalus requires further study and needs the addition of Branchinella sequences to decide whether the Thamnocephalidae are monophyletic. Surprisingly, Polyartemiella hazeni and Polyartemia forcipata (‘‘Family’’ Polyartemiidae), with 17 and 19 thoracic segments and pairs of trunk limb as opposed to all other anostracans with only 11 pairs, do not cluster but are separated by Linderiella santarosae (‘‘Family’’ Linderiellidae), which has 11 pairs of trunk limbs. -
Updated Status of Anostraca in Pakistan
Int. J. Biol. Res., 2(1): 1-7, 2014. UPDATED STATUS OF ANOSTRACA IN PAKISTAN Quddusi B. Kazmi1* and Razia Sultana2 1Marine Reference Collection and Resource Center; University of Karachi, Karachi-75270, Pakistan 2Food & Marine Resources Research Center, PCSIR Laboratories Complex Karachi; Karachi-75270, Pakistan *Corresponding author e-mail: [email protected] ABSTRACT Previously, nine species of the order Anostraca have been reported from Pakistan viz, Branchinella hardingi (Qadri and Baqai, 1956), B. spinosa (H. Milne Edwards, 1840) (now Phallocryptus spinosa), Streptocephalus simplex, 1906, S. dichotomus Baird, 1860, S. maliricus Qadri and Baqai, 1956, S. lahorensis Ghauri and Mahoon, 1980, Branchipus schaefferi Fischer, 1834, Chirocephalus priscus Daday, 1910 and Artemia sp. In the present report these Pakistani species are reviewed. Streptocephalus dichotomus collected from Pasni (Mekran), housed in the Smithsonian National Museum of Natural History, USA (cat no. 213712) is inserted herein and another specimen of Streptocephalus sp., from a new locality, collected from Kalat not yet reported, is illustrated and described in this report, thus extending genus range further Northward. The need for further surveys directed towards getting the knowledge necessary in order to correctly understand and manage temporary pools- the elective habitat of large branchiopods is stressed. KEYWORDS: Anostraca, Brianchiopoda, Pakistan, Present status INTRODUCTION Anostraca is one of the four orders of Crustacea in the Class Branchiopoda. It is the most -
Vernal Pool Fairy Shrimp (Branchinecta Lynchi)
Invertebrates Vernal Pool Fairy Shrimp (Branchinecta lynchi) Vernal Pool Fairy Shrimp (Brachinecta lynchi) Status State: Meets the requirements as a “rare, threatened, or endangered species” under CEQA Federal: Threatened Critical Habitat: Designated 2006 (USFWS 2006) Population Trend Global: Declining due to habitat loss and fragmentation (Eriksen and Belk 1999) State: As above Within Inventory Area: Unknown Data Characterization The location database for the vernal pool fairy shrimp (Brachinecta lynchi) within the inventory area includes 6 records from 1993, 1997, and 1999. The majority of locations are vernal pools within non-native grassland. Other natural and artificial habitats have a high probability of being occupied by additional populations of the vernal pool fairy shrimp throughout the grassland habitats within the ECCC HCP/NCCP inventory area. Beyond the original description (Eng et al. 1990), a scanning electron micrograph of the cyst (resting egg) (Hill and Shepard 1997), and some generalized natural history data (Helm 1997), no peer-reviewed technical literature has been published concerning the vernal pool fairy shrimp. Eriksen and Belk (1999) presented a brief discussion of the vernal pool fairy shrimp and provided a distribution map. Range The vernal pool fairy shrimp is found from Jackson County near Medford, Oregon, throughout the Central Valley, and west to the central Coast Ranges. Isolated southern populations occur on the Santa Rosa Plateau and near Rancho California in Riverside County (Eng et al.1990, Eriksen -
Freshwater Crustaceans As an Aboriginal Food Resource in the Northern Great Basin
UC Merced Journal of California and Great Basin Anthropology Title Freshwater Crustaceans as an Aboriginal Food Resource in the Northern Great Basin Permalink https://escholarship.org/uc/item/3w8765rq Journal Journal of California and Great Basin Anthropology, 20(1) ISSN 0191-3557 Authors Henrikson, Lael S Yohe, Robert M, II Newman, Margaret E et al. Publication Date 1998-07-01 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Joumal of Califomia and Great Basin Anthropology Vol. 20, No. 1, pp. 72-87 (1998). Freshwater Crustaceans as an Aboriginal Food Resource in the Northern Great Basin LAEL SUZANN HENRIKSON, Bureau of Land Management, Shoshone District, 400 W. F Street, Shoshone, ID 83352. ROBERT M. YOHE II, Archaeological Survey of Idaho, Idaho State Historical Society, 210 Main Street, Boise, ID 83702. MARGARET E. NEWMAN, Dept. of Archaeology, University of Calgary, Alberta, Canada T2N 1N4. MARK DRUSS, Idaho Power Company, 1409 West Main Street, P.O. Box 70. Boise, ID 83707. Phyllopods of the genera Triops, Lepidums, and Branchinecta are common inhabitants of many ephemeral lakes in the American West. Tadpole shrimp (Triops spp. and Lepidums spp.) are known to have been a food source in Mexico, and fairy shrimp fBranchinecta spp.) were eaten by the aborigi nal occupants of the Great Basin. Where found, these crustaceans generally occur in numbers large enough to supply abundant calories and nutrients to humans. Several ephemeral lakes studied in the Mojave Desert arul northern Great Basin currently sustain large seasonal populations of these crusta ceans and also are surrounded by numerous small prehistoric camp sites that typically contain small artifactual assemblages consisting largely of milling implements. -
Federal Register/Vol. 81, No. 217/Wednesday, November 9
Federal Register / Vol. 81, No. 217 / Wednesday, November 9, 2016 / Notices 78843 Permit No. TE–046262 California for the purpose of enhancing Department of the Interior, Bureau of the species’ survival. Land Management (BLM), the San Juan Applicant: Blake Claypool, San Diego, California Permit No. TE–048739 Islands National Monument Advisory Committee (MAC) will meet as The applicant requests a new permit Applicant: Daniel A. Cordova of U.S. indicated below: to take (survey by pursuit) the Quino Bureau of Reclamation, Sacramento, checkerspot butterfly (Euphydryas California DATES: The MAC will hold a public editha quino); and take (harass by meeting Monday, November 28th, 2016. survey, capture, handle, release, collect The applicant requests a permit The meeting will run from 8:30 a.m. to vouchers, and collect branchiopod amendment to take (harass by survey, 4:30 p.m. The meeting will be held at cysts) the Conservancy fairy shrimp capture, handle, release, collect San Juan Island Grange Hall in Friday (Branchinecta conservatio), longhorn vouchers, and collect branchiopod Harbor on San Juan Island. Public fairy shrimp (Branchinecta cysts) the Conservancy fairy shrimp comment periods will be available in (Branchinecta conservatio), longhorn longiantenna), San Diego fairy shrimp the afternoon from noon until 12:30 and fairy shrimp (Branchinecta (Branchinecta sandiegonensis), 3:00 p.m. until 3:30 p.m. Riverside fairy shrimp (Streptocephalus longiantenna), and vernal pool tadpole woottoni), and vernal pool tadpole shrimp (Lepidurus packardi); in FOR FURTHER INFORMATION CONTACT: shrimp (Lepidurus packardi) in conjunction with survey activities Marcia deChadene`des, San Juan Islands conjunction with survey activities throughout the range of the species in National Monument Manager, P.O. -
Persistence of Branchinecta Paludosa (Anostraca) in Southern Wyoming, with Notes on Zoogeography
This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. JOURNAL OF CRUSTACEAN BIOLOGY, 13(1): 184-189, 1993 PERSISTENCE OF BRANCHINECTA PALUDOSA (ANOSTRACA) IN SOUTHERN WYOMING, WITH NOTES ON ZOOGEOGRAPHY James F. Saunders III, Denton Belk, and Richard Dufford ABSTRACT The fairy shrimp Branchinectapaludosa is a persistentresident of aestival ponds at high elevation in the Medicine Bow Mountains of southernWyoming. These populationsare far removed from the Arctic tundrahabitat that typifiesthe distributionof the species, and appear to representthe southern margin of the range in North America. All of the records for the northernUnited States and southernCanada appear to lie along the CentralFlyway that is a major migrationroute for waterfowland shorebirdsthat nest in the Arctic. Passive dispersal probablyprovides for frequentcolonization of marginalhabitats and gene flow to established populations. The fairy shrimp Branchinectapaludosa have been deposited in the University of (Muller)is widely distributedin the circum- Colorado Museum (UCM 2192, 2193, polar tundra of the Holarctic region (Vek- 2194). The Snowy Range is an axial rem- hoff, 1990). In Europe, it occurs chiefly at nant which rises about 300 m above the latitudes above 60?N, but there are isolated surrounding Medicine Bow Mountains recordsfrom the High Tatra Mountains on (Houston and others, 1978). The ponds are the borderbetween Czechoslovakiaand Po- mainly in the upperTelephone Creek drain- land at about 49?N (Brtek, 1976). Records age at elevations of 3,200-3,350 m. Most for Russia are typically along the Arctic of the ponds are underlainby the Nash Fork margin, but include the southern tip of the formation (Houston and others, 1978), and Kamchatka Peninsula at 52?N (Linder, the characteristicmetadolomite is present 1932). -
Egg Hatching and Life History of A
EGG HATCHING AND LIFE HISTORY OF A FAIRY SHRIMP BRANCHINECTA MACKINI DEXTER (CRUSTACEA: ANOSTRACA) IN A MOHAVE DOCKET PLAYA DRY LAKE)' DESERT (RABBIT 11-AFC-2 LARS CARPELAN LON R. BROWN AND H. DATE Universityof California, Riverside, California 92502 RECD. MAY 01 2012 Abstract. Observations on populations of Branchinecta mackini in temporaryponds, which last for as little as 3 days to as long as 4 months, on a desert playa showed that hatching of dehydratedcysts (eggs) follows initial entry of water into the basin if salinity remains low. Salinity ranges from an initial 0.5%o to as much as 34%o as the pond evaporates. Hatching is continuous at constant low salinity, but since salinity generally increases rapidly, initial hatch is usually of short duration. Additional periods of hatching follow further inflows of water or after melting of ice, that is, after reductions in salinity. The duration of hatching is in- versely proportional to rate of increase in salinity. When salinity of small-volume summer ponds increases at rates above 500 ppm (1,000 Vmhos) per day, there is virtual inhibitionof hatching. Laboratory studies showed that egg hatching was controlled by both salinity and oxygen operating in various combinations to inhibit or stimulate hatch. The hatching characteristics of desiccated eggs collected from the dried mud of the lake basin differedfrom non-dried eggs obtained from laboratory cultures after ejection from ovisacs of living females. The findingthat a salinity-oxygencomplex regulates hatching in a desert pond permitstenta- tive explanation of a differencebetween branchiopods of humid and arid regions. In both cases the branchiopods are characteristicof astatic waters, and stimulation of the egg to hatch must be by some factor that changes at the time of origin of the temporary pond. -
Table of Contents 2
Southwest Association of Freshwater Invertebrate Taxonomists (SAFIT) List of Freshwater Macroinvertebrate Taxa from California and Adjacent States including Standard Taxonomic Effort Levels 1 March 2011 Austin Brady Richards and D. Christopher Rogers Table of Contents 2 1.0 Introduction 4 1.1 Acknowledgments 5 2.0 Standard Taxonomic Effort 5 2.1 Rules for Developing a Standard Taxonomic Effort Document 5 2.2 Changes from the Previous Version 6 2.3 The SAFIT Standard Taxonomic List 6 3.0 Methods and Materials 7 3.1 Habitat information 7 3.2 Geographic Scope 7 3.3 Abbreviations used in the STE List 8 3.4 Life Stage Terminology 8 4.0 Rare, Threatened and Endangered Species 8 5.0 Literature Cited 9 Appendix I. The SAFIT Standard Taxonomic Effort List 10 Phylum Silicea 11 Phylum Cnidaria 12 Phylum Platyhelminthes 14 Phylum Nemertea 15 Phylum Nemata 16 Phylum Nematomorpha 17 Phylum Entoprocta 18 Phylum Ectoprocta 19 Phylum Mollusca 20 Phylum Annelida 32 Class Hirudinea Class Branchiobdella Class Polychaeta Class Oligochaeta Phylum Arthropoda Subphylum Chelicerata, Subclass Acari 35 Subphylum Crustacea 47 Subphylum Hexapoda Class Collembola 69 Class Insecta Order Ephemeroptera 71 Order Odonata 95 Order Plecoptera 112 Order Hemiptera 126 Order Megaloptera 139 Order Neuroptera 141 Order Trichoptera 143 Order Lepidoptera 165 2 Order Coleoptera 167 Order Diptera 219 3 1.0 Introduction The Southwest Association of Freshwater Invertebrate Taxonomists (SAFIT) is charged through its charter to develop standardized levels for the taxonomic identification of aquatic macroinvertebrates in support of bioassessment. This document defines the standard levels of taxonomic effort (STE) for bioassessment data compatible with the Surface Water Ambient Monitoring Program (SWAMP) bioassessment protocols (Ode, 2007) or similar procedures. -
Reanalysis and Revision of the Complete Mitochondrial Genome of Artemia Urmiana Günther, 1899 (Crustacea: Anostraca)
diversity Article Reanalysis and Revision of the Complete Mitochondrial Genome of Artemia urmiana Günther, 1899 (Crustacea: Anostraca) Alireza Asem 1,2,† , Amin Eimanifar 3,†, Weidong Li 4,*, Chun-Yang Shen 5, Farnaz Mahmoudi Shikhsarmast 1,6, Ya-Ting Dan 7, Hao Lu 1,2, Yang Zhou 8, You Chen 1,9, Pei-Zheng Wang 1,9,* and Michael Wink 10 1 Key Laboratory of Utilization and Protection of Tropical Marine Living Resources, Hainan Tropical Ocean University, Sanya 572000, China; [email protected] (A.A.); [email protected] (F.M.S.); [email protected] (H.L.); [email protected] (Y.C.) 2 College of Fisheries and Life Sciences, Hainan Tropical Ocean University, Sanya 572000, China 3 Independent Senior Scientist, Industrial District, Easton, MD 21601, USA; [email protected] 4 College of Ecology and Environment, Hainan Tropical Ocean University, Haikou 570000, China 5 Department of Biology, Chengde Medical University, Chengde 067000, China; [email protected] 6 College of Marine Science and Technology, Hainan Tropical Ocean University, Sanya 572000, China 7 College of Marine Science, Shanghai Ocean University, Shanghai 200000, China; [email protected] 8 Institute of Deep Sea Science and Engineering, Chinese Academy of Science, Sanya 572000, China; [email protected] 9 College of Ecology and Environment, Hainan Tropical Ocean University, Sanya 572000, China 10 Institute of Pharmacy and Molecular Biotechnology (IPMB), Heidelberg University, Im Neuenheimer Feld 364, 69120 Heidelberg, Germany; [email protected] * Correspondence: [email protected] (W.L.); [email protected] (P.-Z.W.) † Equal contribution as first author. Abstract: In the previously published mitochondrial genome sequence of Artemia urmiana (NC_021382 [JQ975176]), the taxonomic status of the examined Artemia had not been determined, due to partheno- Citation: Asem, A.; Eimanifar, A.; Li, W.; Shen, C.-Y.; Shikhsarmast, F.M.; genetic populations coexisting with A. -
Pennsylvania Statewide Seasonal Pool Ecosystem Classification
Pennsylvania Statewide Seasonal Pool Ecosystem Classification Description, mapping, and classification of seasonal pools, their associated plant and animal communities, and the surrounding landscape April 2009 Pennsylvania Natural Heritage Program i Cover photo by: Betsy Leppo, Pennsylvania Natural Heritage Program ii Pennsylvania Natural Heritage Program is a partnership of: Western Pennsylvania Conservancy, Pennsylvania Department of Conservation and Natural Resources, Pennsylvania Fish and Boat Commission, and Pennsylvania Game Commission. The project was funded by: Pennsylvania Department of Conservation and Natural Resources, Wild Resource Conservation Program Grant no. WRCP-06187 U.S. EPA State Wetland Protection Development Grant no. CD-973493-01 Suggested report citation: Leppo, B., Zimmerman, E., Ray, S., Podniesinski, G., and Furedi, M. 2009. Pennsylvania Statewide Seasonal Pool Ecosystem Classification: Description, mapping, and classification of seasonal pools, their associated plant and animal communities, and the surrounding landscape. Pennsylvania Natural Heritage Program, Western Pennsylvania Conservancy, Pittsburgh, PA. iii ACKNOWLEDGEMENTS We would like to thank the following organizations, agencies, and people for their time and support of this project: The U.S. Environmental Protection Agency (EPA) and the Pennsylvania Department of Conservation and Natural Resources (DCNR) Wild Resource Conservation Program (WRCP), who funded this study as part of their effort to encourage protection of wetland resources. Our appreciation to Greg Czarnecki (DCNR-WRCP) and Greg Podniesinski (DCNR-Office of Conservation Science (OCS)), who administered the EPA and WRCP funds for this work. We greatly appreciate the long hours in the field and lab logged by Western Pennsylvania Conservancy (WPC) staff including Kathy Derge Gipe, Ryan Miller, and Amy Myers. To Tim Maret, and Larry Klotz of Shippensburg University, Aura Stauffer of the PA Bureau of Forestry, and Eric Lindquist of Messiah College, we appreciate the advice you provided as we developed this project. -
Longhorn Fairy Shrimp (Branchinecta Longiantenna)
Invertebrates Longhorn Fairy Shrimp (Branchinecta longiantenna) Longhorn Fairy Shrimp (Branchinecta longiantenna) Status State: Meets the requirements as a “rare, threatened, or endangered species” under CEQA Federal: Endangered Critical Habitat: Designated 2006 (USFWS 2006) Population Trend Global: Declining due to habitat loss and fragmentation (Eriksen and Belk 1999) State: As above Within Inventory Area: Unknown Data Characterization The location database for the longhorn fairy shrimp (Branchinecta longiantenna) within the inventory area includes 2 records from 1982 and 1990 near the Los Vaqueros Reservoir (Eng et. al. 1990, California Natural Diversity Database 2001). These 2 locations are shallow, sandstone-rock-outcrop vernal pools within non-native grassland. Other natural and artificial habitats have a high probability of being occupied by additional populations of the longhorn fairy shrimp throughout the grassland habitats within the ECCC HCP/NCCP inventory area. In addition to the original description (Eng et. al. 1990), Eriksen and Belk (1999) presented a brief discussion of the longhorn fairy shrimp and provided a distribution map. Hill and Shepard (1997) produced a scanning electron micrograph of the cyst (resting egg), and Helm (1997) provided some generalized natural history data. No other peer-reviewed technical literature has been published concerning the longhorn fairy shrimp. Range Only 8 populations of the longhorn fairy shrimp are known (U.S. Fish and Wildlife Service 1996). Longhorn fairy shrimp occurrences are rare and highly disjunct with specific pool characteristics largely unknown (USFWS 2003). The Altamont pass subunits of the species occur within clear depression pools in sandstone outcrops (Eriksen and Belk 1999; EBRPD 2001; CNDDB 2002). Other populations in the middle and southern range of the species occur in loam and shallow alkaline soil, respectively (USFWS 2003).