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§4-71-6.5 LIST of CONDITIONALLY APPROVED ANIMALS November
§4-71-6.5 LIST OF CONDITIONALLY APPROVED ANIMALS November 28, 2006 SCIENTIFIC NAME COMMON NAME INVERTEBRATES PHYLUM Annelida CLASS Oligochaeta ORDER Plesiopora FAMILY Tubificidae Tubifex (all species in genus) worm, tubifex PHYLUM Arthropoda CLASS Crustacea ORDER Anostraca FAMILY Artemiidae Artemia (all species in genus) shrimp, brine ORDER Cladocera FAMILY Daphnidae Daphnia (all species in genus) flea, water ORDER Decapoda FAMILY Atelecyclidae Erimacrus isenbeckii crab, horsehair FAMILY Cancridae Cancer antennarius crab, California rock Cancer anthonyi crab, yellowstone Cancer borealis crab, Jonah Cancer magister crab, dungeness Cancer productus crab, rock (red) FAMILY Geryonidae Geryon affinis crab, golden FAMILY Lithodidae Paralithodes camtschatica crab, Alaskan king FAMILY Majidae Chionocetes bairdi crab, snow Chionocetes opilio crab, snow 1 CONDITIONAL ANIMAL LIST §4-71-6.5 SCIENTIFIC NAME COMMON NAME Chionocetes tanneri crab, snow FAMILY Nephropidae Homarus (all species in genus) lobster, true FAMILY Palaemonidae Macrobrachium lar shrimp, freshwater Macrobrachium rosenbergi prawn, giant long-legged FAMILY Palinuridae Jasus (all species in genus) crayfish, saltwater; lobster Panulirus argus lobster, Atlantic spiny Panulirus longipes femoristriga crayfish, saltwater Panulirus pencillatus lobster, spiny FAMILY Portunidae Callinectes sapidus crab, blue Scylla serrata crab, Samoan; serrate, swimming FAMILY Raninidae Ranina ranina crab, spanner; red frog, Hawaiian CLASS Insecta ORDER Coleoptera FAMILY Tenebrionidae Tenebrio molitor mealworm, -
Argopecten Irradians*
MARINE ECOLOGY PROGRESS SERIES I Vol. 74: 47-59, 1991 Published July 18 Mar. Ecol. Prog. Ser. The eelgrass canopy: an above-bottom refuge from benthic predators for juvenile bay scallops Argopecten irradians* David G.Pohle, V. Monica Bricelj8*,Zaul Garcia-Esquivel Marine Sciences Research Center, State University of New York, Stony Brook, New York 11794-5000, USA ABSTRACT: Juvenile bay scallops Argopecten irradians commonly attach to shoots of eelgrass Zostera marina using byssal threads. Although this behavior has long been recognized, its adaptive value is poorly understood. This study examined (1) the size-specif~cnature of scallop attachment on eelgrass, and (2) the possible role of vertical attachment in providing refuge from benthic predators. Laboratory experiments using artificial eelgrass showed strong, inverse relationships between scallop size (over the range 6 to 20 mm) and several measures of attachment performance (percent attachment, rate of attachment, and height-above-bottom attained). Field experiments in which 10 to 15 mm scallops were tethered to natural eelgrass in Lake Montauk, Long Island, New York (USA), demonstrated a dramatic, highly significant enhancement of scallop survival at greater heights of attachment. Scallops tethered at 20 to 35 cm above bottom experienced > 59 O/O survival over 4 d, compared to < l1 O/O sunrival near the sediment surface. A similar pattern was observed in laboratory tethering experiments using trans- planted natural eelgrass and 3 crab predators common in mid-Atlantic embayments: Carcinus maenas, Libinia dubia, and Dyspanopeus sayi. The refuge value of vertical attachment was found, however, to be less with D. sayi than with the other predators tested, since individuals of ths species climbed eelgrass to feed on scallops in the upper canopy. -
Physiological Effects and Biotransformation of Paralytic
PHYSIOLOGICAL EFFECTS AND BIOTRANSFORMATION OF PARALYTIC SHELLFISH TOXINS IN NEW ZEALAND MARINE BIVALVES ______________________________________________________________ A thesis submitted in partial fulfilment of the requirements for the Degree of Doctor of Philosophy in Environmental Sciences in the University of Canterbury by Andrea M. Contreras 2010 Abstract Although there are no authenticated records of human illness due to PSP in New Zealand, nationwide phytoplankton and shellfish toxicity monitoring programmes have revealed that the incidence of PSP contamination and the occurrence of the toxic Alexandrium species are more common than previously realised (Mackenzie et al., 2004). A full understanding of the mechanism of uptake, accumulation and toxin dynamics of bivalves feeding on toxic algae is fundamental for improving future regulations in the shellfish toxicity monitoring program across the country. This thesis examines the effects of toxic dinoflagellates and PSP toxins on the physiology and behaviour of bivalve molluscs. This focus arose because these aspects have not been widely studied before in New Zealand. The basic hypothesis tested was that bivalve molluscs differ in their ability to metabolise PSP toxins produced by Alexandrium tamarense and are able to transform toxins and may have special mechanisms to avoid toxin uptake. To test this hypothesis, different physiological/behavioural experiments and quantification of PSP toxins in bivalves tissues were carried out on mussels ( Perna canaliculus ), clams ( Paphies donacina and Dosinia anus ), scallops ( Pecten novaezelandiae ) and oysters ( Ostrea chilensis ) from the South Island of New Zealand. Measurements of clearance rate were used to test the sensitivity of the bivalves to PSP toxins. Other studies that involved intoxication and detoxification periods were carried out on three species of bivalves ( P. -
Long Island South Shore Estuary Reserve Coordinated Water Resources Monitoring Strategy Long Island SOUTH SHORE ESTUARY RESERVE
Long Island South Shore Estuary Reserve Coordinated Water Resources Monitoring Strategy New York Suffolk Nassau Long Island SOUTH SHORE ESTUARY RESERVE Open-File Report 2017–1161 U.S. Department of the Interior U.S. Geological Survey Cover. The Long Island South Shore Estuary Reserve (orange) stretches west to east from the Nassau-Queens county line to the town of Southampton. South to north, it extends from mean high tide on the ocean side of the barrier islands to the inland limits of the watersheds that drain into the bays. Image courtesy of the New York State Department of State Office of Planning, Development and Community Infrastructure. Long Island South Shore Estuary Reserve Coordinated Water Resources Monitoring Strategy By Shawn C. Fisher, Robert J. Welk, and Jason S. Finkelstein Prepared in cooperation with the New York State Department of State Office of Planning, Development and Community Infrastructure and the South Shore Estuary Reserve Office Open-File Report 2017–1161 U.S. Department of the Interior U.S. Geological Survey U.S. Department of the Interior RYAN K. ZINKE, Secretary U.S. Geological Survey James F. Reilly II, Director U.S. Geological Survey, Reston, Virginia: 2018 For more information on the USGS—the Federal source for science about the Earth, its natural and living resources, natural hazards, and the environment—visit https://www.usgs.gov or call 1–888–ASK–USGS. For an overview of USGS information products, including maps, imagery, and publications, visit https://store.usgs.gov. Any use of trade, firm, or product names is for descriptive purposes only and does not imply endorsement by the U.S. -
Great South Bay Ecosystem-Based Management Plan
Great South Bay Ecosystem-based Management Plan Prepared by The Nature Conservancy, Long Island Chapter Prepared for The New York State Department of State with funds provided by the Environmental Protection Fund 2008 Draft Final 2012 EXECUTIVE SUMMARY Great South Bay (GSB) on the South Shore of Long Island is teeming with life, but it is also degraded compared to historical conditions. Conservation and management measures are needed to preserve and restore the health of the bay. The Long Island Chapter of the Nature Conservancy (TNC), under contract to the New York State Department of State (DOS), developed this Ecosystem-based Management (EBM) Plan for Great South Bay. Ecosystem-based Management is a management approach that considers the entire ecosystem, including humans. It promotes ecosystem viability and integrity, biodiversity, sustainability, and social values and principles. TNC’s analysis relies on choosing a set of ecological surrogates, representative species, and groups of species, or habitat types that can represent the ecological status of the biodiversity in Great South Bay. For each surrogate, specific measurable objectives are developed that describe the intended ecological state of Great South Bay with respect to each surrogate. The measurable objectives are achieved through the implementation of strategic actions and action steps described in the plan. Overarching objectives and strategic actions are also developed to address water quality, global climate change, and education. The surrogates chosen to represent the GSB ecosystem in the plan are: Hard clams Salt marshes Seagrass meadows Barrier island complex Predatory fishes Winter flounder Alewives Piping plovers Horseshoe crabs This report was originally drafted in 2008 followed by an update in 2012 to each surrogate’s current status, strategic actions and action steps. -
Appendix H 1. References Used for Chapter Iv 2
APPENDIX H 1. REFERENCES USED FOR CHAPTER IV 2. EARLY COORDINATION REQUIREMENTS 3. PROGRAMMATIC SECTION 4(f) EVALUATION 3b. COORIDINATION WITH OFFICIALS HAVING JURISDICTION OVER SECTION 4(f) SOURCES 4. COASTAL ASSESSMENT FORM AND POLICY ANALYSIS 5. NEPA CHECKLIST 6. FISH AND WILDLIFE SERVICE CORRESPONDENCE 7. INVASIVE SPECIES APPENDIX H.1 –REFERENCES USED FOR CHAPTER IV ~oo~ i ~, G5 55 i 1W is ~ Cl bY d1~ Q)IWllluaiiy donI_tele! by OI!W or 1i19f'Il; ap:de.$ ~ edmtb6 w ~~ L~tioIua' &I~ ] b/;mplu; Fire SeeAbore. Suffolk 5hJICed trees. C!laraacristic ioch&dc Col,&.ftly; Nb~e 8~ suncuc COlmty. beach-plum (~ILI mantlm«)p ~ (RG1's lIlpilJ). 'i!li!d rose (It ~A&). btI)bcny So~u; An 19'6; ~DaOlJ!. 1985; Significant (Myrka~). 085tCZQ 1:'ed oot1v (Iunipuus Ha'j)jut Unif Silo. vilPJOlfJlNl). llbiaiDs; allllDM (Nllu eopJlllIPlum). poisoiJ i1#y (TDziC<NU1'IdIoIr ~). black chctty I (PruI'lW 300dn4). hiBb~ b~(~ JL G. ~ rjunes: lllj Q)\'lmllllulty dominaaed by l:~bomm). Amencu holly (f!Arz ~). ISDd ] ~ ~ bel low ghm~ that CCUIn OD active aQd sbadbusb (A,"d~lIchier C/Jlltldeflsi.s). stabilized dimes lIIlong the. ~ aJaSt. This Qaraderistir:: biIdrJ iKIwk great egret ccmmWLil)' a!ft:;.is15 0 lit llIJGUlic or vegetBlioa (Ouwt,fOdius e./buJ) IUSd bIKk-a~d lI1igbl Pitches. Tills ~..... ,... ............. beroft (Nyeticona IJ)II:dcDfWr). we!! as sand ~ l3ad d'!~ rmsr-- The ~ ud ~ of «he ~. ~ d~ seawMi or a~ Coutel ~tlltion is vaiiablct~ 0& RaWflt,y of the LowIamd! 1CCOZCI1le. dwaell, -.moWlfS of ~011 ud erosion" ami diwma: rl/'D8lll t ocem. Cbal"'adcNtile RtRM.· v4 S4 lipoda of abo activls: wbcR ~ lDoYO~g is 8r~(c.:.\I, include, bcacbg'lW (A.JwG'nOphilfJi Examp'e: Fare 1daPd,. -
5. Appendix D
Long Island Duck Farm History and Ecosystem Restoration Opportunities Suffolk County, Long Island, New York February 2009 US Army Corps of Engineers Suffolk County, NY New York District APPENDIX D APPENDIX D Duck Farm Industry and Impacts Report prepared by Suffolk County Department of Planning H. Lee Dennison Building - 4th Floor 100 Veterans Memorial Highway P.O. Box 6100 Hauppauge, New York 11788 DeWitt S. Davies, Ph.D. Chief Environmental Analyst Duck Farm Industry Impacts on the Environment Introduction As documented in the historical overview section, the duck farm industry in Suffolk County was an extremely intensive land use along stream and bay shorelines. Inventory work by the Department of Planning indicates that approximately 2,000 acres of upland property and almost 20 miles of shoreline along freshwater creeks/rivers and estuary tributaries – primarily in the Towns of Brookhaven, Riverhead and Southampton – were utilized during the last century in Suffolk County for duck production. The impacts of duck farming were dramatic, both on-site and off-site. Extensive landform alterations were made to construct animal pens, feed lots and swim ponds, which were often located in or directly adjacent to streams/coves of the bays. Waste effluent discharges from the farms created thick organic matter deposits, degraded water quality and altered phytoplankton and benthic population in near-by surface waters. Duck Farms – An Intensive Land Use The significance of the impacts is reflected by the magnitude of the industry and the waste load generated. Effluent waste loadings from the farms in the form of suspended solids, nutrients and coliform bacteria were huge, especially prior to the required use of treatment technology under water pollution control laws. -
This Is Not a Citeable Document
This Meeting was Cancelled. THIS IS NOT A CITEABLE DOCUMENT NATIONAL SHELLFISHERIES ASSOCIATION Program and Abstracts of the 112th Annual Meeting March 29 – April 2, 2020 Baltimore, Maryland NSA 112th ANNUAL MEETING 1DWLRQDO6KHOO¿VKHULHV$VVRFLDWLRQ 7KH&URZQH3OD]D%DOWLPRUH,QQHU+DUERU+RWHO%$/7,025(0$5</$1' 0DUFK±$SULO 681'$<0$5&+ 6:30 PM 678'(1725,(17$7,21 DO NOT &DUUROO CITE 7:00 PM 35(6,'(17¶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
The Baymen of the Great South Bay, New York; a Preliminary Ecological
The Baymen of the Great South Bay, New 'Ilosk of life may have to be abandoned (extinction for other species). A Preliminary Ecological Profile An ecological profile defines the fishermen's unique lifestyle and cultural re- quirements and thenconsiders them as predators on fish or shellfish, as competi- tors with each other and other species, and subjected to environmental variabili- Jeffrey Kassner ty. It shows therefore how the fishermen function within their environment and Town of Brookhaven, Division of Environmental Protection how they respond to it. The advantage to the ecological profile is that it high- lights the various interactions and constraints, ensuring that all relevant factors impacting the fishermen are considered. It is a comprehensive assessment and ABSTRACTEcology is the study of the interactions among organisms and their environ- does not consider fishermen in isolation. ment. Various theories and concepts taken from ecology, for example, optimal foraging the- The Great South Bay is an embayment located on the south shore of Long ory, have been used in theanthropological study of fishermen. While this approach canpro- Island, New York. The bay supports a significant commercial fishery for the vide useful insights, it removes the fishermen from their environment so that potentially hard clam (Mereenaria mereenaria) which is harvested by fishermen, known lo- significant factors may be taken out of context or omitted. An ecological profileof a fisher- cally as baymen or clam diggers, who are self-employed and work individually men population would present a more comprehensiveecological study, examining theecolog- from small boats (less than 10 m) on open access public bay bottom using hand ical processes of predation, competition and adaptation from the perspective of the fisher- operated rakes and tongs. -
Draft Genome of the Peruvian Scallop Argopecten Purpuratus
GigaScience, 7, 2018, 1–6 doi: 10.1093/gigascience/giy031 Advance Access Publication Date: 2 April 2018 Data Note DATA NOTE Draft genome of the Peruvian scallop Argopecten Downloaded from https://academic.oup.com/gigascience/article/7/4/giy031/4958978 by guest on 29 September 2021 purpuratus Chao Li1, Xiao Liu2,BoLiu1, Bin Ma3, Fengqiao Liu1, Guilong Liu1, Qiong Shi4 and Chunde Wang 1,* 1Marine Science and Engineering College, Qingdao Agricultural University, Qingdao 266109, China, 2Key Laboratory of Experimental Marine Biology, Institute of Oceanology, Chinese Academy of Sciences, Qingdao 266071, China, 3Qingdao Oceanwide BioTech Co., Ltd., Qingdao 266101, China and 4Shenzhen Key Lab of Marine Genomics, Guangdong Provincial Key Lab of Molecular Breeding in Marine Economic Animals, BGI Academy of Marine Sciences, BGI Marine, BGI, Shenzhen 518083, China *Correspondence address. Chunde Wang, Marine Science and Engineering College, Qingdao Agricultural University, Qingdao 266109, China. Tel: +8613589227997; E-mail: [email protected] http://orcid.org/0000-0002-6931-7394 Abstract Background: The Peruvian scallop, Argopecten purpuratus, is mainly cultured in southern Chile and Peru was introduced into China in the last century. Unlike other Argopecten scallops, the Peruvian scallop normally has a long life span of up to 7 to 10 years. Therefore, researchers have been using it to develop hybrid vigor. Here, we performed whole genome sequencing, assembly, and gene annotation of the Peruvian scallop, with an important aim to develop genomic resources for genetic breeding in scallops. Findings: A total of 463.19-Gb raw DNA reads were sequenced. A draft genome assembly of 724.78 Mb was generated (accounting for 81.87% of the estimated genome size of 885.29 Mb), with a contig N50 size of 80.11 kb and a scaffold N50 size of 1.02 Mb. -
Breaking Through
Photo courtesy of George Proios Breaking Through Nothing is more constant than in business and municipal practices that change itself… may have led to a decline in commercial shellfish populations. And nowhere can this be demonstrated more graphically than along Long Island’s barrier Looking long-term at the effects that beaches where the dynamic interactions future breaches along barrier beaches between shifting sands and crashing ocean might have on these estuarine ecosys- waves constantly reshape the thin strands of tems, New York Sea Grant has funded beach and periodically form new inlets. When four novel research projects. Each has new inlets form, salty water from the ocean a different approach and thus provides a enters the calmer, shallow waters of Long different piece of the puzzle. Island’s south shore estuaries (LISSE), po- Continued on page 4 tentially changing the delicate balance of the estuaries’ ecosystems. In recent decades, Breaking Through page 1 by Patrick Dooley and Barbara A. Branca each of these estuarine ecosystems has Funding Breakthrough Research page 3 by Barbara A. Branca, Patrick Dooley already undergone change due to increased and Lane Smith community development along Long Island’s NYSG a Sounding Board for Governor on Ocean Report page 6 populated south shore coupled with changes by Barbara A. Branca and Jack Mattice Are Marshes Losing Ground? page 7 by Barbara A. Branca CoastWatch: page 8 Great Lakes Student Summit by Paul C. Focazio Botulism Update page 10 by Helen Domske and Lane Smith Currents Stakeholders Set Great Lakes Priorities Paul C. Focazio page 12 Earthstock 2004 by Susan M. -
Chapter 2: Brown Tide Management Plan
Peconic Estuary Program C H A P T E R TWO BROWN TIDE MANAGEMENT PLAN OBJECTIVES 1) Determine the chemical, physical and biological factors responsible for producing, sustaining and ending blooms of the Brown Tide organism, Aureococcus anophagefferens. 2) Determine what management actions can be undertaken to prevent or, if that is not possible, to mitigate the effects of recurrent Brown Tide blooms on the ecosystem and economy of the Peconics. C H A P T E R T W O 2-1 Peconic Estuary Program CCMP MEASURABLE GOALS The PEP’s measurable goals with respect to Brown Tide blooms include: • Continue to better coordinate, focus, and expand Brown Tide research efforts (measured by funding appropriated, frequency of Brown Tide symposiums, frequency of updating the Brown Tide Workplan and coordinations within the Brown Tide Steering Committee). [See Action B-1] • Continue the current level of water quality sampling in the Peconic Estuary (measured by the number and frequency of samples taken per year and the number of bays and peripheral embayments sampled). Currently, the Suffolk Department of Health Services conducts biweekly monitoring at 32 stations in the Peconic Estuary throughout the year, resulting in over 830 samples taken annually. [See Action B-1] Measurable goals related to natural resources are found in the Habitat and Living Resources Chapter (Chapter 4). C H A P T E R T W O 2-2 Peconic Estuary Program CCMP INTRODUCTION Brown Tide is a marine microalgal bloom. Microalgae, or phytoplankton, are microscopic, single- cell plants that are found in all natural freshwater and marine ecosystems.